Overview

Comprehensive Description

Biology

Epipelagic (Ref. 58426). There are two forms, the anadromous form known as the sockeye and the landlocked form (with a much smaller maximum size) known as the kokanee (Ref. 27547). Upon emergence from gravel, fry at first tends to avoid light, hiding during the day and emerging at night (Ref. 27547). In some populations, sockeye fry go to the sea during their first summer but most spend one or two (rarely three or four) years in a lake before migrating (Ref. 30333). In a few streams of the Copper River drainage in Alaska, young sockeye stay in the stream (Ref. 27547). Once in the lake, the young spend a few weeks inshore, feeding largely on ostracods, cladocerans and insect larvae. The fish then become pelagic and move offshore, where they feed on plankton in the upper 20 m or so (Ref. 27547). Seaward migration follows with the young individuals first staying fairly close to shore, feeding mainly on zooplankton, but also on small fishes and insects (Ref. 30343, 30346). With growth, they head out to sea and fish become important in the diet (Ref. 27547). Kokanee are confined to lake-stream systems, and most of its life is spent in the lake (Ref. 27547). They feed mainly on plankton, but also take insects and bottom organisms (Ref. 1998). Kokanee, wherever they are native, have been derived from anadromous populations, and each kokanee population apparently has evolved independently from a particular sockeye run (Ref. 30338, 30339). Offspring of kokanee occasionally become anadromous, and sockeye offspring occasionally remain in freshwater (Ref. 27547). Lifespan of the kokanee varies from two to seven years in different stocks (Ref. 27547). The sockeye is one of the most commercially important Pacific salmons; the kokanee is primarily a sport fish but also makes excellent food and in some areas well regarded as food for large trout (Ref. 27547). Marketed fresh, dried or salted, smoked, canned, and frozen; eaten steamed, fried, broiled, microwaved, and baked (Ref. 9988). The Alaska Salmon fishery of this species has been certified by the Marine Stewardship Council (http://www.msc.org/) as well-managed and sustainable (http://www.msc.org/html/content_485.htm).
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Distribution

Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45–70°N to 140°E–125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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Range Description

The current distribution of Oncorhynchus nerka extends from approximately 45-70°N to 140°E-125°W longitude. The species has been recorded from Russia, United States, Canada, and Japan, although the Japanese populations are likely to have resulted from introductions; Japan is therefore not considered to be part of this species' natural range.

See the additional supporting documentation (particularly Figures 1 & 2, and Appendices 1 & 2) for details on the range of this species and of each of the 80 subpopulations identified. Follow the link below for a PDF of the additional supporting documentation.
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occurs (regularly, as a native taxon) in multiple nations

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National Distribution

Canada

Origin: Native

Regularity: Regularly occurring

Currently: Present

Confidence: Confident

Type of Residency: Year-round

United States

Origin: Native

Regularity: Regularly occurring

Currently: Present

Confidence: Confident

Type of Residency: Year-round

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Global Range: During oceanic feeding and maturation, this salmon ranges throughout the North Pacific Ocean, Bering Sea, and eastern Sea of Okhotsk north of 40 degrees north latitude; there is considerable intermingling of Asian and North American populations, and of North American populations from Bering Sea and Gulf of Alaska streams; the range shifts southward for winter, northward during warmer months. Natural lake populations occur in Japan, former USSR, Alaska, Washington, Idaho, Oregon, Yukon, and British Columbia. Anadromous forms occur in Asia from Hokkaido, Japan, to the Anadyr River (spawning mainly on the Kamchatka Peninsula); in North America, anadromous populations range from the Sacramento River, California, north to Point Hope, Alaska (common in north, rare south of Columbia River drainage). Major Alaskan spawning areas are in tributaries and lakes of the Kenai, Chignik, Naknet, Kuichak, Wood, and Kodiak Island river systems. South of Alaska in the Pacific Northwest, the major spawning river is the Fraser River system in British Columbia, with smaller runs in the Baker, Columbia, Cedar, Quinalt, and Ozette rivers in Washington. The Fraser River includes a number of important nursery lakes (Cultus, Adams, Harrison, Horsefly, Shuswap, and Quesnel) and many tributaries that support the major portion of the Pacific Northwest population. In eastern Washington, major nursery lakes for Columbia River are Lake Wenathchee and Osoyoos Lake. In western Washington, major nursery lakes are Quinalt Lake, Ozette Lake, Baker Lake, and Lake Washington. In a 1996 survey of populations in the contiguous U.S., one healthy native stock was identified (Wenatchee River, Washington). The kokanee (lake-stream form) has been introduced in many western states and elsewhere, but most transplants have been unsuccessful in establishing self-sustaining populations.

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Historic Range:
North Pacific Basin from U.S.A. (CA) to Russia

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North Pacific: northern Japan to Bering Sea and to Los Angeles, California, USA (Ref. 2850). Landlocked populations in Alaska, Yukon Territory and British Columbia in Canada, and Washington and Oregon in USA.
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Physical Description

Morphology

Dorsal spines (total): 0; Dorsal soft rays (total): 11 - 16; Analspines: 0; Analsoft rays: 13 - 18; Vertebrae: 56 - 67
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Size

Length: 71 cm

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Maximum size: 840 mm TL
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Max. size

84.0 cm TL (male/unsexed; (Ref. 5723)); 71 cm (female); max. published weight: 7,710 g (Ref. 40637); max. reported age: 8 years (Ref. 72462)
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Diagnostic Description

Both the sockeye and the kokanee are distinguished by the long, fine, serrated, closely spaced gill rakers on the first arch that number between 30 and 40, and by its lack of definite spot on the back and tail (Ref. 27547). Body fusiform, streamlined, laterally compressed, body depth moderate, slightly deeper in breeding males (Ref. 6885). Head bluntly pointed, conical, eye rather small, position variable with sex and condition; snout rather pointed (Ref. 6885). Lateral line straight (Ref. 27547). Pelvic fins with axillary process; caudal emarginate (Ref. 27547). Pre-spawning fish are dark steel blue to greenish blue on the head and back, silvery on the sides and white to silvery on the belly; no definite spots on the back, although some individuals may have dark speckling and irregular marks on the dorsal fin (Ref. 27547). At spawning, the head of the males becomes bright to olive green, with black on the snout and upper jaw; the adipose and anal fins turn red and the paired fins and tail generally become grayish to green or dark; females are generally less brilliantly colored than males (Ref. 27547). Various populations may show less brilliant colors, and a few turn dull green to yellowish, with little if any red (Ref. 27547).
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Ecology

Habitat

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a life history form called “Kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “Sockeye” or “Red Salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some Sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include Salmon Sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type Sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000–5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Habitat and Ecology

Habitat and Ecology
The species exhibits a great variety of life history patterns. It has a genetically diverged life history form called “kokanee” that lives its entire life within freshwater, but this assessment includes only anadromous populations commonly referred to as “sockeye” or “red salmon”. Sockeye are born in gravel nests in rivers or lakes and the majority of life history forms rear as juveniles for one to three years in freshwater before migrating to the ocean. Some sockeye assume a river-type life history and rear in a river channel, while others are lake-type and rear in a lake environment. Primary prey during this life history stage include zooplankton and stream invertebrates. Some sea-type populations migrate within one to three months following emergence, and these make extensive use of estuaries. Most populations spend one to three years in offshore feeding areas where they grow to maturity (ca. 50-60 cm total length, 2.5-3.0 kg weight). Diet in the ocean consists primarily of zooplankton (copepods and euphausiids), but their diet also includes squids and fishes. Natural predators during this period in their life history include salmon sharks (Lamna ditropis) and Daggertooth (Anotopterus nikparini). Foraging individuals mix among populations both within and between Asia and North America, but at maturity they all migrate back toward their natal freshwater habitat where they spawn and die. The return to natal habitat and the isolation of spawning populations results in considerable genetic differentiation and adaptation to local conditions. Many fish are intercepted by fishers during the homeward, spawning migration, and natural predators include seals, sea lions and bears. Spawning occurs in late summer and autumn, in lake outlet or lake tributary streams or along lake beaches in finer sediments where subterranean upwelling occurs or among boulders on wave-aerated shores. River-type sockeye spawn in river channels not associated with lakes. Adults display bright red bodies and green heads. Males compete with each other for access to females. Females compete with each other for gravel sites where they build nests, deposit eggs (fecundity typically ranges from 2,000-5,000 eggs), and briefly guard the redd. Median population size for the species is ca. 6,000 individuals. Reviews of life history and ecology of the species appear in Smith et al. (1987), Burgner (1991), Wood (1995) and Quinn (2005).

Systems
  • Freshwater
  • Marine
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Depth range based on 4 specimens in 1 taxon.

Environmental ranges
  Depth range (m): 0 - 122

Graphical representation

Depth range (m): 0 - 122
 
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
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Habitat Type: Freshwater

Comments: Nonbreeding adult sockeye salmon are oceanic, with many occurring in nutrient-rich waters of Alaska and the arctic. Kokanee do best in large, cold, mountain lakes (Sigler and Sigler 1987), where the presence of well-oxygenated water is essential (Sublette et al. 1990).. Water temperatures above 60 degrees F (about 15.5 C) lead to significant mortality, especially among the young (see Sublette et al. 1990). Young are not often found in estuarine or inshore waters after reaching the marine environment (Pauley et al. 1989).

Kokanee usually spawn in tributary stream of lake, often in riffle over gravel substrate; sometimes along gravelly shore of lake where seepage outflows, springs, or wind-induced waves occur. Sockeye move up coastal rivers and spawns in streams. Female constructs a redd (several nesting pockets) in gravel (usually) or sand bottom.

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Depth: 0 - 250m.
Recorded at 250 meters.

Habitat: pelagic.
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Environment

pelagic-oceanic; anadromous (Ref. 51243); freshwater; brackish; marine; depth range 0 - 250 m (Ref. 50550)
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Migration

Non-Migrant: Yes. At least some populations of this species do not make significant seasonal migrations. Juvenile dispersal is not considered a migration.

Locally Migrant: Yes. At least some populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).

Locally Migrant: Yes. At least some populations of this species make annual migrations of over 200 km.

Anadromous forms migrate from ocean waters up coastal streams and rivers to spawn in natal waters; spend 1-4 years (usually 2 years) in ocean, 2 years in freshwater; ascend river, spend 1-8 months in lake, then move to natal spawning area. Many non-anadromous populations move from lakes into tributary streams to spawn, some remain in lakes. Enters spawning rivers from late spring to midsummer, depending on the population.

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Anadromous. Fish that ascend rivers to spawn, as salmon and hilsa do. Sub-division of diadromous. Migrations should be cyclical and predictable and cover more than 100 km.
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Trophic Strategy

Epipelagic (Ref. 58426). There are two forms, the anadromous form known as the sockeye and the landlocked form (with a much smaller maximum size) known as the kokanee (Ref. 27547). Upon emergence from gravel, fry at first tends to avoid light, hiding during the day and emerging at night (Ref. 27547). In some populations, sockeye fry go to the sea during their first summer but most spend one or two (rarely three or four) years in a lake before migrating (Ref. 30333). In a few streams of the Copper River drainage in Alaska, young sockeye stay in the stream (Ref. 27547). Once in the lake, the young spend a few weeks inshore, feeding largely on ostracods, cladocerans and insect larvae. The fish then become pelagic and move offshore, where they feed on plankton in the upper 20 m or so (Ref. 27547). Seaward migration follows with the young individuals first staying fairly close to shore, feeding mainly on zooplankton, but also on small fishes and insects (Ref. 30343, 30346). With growth, they head out to sea and fish become important in the diet (Ref. 27547). Kokanee are confined to lake-stream systems, and most of its life is spent in the lake (Ref. 27547). They feed mainly on plankton, but also take insects and bottom organisms (Ref. 1998). Kokanee, wherever they are native, have been derived from anadromous populations, and each kokanee population apparently has evolved independently from a particular sockeye run (Ref. 30338, 30339). Offspring of kokanee occasionally become anadromous, and sockeye offspring occasionally remain in freshwater (Ref. 27547). Lifespan of the kokanee varies from two to seven years in different stocks (Ref. 27547).
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Comments: Kokanee feed on zooplankton. Young sockeye eat primarily planktonic crustaceans. At sea, young sockeye feed on zooplankton, small fishes and insects; as they grow they eat more fish.

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Diseases and Parasites

Whirling Disease 3. Parasitic infestations (protozoa, worms, etc.)
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Enteric Redmouth Disease. Bacterial diseases
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General Ecology

Life cycle of sockeye similar to kokanee except sockeye matures in the ocean rather than lakes. Kokanee often travels in large schools. (Sigler and Sigler 1987). Two studies each reported survival rate of 4-20% for marine portion of life cycle (see Pauley et al. 1989). Northern squawfish and rainbow trout may be important predators on young in some lakes. Schools of young in lakes disperse as dusk approaches, reform after dawn (Pauley et al. 1989). In Montana, the introduction of opossum shrimp (Mysis relicta) was followed by an abrupt decline in the kokanee population, apparently due to zooplankton decline caused by shrimp predation (Spencer et al. 1991).

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Life History and Behavior

Cyclicity

Comments: Kokanee: feeding generally heaviest from sundown to dark (Sigler and Sigler 1987). Young sockeye feeding heaviest in afternoon, lightest at night and early morning (Pauley et al. 1989).

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Life Cycle

Adult sockeyes return to natal streams to spawn. This occurs during summer and fall and as late as December in the southern part of the range. The female selects a site, usually with gravel bottom, and digs a nest. During nest building, the female is attended by a dominant male and a few subordinate males. At this stage, females tend to be aggressive toward other females and subordinate males; males are aggressive toward other males. Between digging acts, the female will rest over the pit while the dominant male courts her. Once the nest is completed, the female enters the nest, followed immediately by the dominant male who comes close beside her. Their mouths gape, and the pair vibrates to release eggs and sperm. One or more subordinate males may come to the other side of the female and join in the spawning. The female then moves to the upstream edge of the nest and digs again, covering the old nest, at the same time creating a new one just upstream from the previous one. A female normally needs 3 to 5 days to deposit all her eggs and utilizes 3 to 5 nests for this purpose. She may spawn with several dominant males. A male may breed with several females. All adult sockeye die after spawning (Ref. 27547).Reproductive strategy: synchronous ovarian organization, determinate fecundity (Ref. 51846).
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Reproduction

Anadromous forms migrate from ocean waters up coastal streams and rivers to spawn in natal waters. They spend 1-4 years (usually 2 years) in the ocean before ascending streams (mainly in summer but some stocks as early as winter). Many stocks spawn in fall (peak often in October or November), but spawning extends into winter in some areas. Spawning sites often are in gravel riffles, sometimes along gravelly shores of lakes where seepage outflows, springs, or wind-induced waves occur. Eggs hatch in 6-9 weeks, depending on temperature, and larvae emerge 2-3 weeks later. Sockeye fry move upstream or downstream to nursery lakes, where the young spend 1-2 years (up to 3 or rarely 4 years in some areas of Alaska; usually 1 year in British Columbia) before going to sea, usually in spring; some populations use stream areas for rearing and may migrate to the sea soon after emergence.

Many non-anadromous (kokanee) populations move from lakes into tributary streams to spawn, though some remain in lakes. They enter spawning streams from late spring to midsummer, depending on the population. Kokanee spawn in different areas from August to February, at temperatures of 40-55 F.

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Molecular Biology and Genetics

Molecular Biology

Barcode data: Oncorhynchus nerka

The following is a representative barcode sequence, the centroid of all available sequences for this species. 

 
There are 76 barcode sequences available from BOLD and GenBank.  Below is a sequence of the barcode region Cytochrome oxidase subunit 1 (COI or COX1) from a member of the species.  See the BOLD taxonomy browser for more complete information about this specimen and other sequences.
 
GBGC3912-07|NC_008615|Oncorhynchus nerka| ACACGATGATTCTTCTCAACCAACCACAAAGACATTGGCACCCTCTATTTAGTATTTGGTGCCTGAGCCGGGATAGTCGGCACCGCCCTA---AGCCTACTGATTCGGGCAGAACTAAGCCAGCCAGGCGCTCTTCTAGGAGAT---GACCAGATCTATAACGTAATCGTCACAGCCCATGCCTTCGTTATGATTTTCTTTATAGTCATACCAATTATAATCGGAGGATTTGGAAACTGATTAATCCCTCTAATA---ATCGGAGCCCCCGATATGGCATTCCCACGAATAAATAACATAAGCTTCTGACTCCTCCCCCCCTCGTTTCTCCTCCTCCTATCTTCATCTGGAGTTGAAGCCGGCGCTGGTACCGGATGAACAGTTTATCCCCCTCTGGCCGGAAACCTTGCCCACGCGGGAGCCTCTGTTGACTTA---ACCATCTTCTCCCTTCATTTAGCTGGAATTTCCTCAATTTTAGGAGCCATTAATTTTATCACAACCATTATTAATATGAAGCCCCCAGCCATCTCTCAGTACCAGACCCCACTTTTTGTTTGAGCTGTGCTAATCACTGCTGTACTTCTACTACTTTCCCTACCCGTCCTAGCAGCA---GGCATTACTATGTTACTTACTGACCGAAATTTAAACACCACTTTCTTTGACCCGGCAGGCGGGGGAGATCCGATTTTATACCAACACCTCTTTTGGTTCTTCGGACACCCAGAGGTATATATTCTTATCCTCCCAGGCTTCGGTATAATTTCACATATCGTTGCATACTACTCCGGCAAAAAA---GAACCATTCGGGTATATAGGAATAGTTTGAGCTATAATAGCCATCGGGTTACTAGGGTTTATCGTTTGAGCCCACCACATGTTCACTGTCGGAATAG 
-- end --

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Statistics of barcoding coverage: Oncorhynchus nerka

Barcode of Life Data Systems (BOLDS) Stats
Public Records: 76
Species: 78
Species With Barcodes: 1

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Conservation

Conservation Status

IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 8 site(s), was 0%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 1513%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -22%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 998%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
EN
Endangered

Red List Criteria
A2a;B2ab(v)

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -67%. It therefore qualifies as Endangered against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (55 km2), the number of extant locations (1 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Endangered against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Critically Endangered
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 13 site(s), was -16%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 12%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation
.
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IUCN Red List Assessment


Red List Category
EN
Endangered

Red List Criteria
A2a

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 35 site(s), was -77%. It therefore qualifies as Endangered against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (683 km2), the number of extant locations (10 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Vulnerable against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 8 site(s), was 9%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
EN
Endangered

Red List Criteria
A2a;B2ab(v)

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -66%. It therefore qualifies as Endangered against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (15 km2), the number of extant locations (1 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Endangered against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 162%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 8 site(s), was 33%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 14 site(s), was 91%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 93%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria
A2a;B2ab(v)

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 42%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
CR
Critically Endangered

Red List Criteria
A2a

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -94%. It therefore qualifies as Critically Endangered against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (32 km2), the number of extant locations (3 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Endangered against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
EN
Endangered

Red List Criteria
B2ab(v)

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 2 site(s), was -39%. It therefore qualifies as Vulnerable against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (21 km2), the number of extant locations (4 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Endangered against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 2 site(s), was 100%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 89%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
VU
Vulnerable

Red List Criteria
A2a;B2ab(v)

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 3 site(s), was -38%. It therefore qualifies as Vulnerable against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (309 km2), the number of extant locations (around 6 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Vulnerable against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 2 site(s), was 142%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
EN
Endangered

Red List Criteria
A2a

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 6 site(s), was -78%. It therefore qualifies as Endangered against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (801 km2), the number of extant locations (7 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Vulnerable against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 7%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
CR
Critically Endangered

Red List Criteria
D

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against the A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over one site, is -68%. It therefore qualifies as Endangered against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (20 km²), the number of extant locations (1 lake or distinct spawning area), and its observed rate of change in adult abundance described above qualifies this subpopulation as Endangered against the B2ab(v) criteria. The current average abundance of mature adults in the subpopulation (2) qualifies it as Critically Endangered against the D criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures. Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Critically Endangered
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
EN
Endangered

Red List Criteria
A2a

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 22 site(s), was -54%. It therefore qualifies as Endangered against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (520 km2), the number of extant locations (>30 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Least Concern against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation
.

History
  • 2008
    Endangered
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 702%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 50%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 6 site(s), was 7%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation
.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
At the global population level, Sockeye Salmon are assigned a Red List status of Least Concern (LC). The median and mean rate of change across the 62 assessed populations indicate an expanding global population (9.0 and 72.4 % increase, respectively, over the past three generations), thus there is no evidence of risk to the species under Red List A2 criterion. With an estimated geographic range of 11.5 million km², there is no evidence of threat to the global population under criterion B1 (Table 1). Similarly, at 1.9 million km² of current occupancy (freshwater basin area), there is no evidence of threat under criterion B2 (Table 1). Approximately 7% of the historical range of Sockeye Salmon has been lost due to localized extinction events, but we conclude the species is not threatened globally.

For all Figures, Tables and more details about the methods used for this assessment, see the additional supporting documentation. Follow the link below for a PDF of the additional documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 2 site(s), was 28%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters and complete description of methods and assumptions.

Follow the link below for a PDF of the additional supporting documentation
.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
CR
Critically Endangered

Red List Criteria
A2a

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -84%. It therefore qualifies as Critically Endangered against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (210 km2), the number of extant locations (1 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Endangered against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Critically Endangered
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Vulnerable
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 2 site(s), was 43%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 2 site(s), was 30%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -7%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 420%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
EX
Extinct

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
We classified subpopulations as extinct if the species no longer occurs in its historical habitat, the population has been replaced by a non-indigenous population, or the anadromous component of the population no longer exists, even if a potential remnant gene pool of resident fish (kokanee) still survives above human-made barriers to migration. Determinations were based on available information on populations and inferences based on genetic, ecological and life-history characteristics common to extant sockeye salmon Evolutionarily Significant Units, as defined by NOAA Fisheries in the USA (Gustafson et al. 2007). Additional input was obtained from experts. These extinctions were known to occur immediately following completion of impassible dams throughout the Columbia River drainage. Key dams that eliminated passage to sockeye lakes were built during 1909-1967.

History
  • 2008
    Extinct
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
EX
Extinct

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
We classified subpopulations as extinct if the species no longer occurs in its historical habitat, the population has been replaced by a non-indigenous population, or the anadromous component of the population no longer exists, even if a potential remnant gene pool of resident fish (kokanee) still survives above human-made barriers to migration. Determinations were based on available information on populations and inferences based on genetic, ecological and life-history characteristics common to extant sockeye salmon Evolutionarily Significant Units, as defined by NOAA Fisheries in the USA (Gustafson et al. 2007). Additional input was obtained from experts. These extinctions were known to occur immediately following completion of impassible dams throughout the Columbia River drainage. Key dams that eliminated passage to sockeye lakes were built during 1909-1967.

History
  • 2008
    Extinct
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
NT
Near Threatened

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 291%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. This subpopulation nearly qualifies for listing under B2ab(iii) based on the decline in quality of the freshwater habitat, particularly as a result of extensive hydropower development in the region. We therefore list this subpopulation as Near Threatened. See additional supporting document for data sources, trend model parameters and complete description of methods and assumptions.
Follow the link below for a PDF of the additional supporting documentation
.

History
  • 2008
    Near Threatened
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 12 site(s), was 9%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
NT
Near Threatened

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 121%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. This subpopulation nearly qualifies for listing under B2ab(iii) based on the decline in quality of the freshwater habitat, particularly as a result of extensive hydropower development in the region. We therefore list this subpopulation as Near Threatened. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Near Threatened
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 6 site(s), was 53%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters and complete description of methods and assumptions.

Follow the link below for a PDF of the additional supporting documentation
.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -27%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Endangered
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
VU
Vulnerable

Red List Criteria
A2a

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -49%. It therefore qualifies as Vulnerable against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (3 km2), the number of extant locations (>30 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Least Concern against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Endangered
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
EN
Endangered

Red List Criteria
A2a

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -65%. It therefore qualifies as Endangered against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (73 km2), the number of extant locations (>20 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Least Concern against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Endangered
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 8 site(s), was 20%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 2 site(s), was 26%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation
.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 59%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -21%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
EX
Extinct

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
We classified subpopulations as extinct if the species no longer occurs in its historical habitat, the population has been replaced by a non-indigenous population, or the anadromous component of the population no longer exists, even if a potential remnant gene pool of resident fish (kokanee) still survives above human-made barriers to migration. Determinations were based on available information on populations and inferences based on genetic, ecological and life-history characteristics common to extant sockeye salmon Evolutionarily Significant Units, as defined by NOAA Fisheries in the USA (Gustafson et al. 2007). Additional input was obtained from experts. These extinctions were known to occur immediately following completion of impassible dams throughout the Columbia River drainage. Key dams that eliminated passage to sockeye lakes were built during 1909-1967.

History
  • 2008
    Extinct
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 38 site(s), was 16%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
EX
Extinct

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
We classified subpopulations as extinct if the species no longer occurs in its historical habitat, the population has been replaced by a non-indigenous population, or the anadromous component of the population no longer exists, even if a potential remnant gene pool of resident fish (kokanee) still survives above human-made barriers to migration. Determinations were based on available information on populations and inferences based on genetic, ecological and life-history characteristics common to extant sockeye salmon Evolutionarily Significant Units, as defined by NOAA Fisheries in the USA (Gustafson et al. 2007). Additional input was obtained from experts. These extinctions were known to occur immediately following completion of impassible dams throughout the Columbia River drainage. Key dams that eliminated passage to sockeye lakes were built during 1909-1967.

History
  • 2008
    Extinct
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -29%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Endangered
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -2%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was 125%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters and complete description of methods and assumptions.
Follow the link below for a PDF of the additional supporting documentation
.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
EN
Endangered

Red List Criteria
A2a;B2ab(v)

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 2 site(s), was -55%. It therefore qualifies as Endangered against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (154 km2), the number of extant locations (4 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Endangered against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Endangered
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
VU
Vulnerable

Red List Criteria
A2a

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification

This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 6 site(s), was -39%. It therefore qualifies as Vulnerable against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (864 km2), the number of extant locations (>35 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Least Concern against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters and complete description of methods and assumptions.

Follow the link below for a PDF of the additional supporting documentation.


History
  • 2008
    Vulnerable
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
EN
Endangered

Red List Criteria
A2a;B2ab(v)

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -69%. It therefore qualifies as Endangered against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (33 km2), the number of extant locations (2 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Endangered against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Endangered
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 2 site(s), was 81%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 3 site(s), was -10%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 5 site(s), was 117%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation
.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
CR
Critically Endangered

Red List Criteria
A2a

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 2 site(s), was -92%. It therefore qualifies as Critically Endangered against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (27 km2), the number of extant locations (8 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Vulnerable against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Critically Endangered
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 3 site(s), was 27%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
EN
Endangered

Red List Criteria
B2ab(v)

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 1 site(s), was -41%. It therefore qualifies as Vulnerable against criterion A2. For evaluation against B2 criterion, we estimated the area of occupancy and the number of extant locations for the subpopulation. Area of occupancy was estimated on a one kilometer square grid overlaid on the nursery lake(s) and freshwater river habitat. This surface area estimate is meant to capture habitat occupied for spawning and rearing by both lake- and river-type life histories. The number of extant locations was the sum of the total number of known nursery lakes and distinct spawning regions supporting the subpopulation. The surface area of freshwater habitat supporting this subpopulation (29 km2), the number of extant locations (3 lakes and/or distinct spawning areas), and its observed rate of change in adult abundance described above qualifies this subpopulation as Endangered against the B2ab(v) criteria. The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Endangered
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
LC
Least Concern

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
This subpopulation was evaluated against relevant A, B and D criteria. Recent escapement trends at individual monitoring sites were analyzed and results were scaled upwards to characterize the Red List status of the subpopulation against A2 criterion (i.e., based on the rate of change in adult abundance over three generations, or 12 years for this species). The rate of change applied to this subpopulation, assessed over 6 site(s), was 18%. It therefore qualifies as Least Concern against criterion A2. For evaluation against B2 criterion, we determined that the subpopulation does not quality for listing given stable or increasing adult abundance.The current abundance of mature adults in the subpopulation qualifies it as Least Concern against the D1 criterion. See additional supporting document for data sources, trend model parameters, complete description of methods and assumptions, key threats specific to each threatened and near threatened subpopulation and general conservation measures.
Follow the link below for a PDF of the additional supporting documentation.

History
  • 2008
    Least Concern
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
EX
Extinct

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
We classified subpopulations as extinct if the species no longer occurs in its historical habitat, the population has been replaced by a non-indigenous population, or the anadromous component of the population no longer exists, even if a potential remnant gene pool of resident fish (kokanee) still survives above human-made barriers to migration. Determinations were based on available information on populations and inferences based on genetic, ecological and life-history characteristics common to extant sockeye salmon Evolutionarily Significant Units, as defined by NOAA Fisheries in the USA (Gustafson et al. 2007). Additional input was obtained from experts. These extinctions were known to occur immediately following completion of impassible dams throughout the Columbia River drainage. Key dams that eliminated passage to sockeye lakes were built during 1909-1967.

History
  • 2008
    Extinct
    (IUCN 2008)
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IUCN Red List Assessment


Red List Category
DD
Data Deficient

Red List Criteria

Version
3.1

Year Assessed
2011

Assessor/s
Rand, P.S.

Reviewer/s
Ruggerone, G. & English, K.

Contributor/s
Goslin, M.

Justification
The species is known to exist here, but currently there are no abundance or range data that exist to evaluate its status, or data are of insufficient quality or continuity for the purpose of evaluation.

History
  • 2008
    Data Deficient
    (IUCN 2008)
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National NatureServe Conservation Status

Canada

Rounded National Status Rank: N5 - Secure

United States

Rounded National Status Rank: N5 - Secure

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NatureServe Conservation Status

Rounded Global Status Rank: G5 - Secure

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Current Listing Status Summary

Status: Endangered
Date Listed: 01/03/1992
Lead Region:   National Marine Fisheries Service (Region 11)   
Where Listed: U.S.A. (Snake River, ID stock wherever found.)

Status: Threatened
Date Listed: 03/25/1999
Lead Region:   National Marine Fisheries Service (Region 11)   
Where Listed: U.S.A. (Ozette Lake, WA)


Population detail:

Population location: U.S.A. (Snake River, ID stock wherever found.)
Listing status: E

Population location: U.S.A. (WA) all naturally spawned population in Ozette Lake and its tributary streams
Listing status: T

For most current information and documents related to the conservation status and management of Oncorhynchus nerka, see its USFWS Species Profile

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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Increasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Decreasing
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Stable
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.
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Population

Population
At the species level, the population is believed to be stable; however, some subpopulations are declining. For more details on subpopulaiton size estimates and trends, see the additional supporting documentation (particularly Appendix 2). Follow the link below for a PDF of the additional supporting documentation.

Population Trend
Unknown
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Threats

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:
  1. Mixed stock fishing leading to over fishing small, less productive populations
  2. Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
  3. Negative effects of hatcheries and construction of artificial spawning habitat
It is important to note that in many cases, the causes for declines in some specific Sockeye Salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Source: IUCN

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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Article rating from 0 people

Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Source: IUCN

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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Source: IUCN

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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Threats

Major Threats
General threats to O. nerka
The key threats to the species identified by the IUCN SSC Salmon Specialist Group were:

a) Mixed stock fishing leading to over fishing small, less productive populations
b) Changing river and ocean conditions that are likely linked to global climate change, expressed in poor marine survival rates and increased incidence of disease in adult spawners
c) Negative effects of hatcheries and construction of artificial spawning habitat

It is important to note that in many cases, the causes for declines in some specific sockeye salmon subpopulations remain unknown.
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Comments: Decline is due to dams that blocked migration, mainstem passage mortality at Columbia and Snake river dams, overutilization in commercial fisheries, and habitat modification (see Nehlsen et al. 1991). Sockeye in the Deschutes River (Oregon) were largely eradicated by dam construction (small anadromous run is maintained by incidental passage of smolts from a resident kokanee population) (Nehlsen et al. 1991). In the Puget Sound area, decline of the Baker River sockeye population has been attributed to upstream and downstream passage problems as a result of dam construction (Nehlsen et al. 1991). Lake Ozette sockeye run on the Washington coast declined because of logging and overfishing in the 1940s and 1950s (Nehlsen et al. 1991).

The decline and persistent low abundance of the Rivers Inlet population in British Columbia apparently was due to poor marine survival, and not due to a decline in juvenile abundance (McKinnell et al. 2001).

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Least Concern (LC)
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Management

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Conservation Actions

Conservation Actions
1. Many subpopulations of Sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of Sockeye Salmon, Sakinaw Lake and Cultus Lake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered Ozette Lake, Lake Pleasant and Quinault Lake Sockeye Salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include Ozette Lake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include Lake Pleasant and Quinault Lake, and to investigate the status of the native beach-spawning Sockeye in Ozette Lake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal Sockeye Salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River Sockeye Salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting Sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening Sockeye Salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of Sockeye Salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for reintroduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw Sockeye Salmon by DFO, and endangered Redfish Lake Sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of Sockeye from remnant, isolated Kokanee populations following dam removal or modification (e.g., Allouette Lake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighbouring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced Sockeye Salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild Sockeye Salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild Sockeye Salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighbouring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type Sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of Sockeye Salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the Kamchatka River basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type Sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
Creative Commons Attribution Non Commercial Share Alike 3.0 (CC BY-NC-SA 3.0)

© International Union for Conservation of Nature and Natural Resources

Source: IUCN

Trusted

Article rating from 0 people

Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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Source: IUCN

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Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Average rating: 2.5 of 5

Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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© International Union for Conservation of Nature and Natural Resources

Source: IUCN

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Conservation Actions

Conservation Actions

1. Many subpopulations of sockeye in British Columbia were found to be threatened based on this assessment. Fisheries and Oceans Canada (DFO) is responsible for salmon management and is currently formulating conservation units (Holtby and Ciruna, unpublished manuscript) and initiating new policy (e.g,. Wild Salmon Policy) and procedures to stem the loss in diversity (DFO 2005, Irvine and Fraser 2008). Two locations of sockeye salmon, SakinawLake and CultusLake, have been assessed and listed as Endangered by the Committee on the Status of Endangered Wildlife in Canada (COSEWIC). However, the federal government has declined protection under the Species at Risk Act (SARA) due to the social and economic costs of closures to the fishery (Irvine et al. 2005). We encourage COSEWIC and DFO to focus attention on those subpopulations that we identified as threatened in this IUCN assessment.

2. We considered OzetteLake, LakePleasant and QuinaultLake sockeye salmon as individual spawning sites in a larger subpopulation (SEASONAL UPWELLING). These lake systems are recognized individually as Evolutionarily Significant Units (ESUs) by National Oceanic and Atmospheric Administration (NOAA). The latter two sites were not included in the genetic baseline applied in this assessment, thus we assumed all sites are members of a larger, parent subpopulation. Further, we did not include OzetteLake in our assessment given the recent escapement data available for the native beach-spawning population at that location is obscured by repeated attempts at establishing a tributary spawning population originating from broodstock taken from outside the basin. We encourage efforts at expanding the range-wide microsatellite-DNA baseline to include LakePleasant and QuinaultLake, and to investigate the status of the native beach-spawning sockeye in OzetteLake.

3. Most of the data used in our assessment, particularly in Alaska, were from large aggregate stocks that may contain many (sometimes 100s) of individual spawning sites, and hence may mask important dynamics occurring at small scales. While a number of recent studies have shown that there is a significant degree of coherence among populations within a given region, it is important to acknowledge that a majority of the variability in vital rates are not explained by regional, environmental drivers, and may result from localized threats, for example road or other infrastructural development, or by different life history characteristics which affect productivity. Where possible and feasible, we recommend a more comprehensive monitoring approach that addresses dynamics at the scale of individual spawning sites. An excellent example of this approach is the Wood River system in Alaska’s Bristol Bay region, where a combination of sampling approaches provides a more integrated monitoring system that translates into a robust assessment of the status of the species in that basin.

4. Mixed-stock fishing is likely to be a key factor in the decline observed at many sites and subpopulations in our assessment. We feel a key priority is filling a gap in knowledge about composition of mixed-stock harvest in coastal sockeye salmon fisheries. While a great deal of resources has been invested in developing weak-stock management for Fraser River sockeye salmon through the Pacific Salmon Commission and DFO, there has been much less attention placed in other regions along the west coast of North America, particularly in the regions where we found the greatest diversity of subpopulations. We encourage continued investment in developing methods and protocols to account for subpopulation composition of coastal fisheries targeting sockeye salmon to help track harvest pressure at a biologically and ecologically meaningful scale. Further, we encourage fisheries management agencies to explore restructuring fisheries in a way that would result in shifting fishing pressure from coastal regions to more terminal locations, thus providing a more effective means of controlling fishing pressure at the scale of individual subpopulations.

5. Another leading factor threatening sockeye salmon are poor marine survival rates. This has been documented in cases where smolt-to-adult survival rates are estimated through intensive monitoring programs. This appears to be a significant factor explaining declines in adult abundance across many locations in the southern range of the species in North America. While marine conditions have been shown to cycle based on climate forcing and may, in fact, improve in future years, we feel it is important for those managing salmon in this region to acknowledge that poor marine survival may persist, particularly given projections based on global climate change. Reversing declining trends in those subpopulations affected may require increased attention to agents of mortality that are occurring at other life history stages over which we have more local control.

6. Many previous attempts at re-introductions of sockeye salmon have been unsuccessful, and we feel any effort at captive breeding or inter-basin transfers for re-introduction purposes should proceed with great caution. These efforts, to the extent that they exist, are at best stop-gap measures and are in no way a substitute for conserving the species in the wild. The lack of success from the captive breeding of endangered Sakinaw sockeye salmon by DFO, and endangered RedfishLake sockeye by NMFS, are examples of the limitations to these expensive measures. Recent evidence of re-establishment of anadromous runs of sockeye from remnant, isolated kokanee populations following dam removal or modification (e.g., AllouetteLake in British Columbia) may offer hope in re-establishing anadromous life histories in cases where dams have prevented passage.

7. Enhancement activities (particularly hatchery releases and spawning channel construction) is likely to be a key factor in reducing abundance in neighboring, small wild populations. In our assessment, we were unable to functionally track both wild and enhanced sockeye salmon where they intermingle. We strongly recommend adoption of integrated monitoring programs that includes a robust marking program and monitoring efforts targeted toward wild sockeye salmon populations that would provide the data necessary to address the degree to which enhancement practices threaten wild sockeye salmon. It is important to note that two large basins in our assessment (Fraser and Skeena) are all strongly. influenced by enhancement activities, and these activities likely represent a key factor threatening many neighboring subpopulations.

8. While not addressed in the present assessment due to lack of data, we feel there should be more focused research attention on sea-and river-type sockeye that may serve as colonizers in the future. This line of research is particularly important given expected habitat alterations from climate change.

9. Very few data were available to assess population viability of sockeye salmon in the Russian Far East, and we document a significant reduction in escapement in recent years at a site within the KamchatkaRiver basin that warranted an endangered listing for this subpopulation. The leading threat recognized for this subpopulation is overfishing. The situation has been exacerbated by an increase in illegal fishing practices. We encourage the leading agencies in this region to provide more open access to data, and supporting meta-data, for assessment purposes. We also encourage development of new monitoring efforts throughout the region and increased enforcement to reduce poaching. Many populations of river-type sockeye exist, particularly in western Kamchatka, and focused research on these populations will provide important insight into the status of the species there.
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Management Requirements: Allendorf et al. (1997) proposed criteria for prioritizing Pacific salmon stocks for conservation; data limitations introduce subjectivity into the process, so expert judgment and peer review should be incorporated into the process.

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Needs: See Nehlsen et al. (1991) for general protection and management recommendations for anadromous salmonids. See Thomas et al. (1993) for information on habitat management for this and other at-risk fish species in the Pacific Northwest. Waples and Teel (1990) emphasized the importance of monitoring the genetic consequences of the large-scale artificial propagation programs involving Pacific salmon (see also Waples 1990). Meffe (1992) gave reasons why the hatchery approach to recovery ultimately will fail, and he emphasized that overharvest and habitat destruction need to be addressed in a major landscape-level effort.

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Relevance to Humans and Ecosystems

Benefits

Importance

fisheries: highly commercial; aquaculture: commercial; gamefish: yes; aquarium: public aquariums
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Economic Uses

Comments: Important commercial and sport fish; commercially important from Columbia River to Bristol Bay, Alaska; most valuable commercial fishery in both Alaska and British Columbia; important as subsistence and ceremonial fish to indigenous peoples of Alaska, British Columbia, and Washington. See Pauley et al. 1989 for many details on commercial fishery. Has been used in carcinogen testing (Metcalfe 1989).

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Names and Taxonomy

Taxonomy

Comments: Non-anadromous (kokanee) and anadromous (sockeye) forms formerly were considered different subspecies; subsequent studies indicate that the two subspecies (nerka = sockeye; kennerlyi = kokanee) cannot be adequately separated. Sockeye and kokanee salmon in Redfish Lake, Idaho, likely are reproductively isolated (Williams et al. 1992).

Taylor et al. (1996) examined genetic variation among 24 populations ranging from Kamchatka to the Columbia River and identified two major genetic groups: a "northwestern" group (Kamchatka, western Alaska, northwestern British Columbia) and a "southern" group (sockeye and kokanee populations from the Fraser and Columbia river systems). "The populations did not cluster by migratory form, but genetic affinities were organized more strongly by geographic proximity." "Patterns of genetic affinity and allele sharing suggested that kokanee have arisen from sea-run sockeye salmon several times independently in the North Pacific." The authors concluded that "sockeye salmon and kokanee and para- and polyphyletic, respectively, and that the present distribution of the ecotypes results from parallel evolutionary origins of kokanee from sockeye throughout the North Pacific."

Hendry et al. (2000) presented evidence suggesting that reproductive isolation between introduced populations of common origin can evolve after fewer than 13 generations.

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