Oncorhynchus nerka
— Details
Overview
Comprehensive Description
The Sockeye or Red Salmon (Oncorhynchus nerka) is native to northeastern Asia and, in North America, Arctic and Pacific drainages from Point Hope, Alaska, to the Sacramento River drainage in California. Landlocked populations are found in Alaska, Yukon Territory, British Columbia, Washington, and Oregon. This species is relatively common in the northern part of its North American range, but rarer south of the Columbia River drainage. Although it has been widely stocked, most transplant attempts have failed to establish populations. (Page and Burr 1991)
At different periods in the life cycle, Sockeye Salmon are found in the open ocean and, typically, in lakes, which they reach by migrating up coastal streams. Landlocked Sockeye Salmon are known as Kokanee. At sea, these fish are metallic blue and silver, but spawning (breeding) adults are very distinctively colored, turning bright red with a green head. Adults reach a size of around 84 cm in length. (Page and Burr 1991).
Approximately the first half of a Sockeye Salmon's four to six year lifespan is spent in freshwater, while the second half is spent foraging in estuarine and marine waters of the Pacific Ocean. Sockeye Salmon migrate upstream to breed just once, then die. For detailed information on the biology and status of this species, including conservation issues, see this resource from the NOAA Fisheries Office of Protected Resources.
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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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Article rating
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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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
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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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
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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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Article rating
from 0 people
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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Article rating
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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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
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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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Article rating
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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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Article rating
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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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Article rating
from 0 people
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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Geographic Range
Sockeye salmon, Oncorhynchus nerka, are native to the western coast of North America in the Pacific Ocean. They can be located as far north as northern Alaska and as far south as northern California. During the mating season, Sockeye salmon travel inland as far as mid-west Idaho. Populations of this species have also been introduced in some areas of Asia and Russia.
Biogeographic Regions: nearctic (Native ); palearctic (Introduced ); pacific ocean (Native )
Other Geographic Terms: holarctic
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Bickham, J., C. Wood, J. Patton. 1995. Biogeographic Implications of Cytochrome b Sequences and Allozymes in Sockeye (Oncorhynchus nerka). Journal of Heredity, 86/2: 140-144.
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Hasegawa, K., T. Yamamoto, M. Murakami, K. Maekawa. 2004. Comparison of competitive ability between native and introduced salmonids: evidence from pairwise contests. Ichthyological Research, 51/3: 191-194.
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Quinn, T. 2005. The Bahavior and Ecology of Pacific Salmon and Trout. Canada: University of Washington Press.
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Physical Description
Morphology
Physical Description
When sockeye salmon hatch, they lack pigment and thus color. As they grow into fry, they become green and can have black spots. Sockeye salmon are typically blue in color until they reach reproductive age, when they brighten in color; their bodies turn read and their heads green. Additional distinctive markings appear on the head of males and sides of females during the spawning period. When ready to reproduce, sockeye salmon weigh 1 to 4 kg and measure on average 63 cm in length. Sockeye salmon are commonly misidentified. The otolith, or inner ear, of this species is distinct in size and shape from other members of the genus g. Oncorhynchus. This, however, is not always exact as there can be overlap among species in addition to intraspecific differences.
Range mass: 1 to 4 kg.
Average length: 63 cm.
Other Physical Features: ectothermic ; bilateral symmetry
Sexual Dimorphism: male more colorful
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Casteel, R. 1974. Identification of the Species of Pacific Salmon (Genus Oncorhynchus) Native to North America Based upon Otoliths. Copeia, 1974/2: 305-311.
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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
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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).
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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
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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
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from 0 people
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
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Article rating
from 0 people
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
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Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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).
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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).
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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).
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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).
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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
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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
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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
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from 0 people
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
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from 0 people
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
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from 0 people
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
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from 0 people
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
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from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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).
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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).
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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).
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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).
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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).
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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
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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
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from 0 people
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
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from 0 people
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
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from 0 people
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
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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
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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
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Article rating
from 0 people
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
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Article rating
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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
Trusted
Article rating
from 0 people
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).
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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).
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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).
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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).
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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
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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
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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
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from 0 people
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
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from 0 people
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
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from 0 people
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
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from 0 people
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
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from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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).
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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).
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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).
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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).
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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
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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
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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
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from 0 people
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
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from 0 people
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
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from 0 people
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
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from 0 people
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
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from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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).
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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).
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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).
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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).
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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
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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
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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
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from 0 people
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
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from 0 people
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
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from 0 people
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
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from 0 people
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
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from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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).
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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).
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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).
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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).
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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
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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
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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
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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
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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
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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
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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
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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).
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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).
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Sockeye salmon are born in lakes, rivers, or streams, which are calmer than the Pacific Ocean. After fry, or young salmon, develop, they migrate to the Pacific Ocean where they spend most of their life. They are generally found at depths of 15 to 33 m.
Range depth: 15 to 33 m.
Habitat Regions: temperate ; polar ; saltwater or marine ; freshwater
Aquatic Biomes: pelagic ; lakes and ponds; rivers and streams; coastal ; brackish water
Other Habitat Features: estuarine
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Busch, R. 2000. Salmon Country: A History of the Pacific Salmon. Toronto, Ontario: Key Porter Books.
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Groot, C. 1966. On the Orientation of Young Sockeye Salmon (Oncorhynchus nerka) During Their Seaward Migration Out of Lakes. Behaviour Supplement, 13: 8-13.
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Quinn, T., B. Terhart, C. Groot. 1989. Animal Behaviour. Migratory orientation and vertical movements of homing adult sockeye salmon, Oncorhynchus nerka, in coastal waters, 37/4: 587-599.
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Wood, C., C. Foote. 1996. Evidence for Sympatric Genetic Divergence of Anadromous and Nonanadromous Morphs of Sockeye Salmon (Oncorhynchus nerka). Evolution, 50/3: 1265-1267.
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Known from seamounts and knolls
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Trophic Strategy
Food Habits
While in the ocean, sockeye salmon primarily consume zooplankton. In freshwater environments, they are known to eat insects, and, when upstream, occasionally snails.
Animal Foods: insects; mollusks; zooplankton
Primary Diet: planktivore
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Graynoth, E., L. Bennett, J. Pollard. 1986. Diet of landlocked sockeye salmon (Oncorhynchus nerka) and trout in the Waitaki lakes, New Zealand. New Zealand Journal of Marine and Freshwater Research, 20: 537-547.
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Associations
Ecosystem Roles
Sockeye salmon are host to a variety of parasites, which are generally found within the kidney. Most of these parasites release spores when in freshwater where excretion of water by sockeye salmon is high. These parasites include Myxidium salvelini and Parvicapsula minibicornis, both myxosporeans. Sockeye salmon also contribute to the diet of black bears and brown bears.
Commensal/Parasitic Species:
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Higgins, M., L. Margolis, M. Kent. 1993. Arrested Development in a Freshwater Myxosporean, Myxidium salvelini, Following Transfer of Its Host, the Sockeye Salmon (Oncorhynchus nerka), to Sea Water. The Journal of Parasitology, 79/3: 403-406.
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Jones, S., G. Prosperi-Porta, S. Dawe, K. Taylor, B. Goh. 2004. Parvicapsula minibicornis in Anadromous Sockeye (Oncorhynchus nerka) and Coho (Oncorhynchus kisutch) Salmon from Tributaries of the Columbia River. The Journal of Parasitology, 90/4: 882-885.
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Kent, M., D. Whitaker, S. Dawe. 1997. Parvicapsula minibicornis n. sp. (Myxozoa, Myxosporea) from the Kidney of Sockeye Salmon (Oncorhynchus nerka) from British Columbia, Canada. The Journal of Parasitology, 83/6: 1153-1156.
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Predation
Adult sockeye salmon are easily spotted and caught because of their size, and they are eaten by bears, including brown bears and black bears, and birds, such as the mew gull. Predators of frys (young sockeye salmon) include lake trout, squawfish, and mountain whitefish. Most predation occurs in streams and rivers. As frys, sockeye salmon can often escape predators because of their smaller size. Humans also consume a considerable about of sockeye salmon.
Known Predators:
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Groot, C., L. Margolis. 1991. Pacific Salmon: Life Histories. Vancouver: UBC Press.
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Olson, T., R. Squibb, B. Gilbert. 1998. Brown Bear Diurnal Activity and Human Use: A Comparison of Two Salmon Streams. Ursus, 10: 547-548.
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Quinn, T., M. Kinnison. 1999. Size-Selective and Sex-Selective Predation by Brown Bears on Sockeye Salmon. Oecologia, 121/2: 273-274.
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Life History and Behavior
Behavior
Communication and Perception
The eyes of sockeye salmon are located on opposite sides of their head, and they thus have a greater field of vision than animals with two eyes facing forward. The spectrum of visibility of sockeye salmon includes color, from indigo to red, as well as ultraviolet light. Members of this species have nostrils and an enhanced sense of smell. This also adds to their sense of taste. Additionally, sockeye salmon have lateral lines, which detect vibrations, allowing them to hear.
Perception Channels: visual ; ultraviolet; vibrations
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Life Cycle
Development
Sockeye salmon follow the developmental patterns of many pacific salmon. Eggs are externally fertilized by the male. Embryos begin as a single cell with a yolk. After this cell divides, the resulting cells differentiate into specific body type cells until the fetus is developed and ready to hatch, at which time it is called an alevin. Alevins carry the yolk on the anterior end of their body and appear to be clear because they have no pigment. As alevins develop into adults, the yolk shrinks and coloration occurs. Sex of sockeye salmon is initially difficult to determine, but is easily determined later in life by their body shape and coloration.
Development - Life Cycle: metamorphosis ; indeterminate growth
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Williams, R. 2006. Return to the River: Restoring Salmon to the Columbia River. China: Elsevier Academic Press.
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Life Expectancy
Lifespan/Longevity
The average lifespan for sockeye salmon in the wild is 4 to 5 years. The oldest salmon caught was 8 years of age. Typically, sockeye salmon die after mating.
Range lifespan
Status: wild: 8 (high) years.
Typical lifespan
Status: wild: 4 to 5 years.
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Reproduction
Sockeye salmon mate seasonally. Females lay their eggs and are then to select a mate. Males are chosen after they have come along her side and presented themselves multiple times. They are judged on their color and size. During this process, males can be attacked by females and other males. Larger dominant males reproduce more often than other males and, because sockeye salmon are polygynous, the dominant male can mate with many females. Some subordinate males may not have the opportunity to mate at all.
Mating System: polygynous
Sockeye salmon breed from July to October, although some members of this speices located in the southern-most point of their geographic range have been known to breed into December. When females arrive, they create a nest in the gravel in which they lay their eggs. After fertilization, eggs stay in the gravel nest for 32 to 42 days. Females produce 47 to as many as 206 offspring. Sockeye salmon are independent when hatched and are able to reproduce at 4 to 5 years of age.
Breeding interval: Sockeye salmon breed once a year.
Breeding season: Sockeye salmon generally breed from July to October.
Range number of offspring: 47 to 206.
Range time to hatching: 32 to 42 days.
Average time to independence: 0 years.
Range age at sexual or reproductive maturity (female): 4 to 5 years.
Average age at sexual or reproductive maturity (female): 4 to years.
Range age at sexual or reproductive maturity (male): 4 to 5 years.
Key Reproductive Features: iteroparous ; seasonal breeding ; gonochoric/gonochoristic/dioecious (sexes separate); sexual ; fertilization (External ); broadcast (group) spawning; oviparous
Mothers invest time creating gravel nests, in which eggs incubate. After fertilization, however, the newly hatched alevin have no parental investment.
Parental Investment: no parental involvement; female parental care ; pre-fertilization (Protecting: Female); pre-hatching/birth (Provisioning: Female)
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Busch, R. 2000. Salmon Country: A History of the Pacific Salmon. Toronto, Ontario: Key Porter Books.
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Foote, C. 1990. An Experimental Comparison of Male and Female Spawning Territoriality in a Pacific Salmon. Behaviour, 115/3-4: 283-314.
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Lichatowich, J. 1999. Salmon Without Rivers. Washington, DC: Island Press.
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Moore, J., D. Schindler, J. Carter, J. Fox, J. Griffiths, G. Holtgrieve. 2007. Biotic Control of Stream Fluxes: Spawning Salmon Drive Nutrient and Matter Export. Ecology, 88/5: 1278-1291.
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Quinn, T. 2005. The Bahavior and Ecology of Pacific Salmon and Trout. Canada: University of Washington Press.
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Quinn, T., A. Hendry, L. Wetzel. 1995. The Influence of Life History Trade-Offs and the Size of Incubation Gravels on Egg Size Variation in Sockeye Salmon (Oncorhynchus nerka). Oikos, 74/3: 425-427.
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Conservation
Conservation Status
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 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 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 -62%. 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 (14 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.
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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 16 site(s), was 263%. 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 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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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.
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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)
Trusted
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from 0 people
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)
Trusted
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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)
Trusted
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from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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.
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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.
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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.
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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)
Trusted
Article rating
from 0 people
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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from 0 people
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.
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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
Trusted
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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
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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)
Trusted
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from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
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from 0 people
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)
Trusted
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from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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)
Trusted
Article rating
from 0 people
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
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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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Although listed as a species of least concern by the IUCN Red List, the U.S. Fish and Wildlife Service Species Report listed O. nerka as endangered in 1992. In some areas, sockeye salmon are only listed as threatened, as populations have stabilized. Many programs have been implemented to prevent over-fishing and to rejuvenate sockeye populations in areas where over-fishing has occurred.
US Federal List: endangered; threatened
CITES: no special status
State of Michigan List: no special status
IUCN Red List of Threatened Species: least concern
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Trends
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 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.
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
Major Threats General threats to O. nerkaThe 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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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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Major Threats General threats to O. nerkaThe 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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Major Threats General threats to O. nerkaThe 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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Major Threats General threats to O. nerkaThe 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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Major Threats General threats to O. nerkaThe 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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from 0 people
Major Threats General threats to O. nerkaThe 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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Major Threats General threats to O. nerkaThe 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.
Trusted
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from 0 people
Major Threats General threats to O. nerkaThe 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.
Trusted
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from 0 people
Major Threats General threats to O. nerkaThe 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.
Trusted
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from 0 people
Major Threats General threats to O. nerkaThe 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.
Trusted
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from 0 people
Major Threats General threats to O. nerkaThe 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.
Trusted
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from 0 people
Major Threats General threats to O. nerkaThe 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.
Trusted
Article rating
from 0 people
Major Threats General threats to O. nerkaThe 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.
Trusted
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from 0 people
Major Threats General threats to O. nerkaThe 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.
Trusted
Article rating
from 0 people
Major Threats General threats to O. nerkaThe 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.
Trusted
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from 0 people
Major Threats General threats to O. nerkaThe 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.
Trusted
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from 0 people
Major Threats General threats to O. nerkaThe 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.
Trusted
Article rating
from 0 people
Major Threats General threats to O. nerkaThe 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.
Trusted
Article rating
from 0 people
Major Threats General threats to O. nerkaThe 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.
Trusted
Article rating
from 0 people
Major Threats General threats to O. nerkaThe 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.