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Overview
Brief Summary
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Biology
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Description
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Comprehensive Description
Biology
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Page, L.M. and B.M. Burr 1991 A field guide to freshwater fishes of North America north of Mexico. Houghton Mifflin Company, Boston. 432 p. (Ref. 5723)
http://www.fishbase.org/references/FBRefSummary.php?id=5723&speccode=2590
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Description
Aquaculture of Salmo salar is big business and highly contentious. Production has increased dramatically since the 1960s and now dwarfs the wild salmon fisheries (WWF, 2001). Farming salmon to relieve pressure from wild stocks may seem like a good idea but it can have severe environmental consequences. In Britain, salmon farms are established in Scottish sea lochs and in estuaries. Salmon are cultivated in high concentrations, making them susceptible to parasites and disease. The proximity of these farms to wild populations, and the frequency with which cultivated salmon escape, puts the local wild populations at risk, both from the spread of disease and increased competition (Hendry & Cragg-Hine, 2003).
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Distribution
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Müller, Y. (2004). Faune et flore du littoral du Nord, du Pas-de-Calais et de la Belgique: inventaire. [Coastal fauna and flora of the Nord, Pas-de-Calais and Belgium: inventory]. Commission Régionale de Biologie Région Nord Pas-de-Calais: France. 307 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=9269
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Hayward, P.J.; Ryland, J.S. (Ed.) (1990). The marine fauna of the British Isles and North-West Europe: 1. Introduction and protozoans to arthropods. Clarendon Press: Oxford, UK. ISBN 0-19-857356-1. 627 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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Poll, M. (1945). Contribution à la connaissance de la faune ichtyologique du Bas-Escaut. Bull. Mus. royal d'Hist. Nat. Belg./Med. Kon. Natuurhist. Mus. Belg. 21(11): 1-32
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1641
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Hamerlynck, O.; Hostens, K. (1994). Changes in the fish fauna of the Oosterschelde estuary: a ten-year time series of fyke catches. Hydrobiologia 282-283: 497-507
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=1143
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Van Damme, P.A.; Hostens, K.; Ollevier, F.P. (1994). Fish species of the lower Zeeschelde (Belgium): a comparison with historical checklists. Belg. J. Zool. 124(2): 93-103
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=132986
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Gordon, D. (Ed.) (2009). New Zealand Inventory of Biodiversity. Volume One: Kingdom Animalia. 584 pp
http://www.marinespecies.org/porifera/porifera.php?p=sourcedetails&id=145244
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van der Land, J.; Costello, M.J.; Zavodnik, D.; Santos, R.S.; Porteiro, F.M.; Bailly, N.; Eschmeyer, W.N.; Froese, R. (2001). Pisces, in: Costello, M.J. et al. (Ed.) (2001). European register of marine species: a check-list of the marine species in Europe and a bibliography of guides to their identification. Collection Patrimoines Naturels, 50: pp. 357-374
http://www.marbef.org/data/aphia.php?p=sourcedetails&id=1411
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Nozères C., Archambault D., Chouinard P.-M., Gauthier J., Miller R., Parent E., Schwab P., Savard L., and Dutil J.-D. 2010. Identification guide for marine fishes of the estuary and northern Gulf of St. Lawrence and sampling protocols used during trawl surveys between 2004 and 2008. Can. Tech. Rep. Fish. Aquat. Sci. 2866: xi + 243 p
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=145051
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MEDIN (2011). UK checklist of marine species derived from the applications Marine Recorder and UNICORN, version 1.0.
http://www.marinespecies.org/asteroidea/aphia.php?p=sourcedetails&id=149081
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Ramos, M. (ed.). 2010. IBERFAUNA. The Iberian Fauna Databank
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=149024
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Kedra, M. (2010). A Checklist of marine species occurring in Polish marine waters, compiled in the framework of the PESI EU FP7 project.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=149084
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Miller, Roberta. 2011. The St. Anne de Bellevue Arctic Biological Station Collection In Museum collection database, Fisheries and Oceans Canada digital collections, Maurice Lamontagne Institute, Quebec
http://www.marinespecies.org/asteroidea/aphia.php?p=sourcedetails&id=150285
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Gillespie, G. E. 1993. An updated list of the fishes of British Columbia, and those of interest in adjacent waters, with numeric code designations. Can. Tech. Rep. Fish. Aquat. Sci. 1918: 116 p.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=155121
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Dunbar, M.J. & H.H. Hildebrand (1952). Contribution to the study of the fishes of Ungava Bay. Journal of the Fisheries Research Board of Canada 9:83-128, fig. 1. (viii-1952)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=74556
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Hart, J.L., 1973. Pacific Fishes of Canada. Fish. Res. Bd. Can. Bull 180. 740 pages.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=147633
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Breine, J.; Stevens, M.; Van den Bergh, E.; Maes, J. (2011). A reference list of fish species for a heavily modified transitional water: The Zeeschelde (Belgium) Belg. J. Zool. 141(1): 44-55
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=156540
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Miller, Roberta. 2012. The museum collection database, Fisheries and Oceans Canada digital collections, Maurice Lamontagne Institute, Quebec
http://www.marinespecies.org/asteroidea/aphia.php?p=sourcedetails&id=163928
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Dyntaxa (2013) Swedish Taxonomic Database. Accessed at www.dyntaxa.se [15-01-2013].
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=165516
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Page, L.M. and B.M. Burr 1991 A field guide to freshwater fishes of North America north of Mexico. Houghton Mifflin Company, Boston. 432 p. (Ref. 5723)
http://www.fishbase.org/references/FBRefSummary.php?id=5723&speccode=2590
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Geographic Range
The Atlantic salmon is native to the basin of the North Atlantic Ocean, from the Arctic Circle to Portugal in the eastern Atlantic, from Iceland and southern Greenland, and from the Ungava region of northern Quebec south to the Conneticut River (Scott and Crossman, 1973).
Biogeographic Regions: nearctic (Native ); palearctic (Native ); atlantic ocean (Native )
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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National Distribution
Canada
Origin: Native
Regularity: Regularly occurring
Currently: Present
Confidence: Confident
Type of Residency: Year-round
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National Distribution
Canada
Origin: Native
Regularity: Regularly occurring
Currently: Present
Confidence: Confident
Type of Residency: Year-round
United States
Origin: Native
Regularity: Regularly occurring
Currently: Present
Confidence: Confident
Type of Residency: Year-round
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Global Range: North Atlantic, south to Portugal in the east, south to Connecticut and Housatonic rivers in the west (possibly formerly to Delaware); north to Ungava Bay (northern Quebec) and to the Nastapoka River in eastern Hudson Bay (Morin 1991); inland in North America to Lake Ontario, where now extirpated; widely stocked in lakes but seldom successfully. A spawning population, evidently derived from feral adults used for aquaculture, appears to be established in the Tsitika River in British Columbia, and freshwater and marine recoveries are well documented in Alaska (Volpe et al. 2000). Locally common, but depleted or extirpated from western and southern parts of range (Page and Burr 1991). The only remaining populations that are believed to consist, at least in part, of native fishes in U.S. rivers occur in Maine: Dennys, Machias, East Machias, Narraguagus, Pleasant, Ducktrap, and Sheepscot rivers (Colligan and Nickerson 1996); a few populations have been partially restored through hatchery production (Federal Register, 20 January 1994).
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- Bigelow, H. B. and Schroeder, W. C., 1953; Page, L. M. and B. M. Burr, 1991; Billard, R., 1997; Drummond Sedgwick, S., 1982.
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Range
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Physical Description
Morphology
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Keith, P. and J. Allardi (coords.) 2001 Atlas des poissons d'eau douce de France. Muséum national dHistoire naturelle, Paris. Patrimoines naturels, 47:1-387. (Ref. 40476)
http://www.fishbase.org/references/FBRefSummary.php?id=40476&speccode=4683
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Physical Description
Sea-run Atlantic salmon usually attain a larger size than do landlocked (those living in entirely fresh water) salmon. Sea-run salmon range from 2.3 to 9.1 kg and commercially caught fish average 4.5 to 5.4 kg. The world record rod-caught Atlantic salmon weighed 35.89 kg and was caught in the Tana River of Norway.
The adult Atlantic salmon is a graceful fish, deepening rearward from a small pointed head to the deepest point under the dorsal fin, then tapering to a slender caudal peduncle which supports a spreading and slightly emarginate caudal fin. Atlantic salmon are distinguished from the Pacific salmon because they have fewer than 13 rays in the anal fin. Their mouth is moderately large. The shape, length of head, and depth of body vary with each stage of sexual maturity.
Color varies with age of this fish. Small "parr," older young salmon, have 8 to 11 pigmented bars, or "parr marks," along each side of their body, alternating with a single row of red spots along the lateral line. These markings are lost when the "smolt" age is reached. Salmon in the sea are silvery on the sides and belly, while the back varies with shades of brown, green, and blue. Atlantic salmon also have numerous black spots, usually "X"-shaped and scattered around the body. When spawning, both sexes take on an overall bronze-purple coloration and may acquire reddish spots on the head and body. After spawning, the "kelts" are so dark in color that these fish are also called "black salmon"
(Eddy and Underhill, 1974; Bigelow, 1963; Scott and Crossman, 1973).
Range mass: 2.3 to 35.89 kg.
Other Physical Features: ectothermic ; heterothermic ; bilateral symmetry
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Size
Max. size
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Robins, C.R. and G.C. Ray 1986 A field guide to Atlantic coast fishes of North America. Houghton Mifflin Company, Boston, U.S.A. 354 p. (Ref. 7251)
http://www.fishbase.org/references/FBRefSummary.php?id=7251&speccode=942
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Flower, S.S. 1935 Further notes on the duration of life in animals. I. Fishes: as determined by otolith and scale-readings and direct observations on living individuals. Proc. Zool. Soc. London 2:265-304. (Ref. 274)
http://www.fishbase.org/references/FBRefSummary.php?id=274&speccode=2066
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Daymond, J.R. 1963 Family Salmonidae. Sears Found. Mar. Res. Mem. 1(3):457-546. (Ref. 41037)
http://www.fishbase.org/references/FBRefSummary.php?id=41037&speccode=236
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- Bigelow, H. B. and Schroeder, W. C., 1953; Page, L. M. and B. M. Burr, 1991; Billard, R., 1997; Drummond Sedgwick, S., 1982.
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Diagnostic Description
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Keith, P. and J. Allardi (coords.) 2001 Atlas des poissons d'eau douce de France. Muséum national dHistoire naturelle, Paris. Patrimoines naturels, 47:1-387. (Ref. 40476)
http://www.fishbase.org/references/FBRefSummary.php?id=40476&speccode=4683
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Ecology
Habitat
Environment
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Ocean Biogeographic Information System 2006 OBIS-extracted Depth Data. Harvested by E.Agbayani July 2006 at www.iobis.org. (Ref. 57178)
http://www.fishbase.org/references/FBRefSummary.php?id=57178&speccode=4749
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Kangur, M., T. Paaver and T. Drevs 2003 Salmon, Salmo salar L. p. 91-97. In E. Ojaveer, E. Pihu and T. Saat (eds). Fishes of Estonia. Estonian Academy Publishers, Tallinn. 416 p. (Ref. 92381)
http://www.fishbase.org/references/FBRefSummary.php?id=92381&speccode=236
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Seine River Benthopelagic Habitat
This taxon is one of a number of benthopelagic species, whose habitat includes the Seine River system of Western Europe. Benthopelagic fish are found near the bottom of the water column, feeding on benthos and zooplankton
The Marne and Yonne exhibit the greatest torrential flows, due to the percentage of their courses underlain by impermeable strata, in combination with the river gradients. Although the Loing manifests the highest percentage of impermeable strata of all the tributaries, its low gradient mitigates against torrential velocities. Thus the majority of the Seine and its tributaries exhibit a relaxed generally even flow rate.
Seine water pollutant loads of heavy metals, nutrients, sediment and bacteria are relatively high, especially influnced by wastewater and surface runoff from Paris and its suburbs. Parisian pollutant loadings are noted to be particularly high during periods of high rainfall, not only due to high runoff, but also from the inadequate sewage treatment facilities in periods of high combined wastewater/stormwater flow.
Heavy metal concentrations at Poses weir reveal the following levels: copper, 1.9 milligrams per liter; cadmium, 32 mg/l; and lead, 456 mg/l. Concentrations of zinc are also quite high, making the Seine Estuary one of the most highly contaminated estuaries in the world with respect especially to lead and cadmium. Significant amounts of toxic pollutants are also attached to sediments deposited in the Seine during the last two centuries, including mercury, nickel, chromium, toluene, DDT and a variety of herbicides and pesticides. Downriver from Paris, significant quantites of ammonium are discharged into the Seine from effluent of the Achères wastewater treatment plant.
There are a total of 37 fish species inhabiting the Seine, and another two taxa that are known to have been extirpated in modern times. Two of the largest aquatic fauna known to have lived in the Seine are now locally extinct: the 500 centimeter (cm) long sturgeon (Acipenser sturio) and the 83 cm long allis shad (Alosa alosa).
The largest bentho-pelagic species occurring in the Seine are:
* the introduced 105 cm silver carp (Hypophthalmichthys molitrix);
* the native 120 cm barbel (Hypophthalmichthys molitrix);
* the native 150 cm Atlantic salmon (Salmo salar); and,
* the native 500 cm Wels catfish (Silurus glanis).
- C.Michael Hogan. 2012. ''Seine River. Encyclopedia of Earth, National Council for Science and the Environment, Washington DC ed. Peter Saundry; ed.in-chief C.M.Hogan
- Fishbase. 2010. Species in Seine
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Habitat and Ecology
Systems
- Freshwater
- Marine
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The Atlantic salmon is an anadromous species, living in fresh water for at least the first 2 or 3 years of life before migrating to sea. Relatively large cool rivers with extensive gravelly bottom headwaters are essential during their early life. Smolts migrate to sea where they may live for 1 or 2 years before returning to fresh water. The movements of Atlantic salmon at sea are not well understood. Tagging has shown that while some salmon wander, the great majority return to the river in which they were spawned. When at sea, salmon seem to prefer temperatures of 4 to 12 C. They may withstand exposure to temperatures in their lower lethal limit (-.7 C) and their upper lethal limit (27.8 C), but only for a short period of time (Bigelow, 1963).
Habitat Regions: temperate ; saltwater or marine ; freshwater
Aquatic Biomes: rivers and streams; coastal
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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North-West Atlantic Ocean species (NWARMS)
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=2901
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Water temperature and chemistry ranges based on 33 samples.
Environmental ranges
Depth range (m): 0 - 210
Temperature range (°C): -0.404 - 9.505
Nitrate (umol/L): 1.687 - 13.503
Salinity (PPS): 8.500 - 34.117
Oxygen (ml/l): 2.247 - 7.806
Phosphate (umol/l): 0.354 - 1.719
Silicate (umol/l): 3.300 - 48.967
Graphical representation
Depth range (m): 0 - 210
Temperature range (°C): -0.404 - 9.505
Nitrate (umol/L): 1.687 - 13.503
Salinity (PPS): 8.500 - 34.117
Oxygen (ml/l): 2.247 - 7.806
Phosphate (umol/l): 0.354 - 1.719
Silicate (umol/l): 3.300 - 48.967
Note: this information has not been validated. Check this *note*. Your feedback is most welcome.
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Habitat Type: Freshwater
Comments: Rocky runs and pools of small to large rivers; lakes (Page and Burr 1991). Young remain in gravelly streams for 1-5 years (generally 1-2 years, but up to 8 years in some areas), then (as smolts) enter sea (or lake in landlocked populations) and remain there for 1-4 years. Migration habitat between spawning area and ocean optimally should have a minimum of slow- or no-flow areas. At sea, may remain within influence of estuary or move as far as Greenland. Prior to spawning, holds in streams through summer and early fall; optimum conditions include pools of 6 ft or more, water velocity below 1.6 ft/sec, and temperatures of 50-54 F (Clark et al. 1993).
Spawns in streams, usually in gravel-bottomed riffle above or below a pool. In Canada, streams with pH below 4.7 have no exisiting salmon runs; no impact was observed in streams with pH above 5.4 (Watt 1986, cited by Clark et al. 1993). Eggs are laid in a nest and covered with gravel. Normal egg development requires water temperatures less than 50 F (optimum 43 F). Rearing habitat includes shallow riffle areas interrupted by pools and deeper riffles. Parr require cover such as large rocks. Adults die or return to sea after spawning (males sometimes overwinter in stream). Usually spawns in natal stream.
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- Bigelow, H. B. and Schroeder, W. C., 1953; Page, L. M. and B. M. Burr, 1991; Billard, R., 1997; Drummond Sedgwick, S., 1982.
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Migration
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Kangur, M., T. Paaver and T. Drevs 2003 Salmon, Salmo salar L. p. 91-97. In E. Ojaveer, E. Pihu and T. Saat (eds). Fishes of Estonia. Estonian Academy Publishers, Tallinn. 416 p. (Ref. 92381)
http://www.fishbase.org/references/FBRefSummary.php?id=92381&speccode=236
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Introduction
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Nijssen, H.; de Groot, S.J. (1987). De vissen van Nederland: systematische indeling, historisch overzicht, het ontstaan van de viskweek, uitheemse vissoorten, determineersleutels, beschrijvingen, afbeeldingen, literatuur, van alle in Nederlandse wateren voor komende zee- en zoetwatervissoorten [Fishes of the Netherlands: systematic classification, historical overview, origins of fish culture, non-indigenous species, determination keys, descriptions, drawings, literature references on all marine and freshwater fish species living in Dutch waters]. KNNV Uitgeverij: Utrecht, The Netherlands. ISBN 90-5011-006-1. 224 pp.
http://www.marinespecies.org/aphia.php?p=sourcedetails&id=73
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Non-Migrant: No. All populations of this species make significant seasonal migrations.
Locally Migrant: No. No populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).
Locally Migrant: No. No populations of this species make annual migrations of over 200 km.
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Non-Migrant: Yes. At least some populations of this species do not make significant seasonal migrations. Juvenile dispersal is not considered a migration.
Locally Migrant: Yes. At least some populations of this species make local extended movements (generally less than 200 km) at particular times of the year (e.g., to breeding or wintering grounds, to hibernation sites).
Locally Migrant: Yes. At least some populations of this species make annual migrations of over 200 km.
Migrates up to thousands of kilometers between freshwater spawning habitat and marine nonspawning habitat. A number of native landlocked populations are known. Resident and anadromous populations may be sympatric in some areas. Returns to natal stream in spring. In New England, adults ascend rivers beginning in spring, with a peak in June and continuing into fall.
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Trophic Strategy
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Muus, B.J. and P. Dahlström 1974 Collins guide to the sea fishes of Britain and North-Western Europe. Collins, London, UK. 244 p. (Ref. 173)
http://www.fishbase.org/references/FBRefSummary.php?id=173&speccode=24
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Food Habits
Young Atlantic salmon in streams eat mainly the larvae of aquatic insects such as blackflies, stoneflies, caddisflies, and chironomids. Terrestrial insects may also be important, especially in late summer. When at sea, salmon eat a variety of marine organisms. Plankton such as euphausiids are important food for pre-grisle but amphipods and decapods are also consumed. Larger salmon eat a variety of fishes such as herring and alewives, smelts, capelin, small mackerel, sand lace, and small cod. Prior to spawning, salmon cease to feed; they do not eat after they re-enter fresh water to spawn, despite their apparent willingness to take an artificial fly (Bigelow, 1963).
Animal Foods: fish; insects; aquatic crustaceans; other marine invertebrates; zooplankton
Primary Diet: carnivore (Piscivore , Insectivore , Eats non-insect arthropods)
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Comments: Adults eat fishes and crustaceans (euphausiids, amphipods, decapods) in salt water, do not feed in fresh water. Young in streams eat mainly aquatic insect larvae and terrestrial insects (Scott and Crossman 1973), sometimes fish eggs.
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- Bigelow, H. B. and Schroeder, W. C., 1953; Page, L. M. and B. M. Burr, 1991; Billard, R., 1997; Drummond Sedgwick, S., 1982.
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Associations
Known prey organisms
Baetis
Micronecta poweri
Chimarrha marginata
Chironomidae
Bacillariophyceae
algae
protozoa
Leuctra
Ephemeroptera
Diptera
Entomostraca
Collembola
Helmidae
Based on studies in:
Wales, Dee River (River)
This list may not be complete but is based on published studies.
- R. M. Badcock, 1949. Studies in stream life in tributaries of the Welsh Dee. J. Anim. Ecol. 18:193-208, from pp. 202-206 and Price, P. W., 1984, Insect Ecology, 2nd ed., New York: John Wiley, p. 23
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Diseases and Parasites
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Lannan, C.N., J.L. Batholomew and J.L. Fryer 1999 Chlamydial infections of fish: Epitheliocystis. p.255-267. In P.T.K. Woo and D.W. Bruno (eds.) Fish Diseases and Disorders Vol. 3: Viral, bacterial and fungal infections. CABI Int'l. (Ref. 48851)
http://www.fishbase.org/references/FBRefSummary.php?id=48851&speccode=2594
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Horne, M.T. and A.C. Barnes 1999 Enteric redmouth disease (Yersinia ruckeri). p.455-477. In P.T.K. Woo and D.W. Bruno (eds.) Fish Diseases and Disorders, Vol. 3: Viral, Bacterial and Fungal Infections. CAB Int'l. (Ref. 48849)
http://www.fishbase.org/references/FBRefSummary.php?id=48849&speccode=35
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Plumb, J.A. 1999 Edwardsiella Septicaemias. p.479-521. In P.T.K. Woo and D.W. Bruno (eds.) Fish Diseases and Disorders, Vol. 3: Viral, Bacterial and Fungal Infections. CAB Int'l. (Ref. 48850)
http://www.fishbase.org/references/FBRefSummary.php?id=48850&speccode=2
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Population Biology
Global Abundance
10,000 to >1,000,000 individuals
Comments: As of 2000, the estimated annual number of spawners in eastern North America was about 350,000, down from 1.5 million 30 years ago (Anderson et al. 2000). As of the late 1980s, New England population included about 3000-7000 adults returning to 16 rivers; of these, 1500-2500 were believed to be of wild origin. Prior to European colonization, Maine spawning runs may have been 125,000-500,000 (Beland 1984, cited by Clark et al. 1993). See Clark et al. (1993) and USFWS (1995) for information on current status in Maine.
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Life History and Behavior
Behavior
Communication and Perception
Salmon have a great sense of smell, hearing, and taste which helps them find food and sense danger. Salmon are also able to sense danger by feeling the waves on their body.
Atlantic salmon also use their senses to find and return to their home river. Through imprinting, young fry memorize details about their home streams, and they use this knowledge as adult spawners to find their way back. Scientists are not exactly sure how salmon complete this feat, but some theories are the salmon use the sun and stars as navigational guides, while others claim these fish have stored the taste of their home water in their brain. Most feel that salmon are guided home by the characteristic odor of the parent stream which is imprinted during the smolts' migration (Maynor, 1996).
Communication Channels: visual ; tactile ; chemical
Perception Channels: visual
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Life Cycle
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Balon, E.K. 1990 Epigenesis of an epigeneticist: the development of some alternative concepts on the early ontogeny and evolution of fishes. Guelph Ichthyol. Rev. 1:1-48. (Ref. 7471)
http://www.fishbase.org/references/FBRefSummary.php?id=7471&speccode=4669
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Development
Hatching of the eggs usually occurs in April but the young remain in the gravel until the yolk sac is absorbed and finally emerge in May or June of the year following egg deposition. The newly hatched salmon, called "alevins," remain in rapid water until they are about 65mm long. The fish are now called "parr," and their growth is slow. Parr are called "smolts" when they reach a length of 12 to 15 cm and are ready to go to sea. Salmon grow rapidly while at sea. Some may return to the river to spawn after one year at sea, as "grilse," or may spend 2 years at sea, as "2 sea-year salmon" (Bigelow, 1963; Scott and Crossman, 1973).
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Life Expectancy
Lifespan/Longevity
Range lifespan
Status: wild: 3 (high) years.
Average lifespan
Status: captivity: 3.3 years.
Average lifespan
Status: wild: 5.0 years.
Average lifespan
Status: wild: 13.0 years.
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Lifespan, longevity, and ageing
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Reproduction
Atlantic salmon spawn in October and November, the peak of spawning usually occurring in late October. As spawning time nears, males undergo conspicuous changes in head shape: the head elongates and a pronounced hook, or kype, develops on the tip of the lower jaw. The nesting site is chosen by the female, usually a gravel-bottom riffle above a pool. The female digs the nest, called the "redd," by flapping strongly with her caudal fin and peduncle while on her side; the redd is formed by her generated water currents. The female rests freely during redd preparation while the male continues to court her and drive away other males. When the redd is finished, the male aligns himself next to the female, the eggs and sperm are released, and the eggs are fertilized during the intermingling of the gametes. On average, a female deposits 700-800 eggs per pound of her body weight. The eggs are pale orange in color, large and spherical, and somewhat adhesive for a short time. The female then covers the eggs with gravel, using the same method used to create the redd. The eggs are buried in gravel at a depth of about 12.7 to 25.4 cm.
The female rests after spawning and then repeats the operation, creating a new redd, depositing more eggs, and resting again until spawning is complete. The male continues to court and drive off intruders. Complete spawning by individuals may take a week or more, by which time the spawners are exhausted. Some Atlantic salmon die after spawning but many survive to spawn a second time; a very few salmon spawn three or more times.
Spawning completed, the fish, now called "kelts," may drop downriver to a pool and rest for a few weeks, or they may return at once to the ocean. Some may also remain in the river over winter and return to sea in the spring.
Hatching of the eggs usually occurs in April but the young remain in the gravel until the yolk sac is absorbed and finally emerge in May or June of the year following egg deposition. The newly hatched salmon, called "alevins," remain in rapid water until they are about 65mm long. The fish are now called "parr," and their growth is slow. Parr are called "smolts" when they reach a length of 12 to 15 cm and are ready to go to sea. Salmon grow rapidly while at sea. Some may return to the river to spawn after one year at sea, as "grilse," or may spend 2 years at sea, as "2 sea-year salmon" (Bigelow, 1963; Scott and Crossman, 1973).
Breeding interval: Breed once yearly, few breed twice before dying
Breeding season: October and November
Range age at sexual or reproductive maturity (female): 1 to 2 years.
Range age at sexual or reproductive maturity (male): 1 to 2 years.
Key Reproductive Features: seasonal breeding ; gonochoric/gonochoristic/dioecious (sexes separate); sexual ; fertilization (External ); oviparous
There is no parental investment beyond spawning.
Parental Investment: pre-fertilization (Provisioning)
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Spawns in fall (late October and early November in Maine). Eggs hatch in early spring. Young spend 1-3 years in stream rearing habitat, go to sea (in spring), return to spawn after 1-4 winters at sea (most from New England spend two years at sea). Adults may spawn in more than one year. In Europe, the majority of the smallest adults spawned annually, the largest biennially (Jonsson et al. (1991). Apparently, severe post-spawning mortality is normal in natural habitats, but survivorship generally is higher in artificially "reconditioned" kelts or in lake-locked populations (Stearley 1992).
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- Bigelow, H. B. and Schroeder, W. C., 1953; Page, L. M. and B. M. Burr, 1991; Billard, R., 1997; Drummond Sedgwick, S., 1982.
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Evolution and Systematics
Functional Adaptations
Functional adaptation
Salmon can spend part of their lives in freshwater and part in seawater due to adaptive changes in their physiology.
"The Atlantic salmon (Salmo salar) begins its life in a river, in the wild mountain streams of Norway or Scotland, hatching from an egg there in springtime. The salmon usually spends up to four years in the river before beginning the outward phase of its marathon migration as a smolt (a young salmon ready to migrate to the sea), traveling downriver to the ocean. During this period, the smolt's physiology adapts to enable it to live in seawater." (Shuker 2001:76)
Learn more about this functional adaptation.
- Shuker, KPN. 2001. The Hidden Powers of Animals: Uncovering the Secrets of Nature. London: Marshall Editions Ltd. 240 p.
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Functional adaptation
Salmon identify a specific spawning river using their keen olfactory sense.
"The salmon's extraordinary ability to locate the river where it was born is due to its highly developed olfactory sense, which enables it to distinguish between different rivers by scent." (Shuker 2001:76)
Learn more about this functional adaptation.
- Shuker, KPN. 2001. The Hidden Powers of Animals: Uncovering the Secrets of Nature. London: Marshall Editions Ltd. 240 p.
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Molecular Biology and Genetics
Molecular Biology
Barcode data: Salmo salar
There are 114 barcode sequences available from BOLD and GenBank. Below is a sequence of the barcode region Cytochrome oxidase subunit 1 (COI or COX1) from a member of the species. See the BOLD taxonomy browser for more complete information about this specimen and other sequences.
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Download FASTA File
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Statistics of barcoding coverage: Salmo salar
Public Records: 121
Specimens with Barcodes: 154
Species With Barcodes: 1
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Conservation
Conservation Status
IUCN Red List Assessment
Red List Category
Red List Criteria
Version
Year Assessed
- Needs updating
Assessor/s
Reviewer/s
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North America's population of large salmon is at its lowest point in history. Declining numbers and loss of whole stocks in some rivers are causing increasing concern. Habitat destruction, denial of access to spawning grounds by dams and other obstructions, overfishing (including high-seas fishing and poaching), pollution, and especially acid rain are taking their toll. Cooperation and compromise by the major groups harvesting Atlantic salmon are essential if native stocks are to be saved. Scientific research has led to the creation of artificial spawning channels which provide a significant supplement to the production of salmon from natural streams. The Atlantic Salmon Federation is the largest, most effective organization devoted to the conservation of the Atlantic salmon and its habitat. This group has been successful in reducing commercial salmon fishing and some salmon streams have reported encouraging increases in the number of returning sea run fish as a result (Scott and Crossman, 1973; Atlantic Salmon Federation, 1996). Atlantic salmon are listed as lower risk by the IUCN, and they are considered an endangered species by the U.S. Fish and Wildlife Service.
US Federal List: endangered
CITES: no special status
State of Michigan List: no special status
IUCN Red List of Threatened Species: lower risk - least concern
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National NatureServe Conservation Status
Canada
Rounded National Status Rank: N4 - Apparently Secure
United States
Rounded National Status Rank: N4 - Apparently Secure
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NatureServe Conservation Status
Rounded Global Status Rank: G5 - Secure
Reasons: Large breeding range in streams draining into the North Atlantic; many populations in the U.S. have been extirpated or have declined, but there are many occurrences and large numbers elsewhere; principal threats are habitat loss/degradation and overharvest.
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Status: Endangered
Date Listed: 07/20/2009
Lead Region: Northeast Region (Region 5)
Where Listed: U.S.A., ME, Gulf of Maine Distinct Population Segment. The GOM DPS includes all anadromous Atlantic salmon whose freshwater range occurs in the watersheds from the Androscoggin River northward along the Maine coast to the Dennys River, and wherever these fish occur in the estuarine and marine environment. The following impassable falls delimit the upstream extent of the freshwater range: Rumford Falls in the town of Rumford on the Androscoggin River; Snow Falls in the town of West Paris on the Little Androscoggin River; Grand Falls in Township 3 Range 4 BKP WKR, on the Dead River in the Kennebec Basin; the un-named falls (impounded by Indian Pond Dam) immediately above the Kennebec River Gorge in the town of Indian Stream Township on the Kennebec River; Big Niagara Falls on Nesowadnehunk Stream in Township 3 Range 10 WELS in the Penobscot Basin; Grand Pitch on Webster Brook in Trout Brook Township in the Penobscot Basin; and Grand Falls on the Passadumkeag River in Grand Falls Township in the Penobscot Basin. The marine range of the GOM DPS extends from the Gulf of Maine, throughout the Northwest Atlantic Ocean, to the coast of Greenland. Included are all associated conservation hatchery populations used to supplement these natural populations; currently, such conservation hatchery populations are maintained at Green Lake National Fish Hatchery (GLNFH) and Craig Brook National Fish Hatchery (CBNFH). Excluded are landlocked salmon and those salmon raised in commercial hatcheries for aquaculture.
Population detail:
Population location: U.S.A., ME, Gulf of Maine Distinct Population Segment. The GOM DPS includes all anadromous Atlantic salmon whose freshwater range occurs in the watersheds from the Androscoggin River northward along the Maine coast to the Dennys River, and wherever these fish occur in the estuarine and marine environment. The following impassable falls delimit the upstream extent of the freshwater range: Rumford Falls in the town of Rumford on the Androscoggin River; Snow Falls in the town of West Paris on the Little Androscoggin River; Grand Falls in Township 3 Range 4 BKP WKR, on the Dead River in the Kennebec Basin; the un-named falls (impounded by Indian Pond Dam) immediately above the Kennebec River Gorge in the town of Indian Stream Township on the Kennebec River; Big Niagara Falls on Nesowadnehunk Stream in Township 3 Range 10 WELS in the Penobscot Basin; Grand Pitch on Webster Brook in Trout Brook Township in the Penobscot Basin; and Grand Falls on the Passadumkeag River in Grand Falls Township in the Penobscot Basin. The marine range of the GOM DPS extends from the Gulf of Maine, throughout the Northwest Atlantic Ocean, to the coast of Greenland. Included are all associated conservation hatchery populations used to supplement these natural populations; currently, such conservation hatchery populations are maintained at Green Lake National Fish Hatchery (GLNFH) and Craig Brook National Fish Hatchery (CBNFH). Excluded are landlocked salmon and those salmon raised in commercial hatcheries for aquaculture.
Listing status: E
For most current information and documents related to the conservation status and management of Salmo salar , see its USFWS Species Profile
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Status
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Threats
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IUCN 2006 2006 IUCN red list of threatened species. www.iucnredlist.org. Downloaded July 2006.
http://www.fishbase.org/references/FBRefSummary.php?id=57073
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Comments: Native U.S. populations south of Maine are essentially extirpated due primarily to the effects of dams and water pollution; excessive harvest of adults by humans, stream acidification, sedimentation of spawning and holding habitat, and possibly changes in water temperature regimes contributed to the decline in some areas. Evidence from New England indicates that landlocked populations of Atlantic salmon may be negatively influenced as abundance of northern pike and/or Esox hybrids increases. In the U.S., some of these threats have been alleviated; water quality has improved in recent decades, and fish ladders have been constructed at many dams; reintroduction programs are in progress. Poor marine survival continues to result in reduced returns to U.S. rivers (USFWS 1995, Anderson et al. 2000); depletion of forage species by commercial fisheries and freshwater exposure of juveniles to an endocrine disrupter (leads to mortality in marine phase) are suggested possible causes. Escaped farmed salmon may pose a threat to native populations in coastal Maine rivers (USFWS 1995). See USFWS (1995), NMFS (Federal Register, 29 September 1995), Colligan and Nickerson (1996), and Anderson et al. (2000) for further information on threats to North American populations.
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Management
Management Requirements: See Mills and Piggins (1988) and Mills (1989). See Clark et al. (1993) for a summary of management efforts in Maine. See Kornfield et al. (1995) for management recommendations for Maine populations. See "Maine Atlantic Salmon Restoration and Management Plan 1995-2000." See "Atlantic Salmon Conservation Plan for Seven Maine Rivers."
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Needs: See USFWS (1997) for an explanation of the decision to withdraw the proposed rule to list a distinct population segment in Maine as threatened. See "Review of the status of anadromous salmon (Salmo salar) under the U.S. Endangered Species Act, July, 1999," available from USFWS (Paul Nickerson, 413-253-8615, Hadley, Massachusetts).
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Conservation
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Relevance to Humans and Ecosystems
Benefits
Importance
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Garibaldi, L. 1996 List of animal species used in aquaculture. FAO Fish. Circ. 914. 38 p. (Ref. 12108)
http://www.fishbase.org/references/FBRefSummary.php?id=12108&speccode=4683
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International Game Fish Association 1991 World record game fishes. International Game Fish Association, Florida, USA. (Ref. 4699)
http://www.fishbase.org/references/FBRefSummary.php?id=4699&speccode=2590
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FAO Fishery Information, Data and Statistics Service 1993 Aquaculture production (1985-1991). FAO Fish. Circ. 815, Rev. 5. 213 p. (Ref. 7306)
http://www.fishbase.org/references/FBRefSummary.php?id=7306&speccode=457
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Economic Importance for Humans: Positive
The Atlantic salmon is renowned among game fishermen and is a highly prized food fish. Because of the strong market demand, an active aquaculture industry, which involves cage-rearing, hatcheries, and some sea ranching, has been developed all over the world. The commercial yield of the Atlantic salmon is estimated to be in the millions of dollars with expected annual doubling in the future (Scott and Crossman, 1973).
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Risks
Species Impact: A non-native population apparently established in British Columbia raises concerns that Atlantic salmon could jeopardize native Pacific salmonids "through competition for resources and occupation of niches that are currently underutilized" (Volpe et al. 2000).
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Wikipedia
Atlantic salmon
| This article's lead section may not adequately summarize key points of its contents. (December 2012) |
The Atlantic salmon, Salmo salar, is a fish in the family Salmonidae, which is found in the northern Atlantic Ocean and in rivers that flow into the north Atlantic and, due to human introduction, the north Pacific.[2][3]
It is also commercially known as bay salmon, black salmon, caplin-scull salmon, fiddler, grilse, grilt, kelt, landlocked salmon, ouananiche, outside salmon, parr, Sebago salmon, silver salmon, slink, smolt, spring salmon, or winnish.[4]
Contents |
Life stages[edit]
Most Atlantic salmon follow an anadromous fish migration pattern,[3] in that they undergo their greatest feeding and growth in salt water; however, adults return to spawn in native freshwater streams where the eggs hatch and juveniles grow through several distinct stages.
Atlantic salmon do not require salt water. Numerous examples of fully freshwater (i.e., "landlocked") populations of the species exist throughout the Northern Hemisphere.[3] In North America, the landlocked strains are frequently known as ouananiche.
Freshwater phase[edit]
The freshwater phases of Atlantic salmon vary between one and eight years, variably according to river location.[5] While the young in southern rivers, such as those to the English Channel, are only one year old when they leave, those further north, such as in Scottish rivers, can be over four years old, and in Ungava Bay, northern Quebec, smolts as old as eight years have been encountered.[5] The average age correlates to temperature exceeding 7°C (45°F).[2]
The first phase is the alevin stage, when the fish stay in the breeding ground and use the remaining nutrients in their yolk sacs. During this developmental stage, their young gills develop and they become active hunters. Next is the fry stage, where the fish grow and subsequently leave the breeding ground in search of food. During this time, they move to areas with higher prey concentration. The final freshwater stage is when they develop into parr, in which they prepare for the trek to the Atlantic Ocean.
During these times, the Atlantic salmon are very susceptible to predation. Nearly 40% are eaten by trout alone. Other predators include other fish and birds.[citation needed]
Saltwater phases[edit]
When parr develop into smolt, they begin the trip to the ocean, which predominantly happens between March and June. Migration allows acclimation to the changing salinity. Once ready, young smolt leave, preferring an ebb tide.
Having left their natal streams, they experience a period of rapid growth during the one to four years they live in the ocean. Typically, Atlantic salmon migrate from their home streams to an area on the continental plate off West Greenland. During this time, they face predation from humans, seals, Greenland sharks, skate, cod, and halibut. Some dolphins have been noticed playing with dead salmon, but it is still unclear whether they consume them.
Once large enough, Atlantic salmon change into the grilse phase, when they become ready to return to the same freshwater tributary they departed from as smolts. After returning to their natal streams, the salmon will cease eating altogether prior to spawning. Although largely unknown, odor – the exact chemical signature of that stream – may play an important role in how salmon return to the area where they hatched. Once heavier than about 250 g, the fish no longer become prey for birds and many fish, although seals do prey upon them. Grey and common seals commonly eat Atlantic salmon. Survivability to this stage has been estimated at between 14 and 53%.[2]
Nomenclature[edit]
The Atlantic salmon was given its scientific binomial name by zoologist and taxonomist Carl Linnaeus in 1758. Later, the differently coloured smolts were found to be the same species.
The name, Salmo salar, is from the Latin salmo, meaning salmon, and salar, meaning leaper, according to M. Barton,[6] but more likely meaning "resident of salt water". Lewis and Short's Latin Dictionary (Clarendon Press, Oxford, 1879) translates salar as a kind of trout from its use in the Idylls of the poet Ausonius (4th century CE).
Physiology[edit]
This is a fairly large salmonid, with average adult specimens measuring 71 to 76 cm (28 to 30 in) long and weighing 3.6 to 5.4 kg (7.9 to 12 lb).[7] Record-sized specimens have been measured to a maximum of 153 cm (60 in) and a weight of 45 kg (99 lb).[8] The colouration of young Atlantic salmon does not resemble their adult stage. While they live in fresh water, they have blue and red spots. While they mature, they take on a silver-blue sheen. When adult, the easiest way of identifying them is by the black spots predominantly above the lateral line, although the caudal fin is usually unspotted. When they reproduce, males take on a slight green or red colouration. The salmon has a fusiform body, and well-developed teeth. All fins, save the adipose, are bordered with black.
Distribution and habitat[edit]
At sea, the species is found mainly in the waters off Greenland and in migrations to and from its natal streams, along the northern eastern and western Atlantic coasts. Wild salmon disappeared from many rivers during the twentieth century due to overfishing and habitat change.[2] By 2000 the numbers of Atlantic salmon had dropped to critically low levels.[10]
Diet[edit]
Young salmon begin a feeding response within a few days. After the yolk sac is absorbed by the body, they begin to hunt. Juveniles start with tiny invertebrates, but as they mature, they may occasionally eat small fish. During this time, they hunt both in the substrate and in the current. Some have been known to eat salmon eggs. The most commonly eaten foods include caddisflies, blackflies, mayflies, and stoneflies.[2]
As adults, the fish feed on much larger food: Arctic squid, sand eels, amphipods, Arctic shrimp, and sometimes herring, and the fishes' size increases dramatically.[2]
Behaviour[edit]
Fry and parr have been said to be territorial, but evidence showing them to guard territories is inconclusive. While they may occasionally be aggressive towards each other, the social hierarchy is still unclear. Many have been found to school, especially when leaving the estuary.
Adult Atlantic salmon are considered much more aggressive than other salmon, and are more likely to attack other fish than others. Where they have become an invasive threat, attacking native salmon, such as Chinook salmon and coho salmon, has become a concern.[2]
Breeding[edit]
Atlantic salmon breed in the rivers of Western Europe from northern Portugal north to Norway, Iceland, and Greenland, and the east coast of North America from Connecticut in the United States north to northern Labrador and Arctic Canada. Atlantic salmon which have escaped from the aquaculture industry have also been found breeding in rivers tributary to the Pacific Ocean in British Columbia on Canada's west coast.[citation needed] The species constructs a nest or "redd" in the gravel bed of a stream. The female creates a powerful downdraught of water with her tail near the gravel to excavate a depression. After she and a male fish have eggs and milt (sperm), respectively, upstream of the depression, the female again uses her tail, this time to shift gravel to cover the eggs and milt which have lodged in the depression.
Unlike the various Pacific salmon species which die after spawning (semelparous), the Atlantic salmon is iteroparous, which means the fish may recondition themselves and return to the sea to repeat the migration and spawning pattern several times, although most spawn only once or twice.[3][11] Migration and spawning exact an enormous physiological toll on individuals, such that repeat spawners are the exception rather than the norm.[11] Atlantic salmon show high diversity in age of maturity and may mature as parr, one- to five-sea-winter fish, and in rare instances, at older sea ages. This variety of ages can occur in the same population, constituting a ‘bet hedging’ strategy against variation in stream flows. So in a drought year, some fish of a given age will not return to spawn, allowing that generation other, wetter years in which to spawn.[5]
Very young fertilised salmon eggs, notice the developing eyes and neural tube
A newly hatched Atlantic salmon alevin which, within around 24 hours, will absorb the yolk sac and become a fry
Hybridization[edit]
When in shared breeding habitats, Atlantic salmon will hybridize with brown trout (Salmo trutta).[12][13][14] Hybrids between Atlantic salmon and brown trout were detected in two of four watersheds studied in northern [Spain]. The proportions of hybrids in samples of 'salmon' ranged from 0 to 7-7% but they were not significantly heterogeneous among locations, resulting in a mean hybridization rate of 2-3%. This is the highest rate of natural hybridization so far reported and is significantly greater than rates observed elsewhere in Europe.[15]
Aquaculture[edit]
In its natal streams, Atlantic salmon are considered prized recreational fish, pursued by fly anglers during its annual runs. At one time, the species supported an important commercial fishery and a supplemental food fishery. However, the wild Atlantic salmon fishery is commercially dead; after extensive habitat damage and overfishing, wild fish make up only 0.5% of the Atlantic salmon available in world fish markets. The rest are farmed, predominantly from aquaculture in Norway, Chile, Canada, the UK, Ireland, Faroe Islands, Russia and Tasmania in Australia. Sport fishing communities, mainly from Iceland and Scandinavia, have joined in the North Atlantic Salmon Fund to buy away commercial quotas in an effort to save the wild species of Salmo salar.[11]
Process[edit]
Adult male and female fish are anaesthetised; their eggs and sperm are "stripped" after the fish are cleaned and cloth dried. Sperm and eggs are mixed, washed, and placed into fresh water. Adults recover in flowing, clean, well-aerated water.[16] Some researchers have even studied cryopreservation of their eggs.[17]
Fry are generally reared in large freshwater tanks for 12 to 20 months. Once the fish have reached the smolt phase, they are taken out to sea, where they are held for up to two years. During this time, the fish grow and mature in large cages off the coasts of Canada, the USA, or parts of Europe.[11]
Generally, cages are made of two nets. Inner nets, which wrap around the cages, hold the salmon. Outer nets, which are held by floats, keep predators out.[16]
Controversy[edit]
In the past, some Atlantic salmon have escaped from cages at sea. In the Atlantic Ocean, this has resulted in some breeding with native populations, but generally most surviving offspring were from the domesticated Atlantics, not hybrids.
On the West Coast of Northern America, aquaculturists have taken great care to ensure the non-native salmon cannot escape from their open-net pens, and escape is no longer considered a major concern. Evidence of Atlantic salmon surviving and establishing wild populations in the Pacific is lacking. From 1905 until 1935, in excess of 8.6 million Atlantic salmon of various life stages (predominantly advanced fry) were intentionally introduced to more than 60 individual BC lakes and streams. Historical records indicate, in a few instances, mature sea-run Atlantic salmon were captured in the Cowichan River; however, a self-sustaining population never materialized. Environmental assessments by the US National Marine Fisheries Service (NMFS), the Washington Department of Fish and Wildlife and the BC Environmental Assessment Office have concluded the potential risk of Atlantic salmon colonization in the Pacific Northwest is low.[18]
Human impact[edit]
Human activities have heavily damaged salmon populations across their range. The major impacts were from overfishing and habitat change, and the new threat from competitive farmed fish. Salmon decline in Lake Ontario goes back to the 18th–19th centuries, due to logging and soil erosion, as well as dam and mill construction. By 1896, the species was declared extirpated from the lake.[19] When dams were constructed on the Oswego River, their spawning areas were cut off and they went extinct locally.
In the 1950s, salmon from rivers in the US and Canada, as well as from Europe, were discovered to gather in the sea around Greenland and the Faroe Islands. A commercial fishing industry was established, taking salmon using drift nets. After an initial series of record annual catches, the numbers crashed; between 1979 and 1990, catches fell from four million to 700,000.[20]
Overfishing at sea is generally considered the primary negative factor, though marine exploitation rates estimated for various Newfoundland stocks for the period 1984–1991 averaged 45% on small (<63 cm) salmon and 74.2% on large salmon (>63 cm); closure of the Newfoundland commercial salmon fishery beginning in 1992 has not resulted in general increases in salmon populations through the present.[10]
Beginning around 1990, the rates of Atlantic salmon mortality at sea more than doubled. In the western Atlantic, fewer than 100,000 of the important multiple sea-winter salmon were returning. Rivers of the coast of Maine, plus southern New Brunswick and much of mainland Nova Scotia saw runs drop precipitously, and even disappear. In the mid-1990s, the Atlantic Salmon Federation in cooperation with partners developed sonic tracking technology, and by 2008, the salmon had been tracked from rivers such as the Restigouche and the Miramichi as far along their migration routes as the Strait of Belle Isle, between Labrador and Newfoundland, and halfway to feeding grounds off Greenland. The problems at sea remain, leading to a concerted international effort, called SALSEA, to find out more about the mortality at sea. It is organized by the North Atlantic Salmon Conservation Organization.[citation needed]
Possibly because of improvements in ocean feeding grounds, returns in 2008 were very positive. On the Penobscot River in Maine, returns were about 940 in 2007, and by mid-July 2008, the return was 1,938. Similar stories were reported in rivers from Newfoundland to Quebec. In 2011, more than 3,100 salmon returned to the Penobscot, the most since 1986, and nearly 200 ascended the Narraguagus River, up from the low two digits just a decade before.[21]
Recovery[edit]
Around the North Atlantic, efforts to restore salmon to their native habitats are underway, with slow progress. Habitat restoration and protection are key to this process, but issues of excessive harvest and competition with farmed and escaped salmon are also primary considerations. In the Great Lakes, Atlantic salmon have been introduced successfully, but the percentage of salmon reproducing naturally is very low. Most are stocked annually. Atlantic salmon were native to Lake Ontario, but were extirpated by habitat loss and overfishing in the late 19th century. The state of New York has since stocked its adjoining rivers and tributaries, and in many cases does not allow active fishing.[3][22] Wild salmon on entering rivers as adults have characteristically pointed fins which help scientists distinguish them from farmed or escaped salmon.
In New England, many efforts are underway to restore salmon to the region by knocking down obsolete dams and updating others with fish ladders and other techniques that have proven effective in the West with Pacific salmon. There is some success thus far, with populations growing in the Penobscot and Connecticut Rivers. In Ontario, the Atlantic Salmon Restoration Program[23] was started in 2006, and is one of the largest freshwater conservation programs in North America. It has stocked Lake Ontario with over 700,000 young Atlantic salmon. In October 2007, salmon were video-recorded running in Toronto's Humber River by the Old Mill. In November 2007, a migrating salmon was observed in the Credit River.[19] There has also been some success in establishing Atlantic salmon in Fish Creek, a tributary of Oneida Lake in central New York.
Atlantic salmon, though, remains a popular fish for human consumption.[3] It is commonly sold fresh, canned, or frozen.
Beaver impact[edit]
The decline in anadromous salmonid species over the last two to three centuries is correlated with the decline in the North American beaver and European beaver, although some fish and game departments continue to advocate removal of beaver dams as potential barriers to spawning runs. Migration of adult Atlantic salmon may be limited by beaver dams during periods of low stream flows, but the presence of juvenile Salmo salar upstream from the dams suggests the dams are penetrated by parr.[24] Downstream migration of Atlantic salmon smolts was similarly unaffected by beaver dams, even in periods of low flows.[24] A 2003 study of Atlantic salmon and sea-run brown trout/sea trout (Salmo trutta morpha trutta) spawning in the Numedalslågen River and 51 of its tributaries in southeastern Norway were unhindered by beaver.[25] In a restored, third-order stream in northern Nova Scotia, beaver dams generally posed no barrier to Atlantic salmon migration except in the smallest upstream reaches in years of low flow where pools were not deep enough to enable the fish to leap the dam or without a column of water over-topping the dam for the fish to swim up.[26] The importance of winter habitat to salmonids afforded by beaver ponds may be especially important (and underappreciated) in streams of northerly latitudes without deep pools where ice cover makes contact with the bottom of shallow streams.[24] In addition, the up to eight-year-long residence time of juveniles in fresh water may make beaver-created permanent summer pools a crucial success factor for Atlantic salmon populations. In fact, two-year-old Atlantic salmon parr in beaver ponds in eastern Canada showed faster summer growth in length and mass and were in better condition than parr upstream or downstream from the pond.[27]
Legislation[edit]
The first laws regarding the Atlantic salmon were started nearly 800 years ago.[citation needed]
England[edit]
Edward I instituted a penalty for collecting salmon during certain times of the year. His son Edward II continued, regulating the construction of weirs. Enforcement was overseen by those appointed by the justices of the peace. Because of confusing laws and the appointed conservators having little power, most laws were barely enforced.
Based on this, a royal commission was appointed in 1860 to thoroughly investigate the Atlantic salmon and the laws governing the species, resulting in the 1861 Salmon Fisheries Act. The act placed enforcement of the laws under the Home Office's control, but it was later transferred to the Board of Trade, and then later to the Board of Agriculture and Fisheries.
Another act passed in 1865 imposed charges to fish and catch limits. It also caused the formation of local boards having jurisdiction over a certain river. The next significant act, passed in 1907, allowed the board to charge 'duties' to catch other freshwater fish, including trout.
Despite legislation, board effects decreased until, in 1948, the River Boards Act gave authority of all freshwater fish and the prevention of pollution to one board per river. In total, it created 32 boards.
In 1974, the 32 boards were reduced to 10 regional water authorities (RWAs). Although only the Northumbrian, Welsh, northwest and southwest RWA's had considerable salmon populations, all ten also cared for trout and freshwater eels.
The Salmon and Freshwater Fisheries Act was passed in 1975. Among other things, it regulated fishing licences, seasons, and size limits, and banned obstructing the salmon's migratory paths.[2]
Scotland[edit]
Legislation in Scotland to help Atlantic salmon began in 1318 by Alexander II. It prohibited certain types of traps in rivers.
During the 15th century, many laws were passed; many regulated fishing times, and worked to ensure smolts could safely pass downstream. James III even closed a meal mill because of its history of killing fish attracted to the wheel. Because the fish were held in such high regard, poachers were severely punished.
More recent legislation has established commissioners who manage districts. Furthermore, the Salmon and Freshwater Fisheries Act in 1951 required the Secretary of State be given data about the catches of salmon and trout to help establish catch limits.[2][16]
United States[edit]
Several populations of Atlantic salmon are in serious decline, and are listed as endangered under the Endangered Species Act (ESA). Currently, runs of 11 rivers in Maine are on the list – Kennebec, Androscoggin, Penobscot, Sheepscot, Ducktrap, Cove Brook, Pleasant, Narraguagus, Machias, East Machias and Dennys. The Penobscot is the "anchor river" for Atlantic salmon populations in the US. Returns in 2008 have been around 2,000, more than double the 2007 return of 940.
Section 9 of the ESA makes it illegal to take an endangered species of fish or wildlife. The definition of "take" is to "harass, harm, pursue, hunt, shoot, wound, kill, trap, capture, or collect, or to attempt to engage in any such conduct".[28]
Canada[edit]
The federal government has prime responsibility for protecting the Atlantic salmon, but over the last generation, effort has continued to shift management as much as possible to provincial authorities through memoranda of understanding, for example. A new Atlantic salmon policy is in the works, and in the past three years,[when?] the government has attempted to pass a new version of the century-old Fisheries Act through Parliament.
Federal legislation regarding at-risk populations is weak.[citation needed] Inner Bay of Fundy Atlantic salmon runs were declared endangered in 2000. As of 2008, no recovery plan is in place.
It takes constant pressure from nongovernmental organizations, such as the Atlantic Salmon Federation, for improvements in management, and for initiatives to be considered. For example, the technology for mitigation of acid rain-affected rivers used in Norway is needed in 54 Nova Scotia rivers. Yet, an initiative of the ASF and the Nova Scotia Salmon Association raised the funds to get a project in place, in West River-Sheet Harbour.
In Quebec, the daily catch limit for Atlantic salmon is one fish over 63 cm (25 in), two fish under 63 cm or one fish over and one under 63 cm, provided the smaller fish was the first one caught (a provision designed to prevent an angler from continuing to fish if a large fish is already in possession). The annual catch limit is seven Atlantic salmon of any size.
NASCO[edit]
The North Atlantic Salmon Conservation Organization is an international council made up of Canada, the European Union, Iceland, Norway, the Russian Federation, and the United States, with its headquarters in Edinburgh.[29] It was established in 1983 to help protect Atlantic salmon stocks, through the cooperation between nations. They work to restore habitat and promote conservation of the salmon.
Sustainable consumption[edit]
In 2010, Greenpeace International has added the Atlantic salmon to its seafood red list. "The Greenpeace International seafood red list is a list of fish that are commonly sold in supermarkets around the world, and which have a very high risk of being sourced from unsustainable fisheries".[30]
See also[edit]
- AquAdvantage salmon, a genetically modified Atlantic salmon
- Atlantic Salmon Federation (ASF)
Notes[edit]
- ^ World Conservation Monitoring Centre (1996). "Salmo salar". IUCN Red List of Threatened Species. Version 2.3. International Union for Conservation of Nature. Retrieved 7 March 2011.
- ^ a b c d e f g h i Shearer, W. (1992). The Atlantic Salmon. Halstead Press.
- ^ a b c d e f The Audubon Society Field Guide to North American Fishes, Whales & Dolphins. Chanticleer Press. 1983. p. 395.
- ^ Atlantic salmon. Seafood Portal.
- ^ a b c Klemetsen A, Amundsen P-A, Dempson JB, Jonsson B, Jonsson N, O’Connell MF, Mortensen E (2003). "Atlantic salmon Salmo salar L., brown trout Salmo trutta L. and Arctic charr Salvelinus alpinus (L.): a review of aspects of their life histories". Ecology of Freshwater Fish. doi:10.1034/j.1600-0633.2003.00010.x.
- ^ Barton, M.: "Biology of Fishes.", pages 198–202 Thompson Brooks/Cole 2007
- ^ [1]
- ^ Burnie D and Wilson DE (Eds.), Animal: The Definitive Visual Guide to the World's Wildlife. DK Adult (2005), ISBN 0789477645
- ^ Atlantic Salmon Life Cycle Connecticut River Coordinator's Office, U.S. Fish and Wildlife Service. Updated: 13 September 2010.
- ^ a b . B. Dempson, C. J. Schwarz, D. G. Reddin, M. F. O’Connell, C. C. Mullins, and C. E. Bourgeois (2001). "Estimation of marine exploitation rates on Atlantic salmon (Salmo salar L.) stocks in Newfoundland, Canada". ICES Journal of Marine Science: 331–341. Retrieved 7 May 2011.
- ^ a b c d Heen, K. (1993). Salmon Aquaculture. Halstead Press.
- ^ Youngson, A. F., Webb, J. H., Thompson, C. E., and Knox, D. 1993. Spawning of escaped farmed Atlantic salmon (Salmo salar): hybridization of females with brown trout (Salmo trutta). Canadian Journal of Fisheries and Aquatic Sciences, 50:1986-1990.
- ^ Matthews, M. A., Poole, W. R., Thompson, C. E., McKillen, J., Ferguson, A., Hindar, K., and Wheelan, K. F. 2000. Incidence of hybridization between Atlantic salmon, Salmo salar L., and brown trout, Salmo trutta L., in Ireland. Fisheries Management and Ecology, 7:337-347.
- ^ Seawater tolerance in Atlantic salmon, Salmo salar L., brown trout, Salmo trutta L., and S. salar × S. trutta hybrids smolt. Urke HA, Koksvik J, Arnekleiv JV, Hindar K, Kroglund F, Kristensen T. Source Norwegian Institute of Water Research, 7462, Trondheim, Norway. henning.urke(@)niva.no
- ^ Natural hybridization between Atlantic salmon (Salmo salar) and brown trout (Salmo trutta) in northern Spain by Carlos Garcia de Leaniz
- ^ a b c Sedgwick, S. (1988). Salmon Farming Handbook. Fishing News Books LTD.
- ^ N. Bromage (1995). Broodstock Management and Egg and Larval Quality. Blackwell Science.
- ^ R. M. J. Ginetz (May, 2002). "On the Risk of Colonization by Atlantic Salmon in BC waters" (PDF). B.C. Salmon Farmers Association.
- ^ a b Harb, M. "Upstream Battle", Canadian Geographic Magazine, June 2008, p. 24
- ^ "Salmon campaigner lands top award". BBC News. 22 April 2007.
- ^ Carpenter, Murray (26 December 2011). "Shiny Patches in Maine’s Streambeds Are Bright Sign for Salmon". Retrieved February 2012.
- ^ Mills, D. (1989). Ecology and Management of Atlantic Salmon. Springer-Verlag.
- ^ Atlantic Salmon Restoration Program
- ^ a b c P. Collen & R. J. Gibson (2001). "The general ecology of beavers (Castor spp.), as related to their influence on stream ecosystems and riparian habitats, and the subsequent effects on fish – a review" (PDF). Reviews in Fish Biology and Fisheries 10 (4): 439–461. doi:10.1023/A:1012262217012.
- ^ Howard Park & Øystein Cock Rønning (2007). "Low potential for restraint of anadramous salmonid reproduction by beaver Castor fiber in the Numedalslågen river catchment, Norway". River Research and Applications 23 (7): 752–762. doi:10.1002/rra.1008.
- ^ Barry A. Taylor, Charles MacInnis, Trevor A. Floyd (2010). "Influence of Rainfall and Beaver Dams on Upstream Movement of Spawning Atlantic Salmon in a Restored Brook in Nova Scotia, Canada". River Research and Applications: 183–193. doi:10.1002/rra.1252.
- ^ Douglas B. Sigourney, Benjamin H. Letcher & Richard A. Cunjak (2006). "Influence of beaver activity on summer growth and condition of age-2 Atlantic salmon parr". Transactions of the American Fisheries Society 135 (4): 1068–1075. doi:10.1577/T05-159.1.
- ^ (16 U.S.C. 1532(19)) http://www.epa.gov/EPA-SPECIES/1998/May/Day-01/e11668.htm
- ^ "NASCO ~ The North Atlantic Salmon Conservation Organization". Nasco.int. Retrieved 11 February 2012.
- ^ Greenpeace International Seafood Red list
References[edit]
- Atlantic salmon NOAA FishWatch. Retrieved 4 November 2012.
Unreviewed
Names and Taxonomy
Taxonomy
Comments: Distinct regional stocks have been identified using morphometric and biochemical characters (Claytor and McCrimmon 1988).
See taxonomy comments for the Gulf of Maine population.
Trusted



