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Sockeye Salmon Oncorhynchus nerka

The bright red bodies and green heads of the spawning sockeye make it a poster fish of salmon and river conservation. It prominence in the commercial fishery triggered decades of research so that today the sockeye is one of the most researched fish species on the planet. 

One of the most remarkable ecological stories to emerge in the past few decades is the vital role of salmon in north Pacific ecosystems. An excellent review of the story can be found in Thomas Quinn’s book, The behavior and ecology of Pacific Salmon and Trout (University of Washington Press, 2005). Years ago fisheries biologists in Alaska knew that the carcasses of sockeye salmon enriched otherwise nutrient-poor lakes where the young sockeye grew before leaving to sea. Experiments showed that artificial fertilization of lakes sometimes enhanced the growth of young sockeye. It appeared that the addition of nitrogen and phosphorous enhanced algal growth in lakes that became food of zooplankton eaten by young sockeye. The next breakthrough was the role of salmon carcasses in rivers and lakes. With the development of technology to measure isotopes, scientists were able to measure the relative contribution of marine and terrestrial sources of nitrogen and carbon in plants and animals along riverbanks. Kline et al (1990) showed that substantial amounts nitrogen and carbon in plants, insects and fishes was derived from marine sources. Biologists had long known that bears discard salmon carcasses along the edges of salmon spawning rivers but it was only recently that the significance of bears became clear. The size of bears and the number of cubs they raise is directly related to the amount of meat they consume (Hildebrand et al. 1999) and so large numbers of bears assemble along salmon spawning streams in autumn. They catch large numbers of large fish but eat mostly the brains and eggs and discard about 70% of the carcass. The remaining protein is left to rot in the forest where it eventually is taken up by the forest plants, insects, birds, mammals and fish (Bilby et al. 1996, Helfield 2001, Reimchen et al. 2003, Wilkinson et al 2005).

 

 

Distribution and Migration

Juvenile sockeye entering the ocean swim north along the coast of British Columbia and Alaska and then move offshore into the Gulf of Alaska where they spend the next two years. Sockeye gather in cold regions of the Gulf of Alaska where planktonic food is abundant. After two to three years, Canadian sockeye migrate toward the coast of British Columbia arriving between late June and August. Fraser River sockeye enter either Johnstone Strait or Juan de Fuca Strait and arrive at the mouth of the Fraser River in early July through to early September. Fish entering the Fraser River mouth arrive in early summer in time to reach the upper Fraser watershed. Late arriving sockeye linger for three to six weeks near the mouth of the Fraser River before entering the river to spawn in the mid Fraser watershed. The spawners migrating to the lower Fraser River tributaries takes only a few days compared to several weeks for fish returning to the upper Fraser River watershed. They arrive at spawning grounds in the lower Fraser River Valley in November. Department of Fisheries and Oceans estimated that 20-30% of the sockeye run escape the combined commercial and native fisheries.

 

Sockeye Spawning Behaviour

The typical life cycle of a Fraser River sockeye salmon is completed in four years. Adult sockeye return to river tributaries connected to lakes to spawn between late summer and autumn. Females dig nests or redds in the gravel bottom where they deposit fertilized eggs where they leave them to incubate for several months. Eggs hatch into young fish in the winter months to emerge in spring as fry. The fry move to a lake to feed and grow for a year before they migrate into the Fraser River.

The carcasses of the adults provide an important source of nutrients to otherwise nutrient poor lakes (Larkin and Slaney 1996). The decaying carcasses deposited into the lake are later recycled into their offspring through the lake plankton they eat. The loss of sockeye to lakes might deprive the ecosystem of an important source of nutrients. Larkin and Slaney (1996) estimated that nutrients increased in enhanced streams (i.e. streams with hatchery fish, sockeye lake fertilization, spawning channel creation, and other methods) but declined in unmodified streams. The combined historical effect of logging in spawning rivers and streams, overfishing of adult fish by commercial and recreational fishers, and reduced survival at sea during shifts in ocean productivity might spell long term trouble for many small streams that have become starved of nutrients when the salmon did not return (Larkin and Slaney 1996).   

 

References

 

Bilby, R.E., B.R. Fransen and P.A. Bisson. 1996. Incorporation of nitrogen and carbon from spawning coho salmon into the trophic

system of small streams: evidence from stable isotopes. Canadian Journal of Fisheries and Aquatic Sciences 53:164-173.

 

Bilby, R.E., B.R. Fransen, P.A. Bisson and J.K. Walter. 1998. Responses of juvenile coho salmon (Oncorhynchus kistusch) and

steelhead (Oncorhynchus mykiss) to the addition of salmon carcasses to two streams in southwestern Washington, U.S.A. Canadian

Journal of Fisheries and Aquatic Sciences 55:1901-1918.

 

Healey, M.C. 1991. The life history of chinook salmon. Pp 311-393 in: Pacific Salmon Life Histories. C. Groot and L. Margolis (eds).

University of British Columbia Press.

 

Helfield, JM,  2001. Interactions between salmon, bear, and riparian vegetation in Alaska. PhD thesis, U of Washington, Seattle. 

 

Hilderbrand, G.V., Schwartz, C.C., Robbins, C.T., Jacoby, M.E., Hanley, T.A., Arthur, M.S., and Servheen, C. 1999. The importance

of meat, particularly salmon, to body size, population productivity, and conservation of North American brown bears.

Canadian Journal of Zoology  77: 132–138.

 

Kline, TC et al. 1993. Recycling of elements transported upstream by runs of Pacific salmon: 1. Canadian Journal of Fisheries and

Aquatic Sciences 50-2350-2365.

 

Larkin, G.A., and P.A. Slaney. 1996. Trends in marine-derived nutrient sources to South Coastal British Columbia Streams: Impending

implications to Salmonid production. Province of British Columbia, Ministry of Environment, Lands and Parks, and Ministry of Forests.

Watershed Restoration Management Report No. 3:56p, Victoria.

 

Quinn, T.P. 2005. The behavior and ecology of Pacific salmon and trout. UBC Press, Vancouver.

Reimchen, T. 2003. Some ecological and evolutionary aspects of bear-salmon interactions in coastal British Columbia. Canadian Jounral of Zoology 78: 448-458.

 

Wilkinson, C.E., M.D. Hocking and T.E Reimchen. 2005. Uptake of salmon-derived nitrogen by mosses and liverworts in coastal British

Columbia. Oikos 108: 85-98.

 

 

 

 
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