Temporal range: Late Miocene - Recent
|Sockeye salmon, Oncorhynchus nerka
Female (above) and male in mating season
Note male with hooked jaws
Oncorhynchus is a genus of fish in the family Salmonidae; it contains the Pacific salmons and Pacific trouts. The name of the genus is derived from the Greek onkos ("hook") and rynchos ("nose"), in reference to the hooked jaws of males in the mating season (the "kype").
Salmon and trout with ranges generally in waters draining to the Pacific Ocean are members of the genus. Their range extends from Beringia southwards, roughly to Japan in the west and Mexico to the east. In North America, some subspecies of O. clarki are native in the Rocky Mountains and Great Basin, while others are native to the Rio Grande and western tributaries of the Mississippi River Basin which drain to the Gulf of Mexico, rather than to the Pacific. Several species of Oncorhynchus have been introduced into non-native waters around the globe establishing self-sustaining wild populations.
The six Pacific salmons of Oncorhynchus are anadromous (migratory) and semelparous (die after spawning). Anadromous forms of Oncorhynchus mykiss known as steelhead are iteroparus. The Coastal cutthroat trout form of Oncorhynchus clarki is considered semi-anadromous as it spends short periods of time in marine environments.
Several late Miocene [about 7 million years ago (Mya)] trout-like fossils in Idaho, in the Clarkia Lake beds, appear to be of Oncorhynchus.1 The presence of these species so far inland established Oncorhynchus was not only present in the Pacific drainages before the beginning of the Pliocene (5–6 Mya), but also that rainbow and cutthroat trout, and Pacific salmon lineages had diverged before the beginning of the Pliocene. Consequently, the split between Oncorhynchus and Salmo (Atlantic salmon) must have occurred well before the Pliocene. Suggested dates ions have gone back as far as the early Miocene (about 20 Mya).23 One fossil species assigned to this genus, O. rastrosus, the sabertooth salmon (synonym Smilodonichthys), is a 9-foot (2.7 m)-long species known from Late Miocene to Pleistocene fossil.4
Speciation among Oncorhynchus has been examined for decades, and a family "tree" is not yet completely developed for the Pacific salmonids. Mitochondrial DNA (mtDNA) research has been completed on a variety of Pacific trout and salmonid species, but the results do not necessarily agree with fossil research, or molecular research. Chum, pink and sockeye salmon lineages are generally agreed to have diverged in the sequence after other species.2 Montgomery (2000) discusses the pattern of the fossil record as compared to tectonic shifts in the plates of the Pacific Northwest of America. The (potential) divergence in Onchorhyncus lineages appear to follow the uprising of the Pacific Rim. The climatic and habitat changes that would follow such a geologic event are discussed, in the context of potential stressors leading to adaptation and speciation.3
One interesting case involving speciation with salmon is that of the kokanee (landlocked) sockeye. Kokanee sockeye evolve differently from anadromous sockeye—they reach the level of "biological species". Biological species—as opposed to morphological species—are defined by the capacity to maintain themselves in sympatry as independent genetic entities. This definition can be vexing because it apparently applies only to sympatry, and this limitation makes the definition difficult to apply. Examples in Washington, Canada, and elsewhere have two populations living in the same lake, but spawning in different substrates at different times, and eat different food sources.5 There is no pressure to compete or interbreed (two responses when resources are short). These types of kokanee salmon show the principal attributes of a biological species: they are reproductively isolated and show strong resources partitioning.
Declines in the abundance of wild salmon due to overfishing placed greater pressure on hatcheries to increase production and restore the wild salmon stock to supply fisheries.67 The problem is that hatcheries can never truly replicate the environment of wild salmon, an issue which often results in physiological and behavioral differences between wild salmon and those reared in hatcheries. These differences are often the product of genetic changes associated with inbreeding, artificial selection, and natural selection as well as different environmental pressures acting on hatchery fish than wild populations.8 Due to the size selective nature of fishing favoring larger fish, a reduction in average size of the adult salmon has been observed over time. The smaller salmon make a greater proportion of the remaining individuals continuing the population, and problems arise when these hatchery-reared fish are introduced into the wild populations. Unlike wild salmon, larger salmon are selected for in hatcheries and are typically much larger than wild salmon.9 The result is that hatchery-produced salmon tend to out-compete wild salmon for space, food, and other resources. Some salmon species in hatcheries exhibit predatory behavior toward wild salmon because they grow to be much larger. Regardless of whether predation is observed, natural social interactions are disturbed by the release of large numbers of hatchery-reared salmon where wild populations are low because salmon in hatcheries naturally have a higher propensity towards aggressive behavior.10 Overall, natural salmon populations are put at risk when hatchery-reared salmon populations are introduced due to competition for resources, predation by larger individuals, and negative social interactions that upset the natural order observed in wild salmon populations. As a result, wild salmon populations are steadily dropping as the pressure to continue breeding salmon in hatcheries increases. Conservation efforts that work to place limitations on hatcheries to increase the wild salmon populations are hindered by financial pressures because hatcheries effectively support many states economically by accounting for over 70% of the salmon harvested for recreational and commercial purposes.11
Pacific salmon are harvested throughout the world as a source of food in countries ranging from the United States to South Korea.12 Over the past century, pacific salmon have been extensively fished through both recreational fishing and commercial fishing. In fact, since the 1970s there has been a nearly threefold increase in catch of pacific salmon.9 As this catch has increased, a selection of reduced body size has been observed. In Japanese Chum Salmon, for example, between 1970 and 1988 there has been a continuous decrease in body weight averaging between 11 and 32 percent.13 In part, this decline in body weight has been related to the size selective effect of fishing gear used in the harvesting of salmon populations.6 Salmon of larger body weight are more apt to be caught during fishing efforts, causing lower body weight to be a beneficial character trait for survival. Thus, pacific salmon have become continuously smaller in body size. However, studies have also shown that for pacific salmon a larger mean size at the time of reproduction increases the survival of offspring.14 The life history of salmon favors delayed reproduction because fecundity increased with body size.12 Consequently, the smaller body size of salmon results in a negative impact on population growth by decreasing the survivability of progeny, and thus decreasing the growth rate of populations. This reduction of productivity in pacific salmon is, in part, seeded in the overfishing and has causes a reduction in population sizes throughout pacific salmon species.
There has been evidence that the sockeye salmon are affected by thermal conditions and their responses to temperature are relatively strong and tend to vary from region to region. Canada has also used the Species at Risk Act to recognize the importance of biological diversity when it come to the conservation of the salmon population.15 This means that multiple species of salmon would be looked at when it comes to conservation as well as multiple areas that each species live in. COSEWIC, a Canadian organization for the conservation of species, has named the Interior Fraser River Coho, the Cultus Lake Sockeye, and the Sakinaw Lake Sockeye to all be endangered. In British Columbia sockeye salmon in four different watersheds were certified by the Marine Stewardship Council or MSC as sustainable fisheries in July 2010 and the certification is good for a period of five years.16 In 2011 MSC also certified the Pink Salmon Fishery and as of 2012 The Chum Salmon Fisheries started their review under the MSC to become certified as a sustainable fishery.17
The US government has been working developing a nation wide policy for the salmon populations.The Pacific Salmon Stronghold Conservation Act was re-submitted to congress and if passed will create geographic strongholds for salmon populations.18 Other policies include the Wild Salmon Policy which was enacted in 2005 and its number one focus is the conservation of salmon off of the coasts. Even localized policies have begun, with one in Oregon which focuses on the southernmost watershed and was approved January 2013.19 In the Alaskan efforts, there is evidence of eight known regional groups of survival. It is also seen that the emigration of smolts (young salmon) from freshwater to other areas such as marine areas have shown significant consequences on the survival of different salmon groups. The Alaska Department of Fish and Game first received MSC, Marine Stewardship Council, Certification in sustainable seafood back in 2000.17 Each certification is good for a period of five years, with yearly check ups to ensure that the fishery remains sustainable. It was renewed again in 2007, but in 2012 The ADFG left the program. The Annette Island Reserve salmon fishery is under the control of the Metlakatla Indian community and as such was not included in the previous assessments of the Alaskan fisheries. It received it’s sustainability certification in June 2011.17 The Wild Salmon Center is a non profit organization that works on promoting conservation efforts for the Salmon worldwide and in the United States has secured some of its nine protected locations equaling 8 million acres for protected watershed areas for the west coast salmon.18 Other efforts of the Wild Salmon Center include combating illegal fishing, maintaining sustainable fisheries, and creating local watersheds as new habitats.20
Poaching is a threat to Oncorhynchus salmon populations in Russia. It is estimated that illegal catching if salmon is 1.5 times more than the reported catch. The Wild Salmon Center is working with Russian authorities to try and help improve traceability systems so that markets and distinguish between legal sustainable salmon and the illegal salmon.21 The Wild Salmon Center has secured some of its protected locations for the salmon populations. In efforts with the WWF, the Wild Salmon Center was also able to have a sockeye salmon fishery certified as completely sustainable in 2012.22 The Iturup Island Pink and Chum Salmon Fishery was first certified in 2009 and was the first Russian salmon fishery to receive certification in sustainability by MSC.17 Other fisheries that were certified by MSC include the Northeast Sakhalin Island Pink Salmon, certified in June 2012, and the Ozernaya River Sockeye Salmon, certified in September 2012. The Aniva Bay Pink Salmon and the Sakhalin Island Pink salmon are both under review by the MSC.17
Some of the species in this genus are highly variable and a plethora of now-obsolete taxa have been described. The following list follows the most recent treatment in Fishbase. Currently, 15 species in this genus are recognized:23
- Oncorhynchus apache (R. R. Miller, 1972) (Apache trout, Arizona trout)
- Oncorhynchus chrysogaster (Needham & Gard, 1964) (Mexican golden trout)
- Oncorhynchus clarkii (J. Richardson, 1836) (cutthroat trout)
- Oncorhynchus gilae (R. R. Miller, 1950) (Gila trout)
- Oncorhynchus gorbuscha (Walbaum, 1792) (pink salmon, humpback salmon)
- Oncorhynchus iwame Seiro Kimura & M. Nakamura, 1961 (Iwame trout, markless trout)
- Oncorhynchus kawamurae D. S. Jordan & E. A. McGregor, 1925 (kunimasu, black kokanee)
- Oncorhynchus keta (Walbaum, 1792) (chum salmon, dog salmon, keta salmon, silverbrite salmon)
- Oncorhynchus kisutch (Walbaum, 1792) (coho salmon, silver salmon, silvers)
- Oncorhynchus masou (Brevoort, 1856) (seema, masu salmon, cherry salmon, Japanese salmon)
- Oncorhynchus mykiss (Walbaum, 1792) (rainbow trout, steelhead, ocean trout, redband trout)
- Oncorhynchus nerka (Walbaum, 1792) (sockeye salmon, red salmon, blueback salmon, kokanee)
- Oncorhynchus rhodurus D. S. Jordan & E. A. McGregor, 1925 (Biwa trout)
- Oncorhynchus tshawytscha (Walbaum, 1792) (Chinook salmon, blackmouth, black salmon, chub salmon, Columbia River salmon, hookbill salmon, king salmon, Quinnat salmon, spring salmon, Tyee salmon, winter salmon)
In addition to the above, the following subspecies have been named:
- Oncorhynchus clarkii
- Oncorhynchus clarkii clarkii (J. Richardson, 1836) Coastal cutthroat trout
- Oncorhynchus clarkii bouvieri – Yellowstone cutthroat trout
- Oncorhynchus clarkii lewisi – Westslope cutthroat trout
- Oncorhynchus clarkii pleuriticus (Cope, 1872) (Colorado River cutthroat trout)
- Oncorhynchus clarkii alvordensis – Alvord cutthroat trout (extinct)
- Oncorhynchus clarkii behnkei – Snake River fine-spotted cutthroat trout
- Oncorhynchus clarkii clarkii f. crescentii – Lake Crescent cutthroat trout, Crescenti trout (sometimes O. c. crescentii)
- Oncorhynchus clarkii henshawi – Lahontan cutthroat trout
- Oncorhynchus clarkii macdonaldi – yellowfin cutthroat trout (extinct)
- Oncorhynchus clarkii seleniris – Paiute cutthroat trout
- Oncorhynchus clarkii stomias – greenback cutthroat trout
- Oncorhynchus clarkii utah – Bonneville cutthroat trout
- Oncorhynchus clarkii virginalis – Rio Grande cutthroat trout
- Oncorhynchus masou
- Oncorhynchus mykiss
- Smiley, Charles J. "Late Cenozoic History of the Pacific Northwest". Association for the Advancement of Science: Pacific Division. Retrieved 2006-08-08.dead link
- McPhail, J.D.; Strouder, D.J. (1997). "Pacific Salmon and Their Ecosystems: Status and Future Options". The Origin and Speciation of Oncorhynchus. New York, New York: Chapman & Hall.
- Montgomery, David R. (2000). "Coevolution of the Pacific Salmon and Pacific Rim Topography". Department of Geological Sciences, University of Washington. Retrieved 2011-07-11.
- Sepkoski (2002)
- "Kokanee Heritage Project".
- Ricker, W. E. 1981. Changes in the average size and average age of Pacific salmon. Canadian Journal of fisheries and Aquatic Sciences, 38: 16361656.
- Ricker, W. E. 1995. Trends in the average size of Pacific salmon in Canadian catches. In Climate change and northern fish populations, pp. 563-602. Ed. by R. J. Beamish. Canadian Special Publication of Fisheries and Aquatic Sciences 121.Rand, P.S. 2011. Oncorhynchus nerka. In: IUCN 2012. IUCN Red List of Threatened Species. Version 2012.
- Rand, P.S. 2011. Oncorhynchus nerka. In: IUCN 2012. IUCN Red List of Threatened Species. Version 2012.
- Beamish, R.J.1997. "ICES Journal of Marine Science." Hatchery and Wild Production of Pacific Salmon in Relation to Large-scale, Natural Shifts in the Productivity of the Marine Environment. N.p., n.d.
- "Risks to Wild Populations from Hatchery Fish - Salmon Hatchery Q & As." Northwest Fisheries Science Center. N.p., n.d. Web.
- "Salmon Hatcheries Overview | Washington Department of Fish & Wildlife." Washington Department of Fish & Wildlife. N.p., n.d. Web.
- Groot, Cornelis, and Leo Margolis. (1991) Pacific salmon life histories. UBC press.
- IIshida, Y., Ito, S., Kaeriyama, M., McKinnell, M., and Nagasawa, K. 1993. Recent changes in age and size of chum salmon (Oncorhynchus keta) in the North Pacific Ocean and possible causes. Canadian Journal of Fisheries and Aquatic Sciences, 50: 290-295.
- Bigler, B. S., Welch, D. W., and Helle, J. H. 1996. A review of size trends among North Pacific salmon (Oncorhynchus spp.). Canadian Journal of Fisheries and Aquatic Sciences, 53: 455-465.
- Regan, Geoff. (2005) Canada’s Policy for Conservation of Wild Pacific Salmon. Fisheries and Oceans Canada.
- MSC Certification Requirements. Marine Stewardship Council. N.p., n.d. Web.
- Certification Status of Pacific Salmon Fisheries. State of the Salmon. N.p., n.d. Web.
- The Salmon Stronghold Initiative.. Wild Salmon Center. N.p., n.d. Web.
- Beyerlin et al. (2013) Conservation Plan for Fall Chinook Salmon in the Rogue Species Management Unit. Oregon Fish and Wildlife Commission.
- Initiatives. Wild Salmon Center. N.p., n.d. Web.
- Sustainable Fisheries. Wild Salmon Center. N.p., n.d. Web.
- Brandon, H. (2012) Conserving Kamchatka Salmon Through Marine Stewardship Council Certification. World Wildlife Fund.
- Froese, Rainer, and Daniel Pauly, eds. (2012). Species of Oncorhynchus in FishBase. February 2012 version.
- Behnke, Robert J. (2002): Trout and Salmon of North America. Free Press, 2002.
- Sepkoski, Jack (2002): Osteichthyes. In: A compendium of fossil marine animal genera. Bulletin of American Paleontology 364: 560. HTML fulltext
- Stearley, R.F. & Smoth, G.R. (1993): Phylogeny of the Pacific trout and salmon (Oncorhynchus) and the genera of family Salmonidae. Transactions of the American Fisheries Society 122(1): 1-33. DOI:10.1577/1548-8659(1993)122<0001:POTPTA>2.3.CO;2 HTML fulltext
- Stephenson, S.A. (2005) The distribution of Pacific salmon (Oncorhynchus spp.) in the Canadian western Arctic. http://www.dfo-mpo.gc.ca/Library/321160.pdf
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