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Ecology and Vulnerability Atlantic Salmon
Ecology and Vulnerability
Atlantic Salmon
Background
Atlantic salmon are large silver fish with dark spots along the upper portion of their body. During spawning, they display colors of reddish-green to grayish-... Read More
Background
Atlantic salmon are large silver fish with dark spots along the upper portion of their body. During spawning, they display colors of reddish-green to grayish-brown. They are migratory anadromous fish, spending a large portion of their lives in saltwater but migrating to freshwater to spawn. In the northwest Atlantic Ocean, the historical range (prior to European settlement) of Atlantic salmon extended from southern Greenland to as far south as the Housatonic River in Connecticut 7. Atlantic salmon have a relatively complex life cycle where juveniles, also known as parr, typically spend their first 1 to 3 years in freshwater streams and lakes before migrating to marine habitats. The transition period from freshwater to marine habitats is known as “smoltification”. Adults spend 2 to 3 years in the ocean feeding primarily on fish and crustaceans before returning to natal streams to spawn 5,13. Atlantic salmon prefer to spawn in a gravel substrate with some degree of water circulation to keep eggs oxygenated. Eggs hatch in March and April, and parr feed on larval insects in habitats with vegetation and structural cover 5. The survival and growth of juveniles is dependent on predation, disease, competition, water temperature, and food supply 3,5. Atlantic salmon have the ability to spawn multiple times within their life cycle, unlike Pacific salmon, which spawn once and die.
Salmon and other anadromous fish are important sources of marine-derived nutrients; fish act as energy conduits to freshwater habitats as they migrate from the ocean, up river, and are distributed across the terrestrial landscape by predators such as raptors, bears and mink. These marine nutrients enhance the growth of plants, wildlife, and fish — including juvenile salmon — that occupy streams and the surrounding areas where salmon are found 2,14,15.
Prior to European settlement, nearly every major river north of the Hudson contained an abundance of Atlantic salmon 5. More recently, however, New England salmon populations have declined significantly as a result of overfishing, poor water quality, and dam construction 8,15,19. These factors drastically reduced Atlantic salmon populations as early as the 1800s. By the end of the 19th century, three of the five largest salmon populations in New England (Connecticut River, Merrimack River, and Androscoggin River) were eliminated 4. By the year 2000, the Gulf of Maine population was listed as endangered 13. State and federal agencies have invested in stocking programs, but overall these efforts have resulted in few returning adults 17. This is likely due to continued overfishing and the persistence of dams in New England waterways. Salmon aquaculture has recently increased to meet market demands; however, farmed salmon threatens wild salmon populations through disease and parasite outbreaks as wells as genetic, habitat, and food web impacts.
Climate Impacts
Climate change will likely impact Atlantic salmon in a number of ways. Salmon are a cold-water-adapted species, and their daily activities and survival are dependent on temperature. The maximum critical temperature for Atlantic salmon survival (20° C/68° F, depending on life stage) will likely be exceeded in many areas with climate change 18. Projected increases in temperature associated with climate change have been shown to alter the proportion of residents (those individuals that remain within the system year-round) and migrants (those that leave the system seasonally) in a similar species (masu salmon), which may impact Atlantic salmon distribution and population dynamics 20. Warming ocean temperatures have been associated with declines in Atlantic salmon survival 6,9. In addition, warming temperatures can disrupt food webs and alter species interactions through changes in predation and competition 1,12. Increasing sea surface temperatures have also been associated with declining body condition and fat content (or energy storage) in spawning adults 16. Thus, heat stress will likely impact growth, survival, and reproduction.
Atlantic salmon are also dependent on stable and reliable stream flow patterns. Changes in the timing, magnitude, and duration of stream and river flows from altered precipitation and temperature regimes are expected to further stress anadromous salmon populations by decreasing recruitment, survival, and productivity 10,21. The presence of dams and other man-made barriers can alter river and stream temperature and flow in addition to restricting migration and connectivity between salmon spawning, nursery, and ocean habitats 22.
The combination of climate change and existing stressors can have disproportionate effects on Atlantic salmon populations. Because Atlantic salmon populations have been driven down to such low numbers, their overall genetic diversity has declined, making them less able to adapt and less resilient to future shifts and stressors. Overall, Atlantic salmon have an increased vulnerability to climate change due to their complex life cycle, reproductive strategy, use of both marine and freshwater habitats, and stress due to other human activities 18.
1. Beaugrand, G., and P. Reid. 2003. Long-term changes in phytoplankton, zooplankton and salmon related to climate. Global change biology 9: 801–817.
2. Bilby, R.E., Fransen, B.R., Bisson, P.A. 1996. Incorporation of nitrogen and carbon from spawning adult coho salmon into the trophic system of small streams: evidence from stable isotopes. Canadian Journal of Fisheries Aquatic Science 53: 164-173.
3. Bley, P.W. 1987. Age, growth, and mortality of juvenile Atlantic salmon in streams: a review. Biological Report 87(4). U.S. Fish and Wildlife Service. Washington, D.C. 25 pp.
4. Colligan, M.A., Kocik, J.F., Kimball, D.C., Marancik, J, McKeon, JF, Nickerson, PR. 1999. Status Review for anadromous Atlantic Salmon in the United States. National Marine Fisheries Service/US Fish and Wildlife Service Joint Publication. Gloucester, Massachusetts
5. Fay, C., M. Bartron, S. Craig, A. Hecht, J. Pruden, R. Saunders, T. Sheehan, and J. Trial. 2006. Status Review for Anadromous Atlantic Salmon (Salmo salar) in the United States. Report to the National Marine Fisheries Service and U.S. Fish and Wildlife Service. 294 pages.
6. Friedland K.D., Shank B.V., Todd C.D., McGinnity, P., Nye J.A. 2013. Differential response of continental stock complexes of Atlantic salmon (Salmo salar) to the Atlantic Multidecadal Oscillation. J Mar Syst. 2014; 133: 77-87. doi: 10.1016/j.jmarsys.03.003
7. Fuller, P., M. Neilson, K. Dettloff, A. Fusaro, and R. Sturtevant. 2016. Atlantic Salmon Fact Sheet. United States Geological Survey (USGS).
8. Hall C.J., Jordaan A., Frisk M.G. 2011. The historic influence of dams on diadromous fish habitat with a focus on river herring and hydrologic longitudinal connectivity. Landscape Ecology 26: 95-107.
9. Hare J.A., W.E. Morrison, M.W. Nelson, N.M. Stachura, E.J. Teeters, R.B Griffis, et al. 2016. A Vulnerability Assessment of Fish and Invertebrates to Climate Change on the Northeast U.S. Continental Shelf. PLoS ONE 11: e0146756. doi:10.1371/ journal.pone.0146756
10. Jonsson, B., Jonsson, N. 2009. A review of the likely effects of climate change on anadromous Atlantic salmon Salmo salar and brown trout Salmo trutta, with particular reference to water temperature and flow. Journal of Fish Biology 75:2381-2447.
11. Judd, Sylvester. 1905. The History of Hadley: Including the Early History of Hatfield, South Hadley, Amherst, and Granby, Massachusetts. H. R. Huntting Company, p. 307.
12. Mills K.E., Pershing A.J., Sheehan T.F., Mountain D. 2013. Climate and ecosystem linkages explain widespread declines in North American Atlantic salmon populations. Global Change Biology 19:3046-3061. doi: 10.1111/gcb.12298
13. National Oceanic and Atmospheric Administration (NOAA). 2016. Species: Atlantic Salmon (Salmo salar).
14. Reimchen, T.E., Mathewson, D., Hocking, M.D., Morgan, J. 2002. Isotopic Evidence for Enrichment of Salmon-Derived Nutrients in Vegetation, Soil, and Insects in Riparian Zones in Coastal British Columbia. American Fisheries Society Symposium XX:00-000.
15. Saunders, R., Hachey, M.A., Fay, and C.W. 2006. Maine’s diadromous fish community: past, present, and implications for Atlantic salmon recovery. Fisheries 31:537–547.
16. Todd, C.D., Hughes, S.L., Marshall, C.T., Macleans, J.C., Lonerhan, M.E., Biuw, E.M. 2008. Detrimental effects of recent ocean surface warming on growth condition of Atlantic salmon. Global Change Biology. 14:958-970.
17. United States Atlantic Salmon Assessment Committee (USASAC). 2000. Annual Report of the U.S. Atlantic Assessment Committee. Report No. 12-1999 Activities. Glouster, MA.
18. Whitman, A., A. Cutko, P. De Maynadier, S. Walker, B. Vickery, S. Stockwell, and R. Houston. 2013. Climate change and biodiversity in Maine: vulnerability of habitats and priority species. Report SEI-2013-03. Manomet Center for Conservation Sciences (in collaboration with Maine Beginning with Habitat Climate Change Working Group). Brunswick, ME.
19. Brown, J.J., Limburg, K.E., Waldman, J.R., Stephenson, K., Glenn, E., Juanes, F., Jordaan, A. 2013. Fish and hydropower on the U.S. Atlantic coast: failed fisheries policies from half-way technologies. Conservation letters 6:4 280-286.
20. Morita, K., Tamate, T., Kuroki, M., Nagasawa, T. 2014. Temperature-dependent variation in alternative migratory tactics and its implications for fitness and population dynamics in a salmonid fish. Journal of Animal Ecology. 83: 1268-1278.
21. Ward, E.J., Anderson, J.H., Beechie, T.J., Pess, G.R., Ford, M.J. 2015. Increased hydrologic variability threatens depleted anadromous fish populations. Global Change Biology. 21: 2500-2509.
22. Daufresne, M., Boët, P. 2009. Climate change impacts on structure and diversity of fish communities in rivers. Global Change Biology 13: 2467-2478.
23. DFO. 2012. Temperature threshold to define management strategies for Atlantic salmon (Salmo salar) fisheries under environmentally stressful conditions. DFO Can. Sci. Advis. Sec. Sci. Advis. Rep. 2012/019.
This species was identified as moderately vulnerable to climate change because of the following factors:
- Natural barriers
- Anthropogenic barriers such as dams ... Read More
This species was identified as moderately vulnerable to climate change because of the following factors:
- Natural barriers
- Anthropogenic barriers such as dams
- Climate change mitigation efforts
- Specific physiological thermal thresholds
- Specific hydrological thresholds
Factors that decrease vulnerability include:
- Ability to disperse
Sneddon, L. A., and G. Hammerson. 2014. Climate Change Vulnerability Assessments of Selected Species in the North Atlantic LCC Region. NatureServe, Arlington, VA.
This species was identified as highly vulnerable to climate change because of the following factors:
- Highly specialized habitat
- A critical part of its life cycle is... Read More
This species was identified as highly vulnerable to climate change because of the following factors:
- Highly specialized habitat
- A critical part of its life cycle is associated with a microhabitat with distinct microclimates
- Southern range includes less than half of northern Maine
- Likely to experience significant declines in habitat
- Highly fragmented habitat
- Maximum critical temperature for survival will likely be exceeded
- Growth and reproduction likely to be impacted by stress heat
- Survival is dependent on stable hydrological patterns
- Dispersal is limited by natural and anthropogenic barriers
- Likely low genetic diversity
- Likely disruption of environmental cues
- Likely disruption of specialized relationships with host or prey species
- Dependent on or susceptible to interspecific interactions
- Likely increase in existing or novel pathogens
- Habitat degradation by invasive species?
- Herbivory by non-native pests
- Herbicide and pesticide use
Whitman, A., A. Cutko, P. De Maynadier, S. Walker, B. Vickery, S. Stockwell, and R. Houston. 2013. Climate change and biodiversity in Maine: vulnerability of habitats and priority species. Report SEI-2013-03. Manomet Center for Conservation Sciences (in collaboration with Maine Beginning with Habitat Climate Change Working Group), Brunswick, ME.
This species was identified as highly vulnerable to climate change because of the following factors:
- Increasing ocean surface temperature
- Ocean acidification ... Read More
This species was identified as highly vulnerable to climate change because of the following factors:
- Increasing ocean surface temperature
- Ocean acidification
- Increasing air temperature
- Currently depleted
- Dispersal and early life history requirements
- Complex spawning cycle
- Complexity in reproduction
Hare J.A., W.E. Morrison, M.W. Nelson, N.M. Stachura, E.J. Teeters, R.B Griffis, et al. 2016. A Vulnerability Assessment of Fish and Invertebrates to Climate Change on the Northeast U.S. Continental Shelf. PLoS ONE 11: e0146756. doi:10.1371/ journal.pone.0146756
This species was identified as moderately vulnerable to climate change because of the following factors:
- Natural barriers
- Anthropogenic barriers such as dams ... Read More
This species was identified as moderately vulnerable to climate change because of the following factors:
- Natural barriers
- Anthropogenic barriers such as dams
- Climate change mitigation efforts
- Specific physiological thermal thresholds
Factors that decrease vulnerability include:
- Ability to disperse
Sneddon, L. A., and G. Hammerson. 2014. Climate Change Vulnerability Assessments of Selected Species in the North Atlantic LCC Region. NatureServe, Arlington, VA.
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