Salish Sea Marine Survival Project

Salish Sea Marine Survival Project

The Salish Sea Marine Survival Project: Canadian Program Summaries summarizes findings from the Pacific Salmon Foundation’s five year study on salmon declines in the Strait of Georgia.

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45 NEXT STEPS 1. Estuaries are essential for salmon production. Work to continue estuary rehabilitation and protection in the Strait of Georgia is highly recommended. 2. Removal of marine debris from estuaries is required to allow for successful restoration. 3. Signage providing information about extent of local eelgrass and kelp habitats, as well as creation of eco-friendly mooring buoys, could reduce damage to these important habitats. 4. Studies are required to determine effective strategies to mitigate high levels of contaminants, including hydrogen sulfide, in estuarine sediments that would otherwise be suitable for eelgrass productivity. 5. An ongoing study evaluates the effects of temperature stress on kelp populations in the Salish Sea. There appear to be kelp populations that are adaptable to local temperature regimes: work is being carried out to assess thermal tolerance with the hope that warm water-adapted populations could be more effective for restoration activities, particularly under climate change. 6. Research is needed to find possible genetic strains of eelgrass resistant to wasting disease (Labyrinthula zosterae), a mold disease related to increased sea surface temperatures. 7. Research is needed to define areas of eelgrass and kelp on the entire coast of BC. A mapping of the extent of local kelp and eelgrass habitats, and protection of these habitats is highly recommended. Figure 4. Chinook smolts leave both the Green and Skagit Rivers early as small fry and later as larger parr. However, returning adults to the more developed Green River are only derived from those smolts that left as parr. The fry component did not appear to survive. Similar results were apparent in a number of other degraded estuaries. Figure provided by Lance Campbell, WDFW. Figure 5. Changes in spatial distribution of eelgrass between two consecutive mapping years in Horton Bay along with shoreline activities. Eelgrass is seen to progressively deteriorate as boat traffic increases and more docks are built. Figure provided by Natasha Nahirnick. KELP LIMITING FACTORS Prolonged (>35 days) temperatures >16° C. Grazing pressure from sea urchins and kelp crabs. Competition from other algae for substrate. EELGRASS LIMITING FACTORS Salinity over 42 ppt, high turbidity (lack of light), pH outside of 7.3 to 9.0, temps outside of 5° C to 30° C. Substrates with high levels of hydrogen sulfide (from long term log booming). Direct damage due to anchorages and presence of marine debris.

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