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Fraser River sockeye salmon: data synthesis and cumulative impacts

Fraser River sockeye salmon: data synthesis and cumulative impacts

Fraser River sockeye salmon: data synthesis and cumulative impacts

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changes in <strong>Fraser</strong> <strong>sockeye</strong> stock productivity. As discussed in section 4.7, these effects are mostlikely to occur in Stage 4 (growth in the North Pacific <strong>and</strong> return to the <strong>Fraser</strong>).McKinnell et al. (2011) investigate how marine conditions along the coast may potentially haveaffected <strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong> <strong>salmon</strong> over recent decades <strong>and</strong> the 2005 brood year (2009returns) in particular. The physical conditions examined include wind, river discharge, salinity,temperature, water density, <strong>and</strong> water column stability. The primary biological conditionsexamined were the timing <strong>and</strong> magnitude of chlorophyll production. Broad scale climate driverscan influence river discharge <strong>and</strong> wind regimes, which may then influence the salinity of coastalwaters. Salinity <strong>and</strong> temperature interact to affect water density, water column stability <strong>and</strong>therefore surface mixing, which <strong>impacts</strong> the productivity of the surface layer <strong>and</strong> its potential toincrease in temperature. <strong>Fraser</strong> <strong>sockeye</strong> <strong>salmon</strong> are negatively affected by warmer <strong>and</strong> lessproductive ocean conditions. McKinnell et al. (2011, Sections 6.1, 6.2) explore the oceanography<strong>and</strong> climate of the Strait of Georgia <strong>and</strong> Queen Charlotte Strait/Sound.Johannes et al. (2011) explore how human activity <strong>and</strong> development in the areas surroundingStrait of Georgia may potentially have had a negative impact on habitat quality for <strong>sockeye</strong><strong>salmon</strong> as they leave the <strong>Fraser</strong> <strong>River</strong> estuary. Changes in the human population may be a proxyfor many feasible mechanisms by which human activity <strong>and</strong> development might directly impact<strong>sockeye</strong> <strong>salmon</strong> habitat quality. Increasing contaminants in the Strait of Georgia from mills,industrial facilities, chemical inputs to farming, <strong>and</strong> liquid <strong>and</strong> solid waste inputs couldpotentially degrade habitat quality. Forestry is a major l<strong>and</strong> use in the areas surrounding theStrait of Georgia. Although forestry has been shown to often have a negative effect on freshwater<strong>and</strong> estuary habitats for <strong>salmon</strong>, the potential impact on inshore marine habitat is uncertain(Johannes et al., 2011). Increased marine traffic may also create transient disturbances upon thesurface <strong>and</strong> contribute further contaminants to the water.Climate change could potentially have driven broad scale changes to the entire ecosystem(Hinch <strong>and</strong> Martins, 2011). It is plausible that climate change may have contributed to changesin the timing, magnitude, patterns, trends <strong>and</strong> variability in physical <strong>and</strong> biological habitatconditions along the coast. The potential <strong>impacts</strong> to <strong>sockeye</strong> <strong>salmon</strong> could be direct, such asincreases in sea surface temperature, or indirect, such as changes in predation, disease, or foodabundance <strong>and</strong> quality.4.4.2 Exposure of <strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong> to stressorsMost of the evidence on exposure to particular stressors during this life stage is based on anunderst<strong>and</strong>ing of the general migration route <strong>and</strong> timing of <strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong> <strong>salmon</strong> <strong>and</strong> an58

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