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Potential Effects of Contaminants on Fraser River Sockeye Salmon

Potential Effects of Contaminants on Fraser River Sockeye Salmon

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8.9 Recommendati<strong>on</strong>sThis evaluati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> the effects <str<strong>on</strong>g>of</str<strong>on</strong>g> c<strong>on</strong>taminants <strong>on</strong> <strong>Fraser</strong> <strong>River</strong> sockeye salm<strong>on</strong> wasc<strong>on</strong>strained by a number <str<strong>on</strong>g>of</str<strong>on</strong>g> key data gaps. As insufficient data were available to fullyassess the role <str<strong>on</strong>g>of</str<strong>on</strong>g> c<strong>on</strong>taminant exposures in the declines <str<strong>on</strong>g>of</str<strong>on</strong>g> sockeye salm<strong>on</strong> over the pasttwo decades or the low returns <str<strong>on</strong>g>of</str<strong>on</strong>g> sockeye salm<strong>on</strong> to the <strong>Fraser</strong> <strong>River</strong> in 2009, severalrecommendati<strong>on</strong>s are <str<strong>on</strong>g>of</str<strong>on</strong>g>fered to enhance the probability that the requisite data andinformati<strong>on</strong> are available in the future. These recommendati<strong>on</strong>s include:• Effluent m<strong>on</strong>itoring programs for all industrial sectors should be reviewed andevaluated to determine if they provide the necessary and sufficient data tocharacterize effluents and evaluate effects <strong>on</strong> aquatic ecosystems. The results<str<strong>on</strong>g>of</str<strong>on</strong>g> such m<strong>on</strong>itoring programs should be compiled in a single database that ispublically accessible.• Routine m<strong>on</strong>itoring programs should be developed and implemented toprovide the data needed to characterize exposure <str<strong>on</strong>g>of</str<strong>on</strong>g> sockeye salm<strong>on</strong> to aquaticc<strong>on</strong>taminants in the incubati<strong>on</strong> habitats, rearing habitats, and migratory habitatsthat are used by sockeye salm<strong>on</strong> c<strong>on</strong>servati<strong>on</strong> units;• Such m<strong>on</strong>itoring programs should evaluate water quality, sediment quality, andfish-tissue quality <strong>on</strong> temporal and spatial scales that are relevant for assessingeffects <strong>on</strong> sockeye salm<strong>on</strong> and other key indicators <str<strong>on</strong>g>of</str<strong>on</strong>g> envir<strong>on</strong>mental qualityc<strong>on</strong>diti<strong>on</strong>s;• Such m<strong>on</strong>itoring programs should address the aquatic c<strong>on</strong>taminants identifiedin this investigati<strong>on</strong>. To help focus such m<strong>on</strong>itoring programs, thec<strong>on</strong>taminants <str<strong>on</strong>g>of</str<strong>on</strong>g> c<strong>on</strong>cern in each area <str<strong>on</strong>g>of</str<strong>on</strong>g> interest have been identified (Table8.1). Near-term priorities should include TSS and streambed substrate qualitym<strong>on</strong>itoring in incubati<strong>on</strong> habitats, nutrient m<strong>on</strong>itoring in rearing habitats,dissolved metal m<strong>on</strong>itoring in all habitats, and selenium, PCB, andPCDD/PCDF m<strong>on</strong>itoring in all habitats, and selenium, PCB, and PCDD/PCDFm<strong>on</strong>itoring in fish tissues. It is likely that well-designed surveys will berequired to identify the appropriate scale <str<strong>on</strong>g>of</str<strong>on</strong>g> m<strong>on</strong>itoring for endocrinedisrupting compounds and c<strong>on</strong>taminants <str<strong>on</strong>g>of</str<strong>on</strong>g> emerging c<strong>on</strong>cern;• Ambient m<strong>on</strong>itoring programs should also include direct measures <str<strong>on</strong>g>of</str<strong>on</strong>g> effects <strong>on</strong>sockeye salm<strong>on</strong>, such as morphology, physiology, en-route mortality, prespawnmortality, and egg viability;140

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