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Fraser River sockeye salmon: data synthesis and cumulative impacts

Fraser River sockeye salmon: data synthesis and cumulative impacts

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Stage 5: Migration back to SpawnWhile the timing of en-route mortality coincides generally with the <strong>Fraser</strong> <strong>sockeye</strong> situation,the <strong>Fraser</strong> <strong>sockeye</strong> productivity indices already account for en-route mortality (i.e., recruits =spawners + harvest + en-route mortality). Therefore, there is no point in examining correlationsbetween en-route mortality <strong>and</strong> life cycle or post-juvenile productivity indices within the samegeneration. The only possible effects on productivity indices are inter-generational effects, forwhich the evidence is limited <strong>and</strong> equivocal. We therefore conclude that it is unlikely that enroutemortality (or pre-spawn mortality, which has only increased for Late Run <strong>sockeye</strong>) are aprimary factor in declining indices of <strong>Fraser</strong> <strong>sockeye</strong> productivity. However, en-route mortalityhas definitely had a significant impact on the <strong>sockeye</strong> fishery <strong>and</strong> the numbers of adult fishreaching the spawning ground, particularly for the Early <strong>and</strong> Late runs. Pre-spawn mortality,habitat changes, <strong>and</strong> contaminants are unlikely to be responsible for the overall pattern ofdeclining <strong>sockeye</strong> productivity. No conclusion is possible regarding pathogens due toinsufficient <strong>data</strong>. None of the factors assessed for this life history stage are likely to have shownsignificant changes between 2009 <strong>and</strong> 2010.The above conclusions are based on qualitative <strong>and</strong> quantitative analyses of existing information.There are two important caveats on these conclusions. First, there are major gaps in both ourfundamental underst<strong>and</strong>ing of how various factors interact to affect <strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong><strong>salmon</strong>, <strong>and</strong> in the <strong>data</strong> available to quantify those factors. Second, all Cohen Commissionresearchers have had a limited amount of time to analyze existing information; future <strong>data</strong>syntheses <strong>and</strong> analyses will likely provide deeper <strong>and</strong> different insights. Below, we summarizeour recommendations for improving the <strong>data</strong> <strong>and</strong> underst<strong>and</strong>ing of <strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong> <strong>salmon</strong>.5.2 Research <strong>and</strong> Monitoring PrioritiesOur summary of research <strong>and</strong> monitoring priorities includes findings from both the workshopinvolving all Cohen Commission researchers (held Nov. 30 – Dec. 1, 2010), <strong>and</strong> our <strong>synthesis</strong> ofthe more detailed recommendations contained in the Cohen Commission’s technical reports.5.2.1 Results from the workshopWorkshop participants were asked to examine section 5.3 of the Expert Panel’s Report to thePacific Salmon Commission (PSC report), Priorities for Monitoring <strong>and</strong> Research (Peterman etal. 2010), as a starting point for a plenary discussion. Since each of the twelve projects containsrecommendations specific to their topic areas, the purpose of this exercise was to broadly addresspriorities for monitoring <strong>and</strong> research beyond project boundaries.103

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