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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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would provide evidence supporting the importance of these stressors. In examining the patternsover 64 <strong>Fraser</strong> <strong>and</strong> non-<strong>Fraser</strong> <strong>sockeye</strong> populations from Washington to SE Alaska, Peterman<strong>and</strong> Dorner (2011; pg. 3) comment that: “The large spatial extent of similarities in productivitypatterns that we found across populations suggests that there might be a shared causalmechanism across that large area.”, though they acknowledge that further work is required to testthis hypothesis. The Cohen Commission technical reports do not however include analyses ofthe relationships between stressors at this stage <strong>and</strong> productivity indices for non-<strong>Fraser</strong> <strong>River</strong><strong>sockeye</strong>.4.5.5 Other evidenceThe relevant technical reports do not present any further evidence for factors contributing tolong-term declines in <strong>sockeye</strong> <strong>salmon</strong> that fit within the WOE evaluation framework utilized (i.e.thresholds, specificity, experiments, or removals).4.5.6 ConclusionsTable 4.5-1 shows a summary of the results of the weight of evidence evaluation of potentialcontributing factors encountered in this stage of growth in the North Pacific <strong>and</strong> return to the<strong>Fraser</strong> <strong>River</strong>. All of the potential factors in this life stage have plausible mechanisms. There arevirtually no <strong>data</strong> on exposure for pathogens making no conclusion possible. Identical to theprevious stage, the evidence presented suggests that <strong>sockeye</strong> <strong>salmon</strong> returning through the Straitof Georgia have little direct exposure to human activities <strong>and</strong> development, leading to aconclusion that it is unlikely that these factors have contributed to the decline of <strong>Fraser</strong> <strong>River</strong><strong>sockeye</strong> <strong>salmon</strong>. Sockeye <strong>salmon</strong> have been exposed to predators, marine conditions, <strong>and</strong>climate change during this open ocean phase. There has been no evidence presented on anycorrelations between key predators <strong>and</strong> <strong>sockeye</strong> <strong>salmon</strong> survival. However, over the same timeperiod that <strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong> <strong>salmon</strong> productivity has been decreasing, some importantpredators appear or are believed to be increasing in abundance, many potentially importantalternate prey have been decreasing, <strong>and</strong> marine mammals have been increasing substantially(although it is believed there is no relationship with the changes in <strong>sockeye</strong> <strong>salmon</strong> population).It therefore remains possible that predators have contributed to the observed declines in <strong>sockeye</strong><strong>salmon</strong>. Both technical reports addressing marine conditions, as well as the report addressingclimate change, show or reference research that shows correlations with <strong>sockeye</strong> <strong>salmon</strong>patterns, but present no further evidence on thresholds, specificity, experiments, or removals.Marine conditions <strong>and</strong> climate change remain possible contributors to the long-term decline of<strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong> <strong>salmon</strong>. Peterman <strong>and</strong> Dorner’s analyses of delayed density dependencewere applied to total productivity over the whole life cycle. Therefore, their conclusions thatdelayed density dependence is unlikely to have been a primary factor causing productivity78

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