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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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The results show that the global model (M1) had the greatest level of support. The fact that thismodel was ranked highest even with 18 more variables than the next model indicates that thevariables associated with only a single project are not sufficient to explain the pattern inproductivity. When comparing the relative performance of models representing individualstressor categories the predators/alternate prey model (M5) has the greatest level of supportfollowed closely by the Lower <strong>Fraser</strong>/Strait of Georgia project (M7). The predator/alternate preymodel reflects two possible mechanisms for affecting <strong>Fraser</strong> <strong>sockeye</strong>: changes in the abundanceof predators <strong>and</strong>/or changes in the availability of alternate prey.As discussed above, each stressor category is only represented by the available <strong>data</strong>. Many ofthose categories are not adequately represented. For example, “climate change” (M6) is onlyrepresented by a single variable – the delayed effect of lower <strong>Fraser</strong> <strong>River</strong> water temperature forreturning adults – that does not fully capture the potential <strong>impacts</strong> of climate change on <strong>sockeye</strong><strong>salmon</strong> over their entire life. A second example is the impact of pathogens <strong>and</strong> disease, whichcould potentially be an important factor but are simply not represented within any of thesemodels due to the lack of <strong>data</strong>. Therefore it is not possible to make any conclusions at all aboutthe relative importance of pathogens <strong>and</strong> disease compared to other stressors, which is a majorweakness.Overall, we do not believe that organizing the <strong>data</strong> by stressor category is as useful as organizingthe <strong>data</strong> by life history stage. The boundaries between categories are arbitrary <strong>and</strong> many of themlack sufficient <strong>data</strong>. In the analysis organized around stressor category, none of the models haddefinitively higher support than the global model, which included all available variables. Bycontrast, when the exact same <strong>data</strong> were organized by life history stage, several of the modelsachieved a higher level of support than the global model.The results of this analysis raise the important issue (mentioned in Section 3.2) about correlationversus causation. An example of this issue is found within the predators model. Christensen <strong>and</strong>Trites (2011) show that the abundance of both Steller sea lions <strong>and</strong> Harbour seals have increasedsubstantially over the past few decades. Because the timeframe of that increase corresponds withthe period over which <strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong> <strong>salmon</strong> have been declining in productivity, thesemeasures are likely to exhibit a high degree of correlation. While it is possible, this does notnecessarily mean that the increase in pinnipeds is driving down the <strong>sockeye</strong> <strong>salmon</strong> population.Alternative explanations are: some other factor is affecting both populations; or, pinnipedpopulations have been recovering from low abundance since the banning of hunting <strong>and</strong> culling,<strong>and</strong> <strong>sockeye</strong> productivity is being driven by something else. Further study is required todetermine which of these possibilities are most likely. Any factor with a strong temporal trendover the same period of time as the strong temporal downtrend in <strong>sockeye</strong> <strong>salmon</strong> productivity98

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