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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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“likely” contributor to the overall pattern <strong>and</strong> a “very likely”, potentially major, contributor tothe poor 2009 returns.Using the <strong>data</strong> collected from the other Cohen Commission technical projects, we haveconducted quantitative analyses over several time periods. The analyses use multiple regressionto compare the ability of several different oceanographic <strong>and</strong> climatic variables (measured inQCS <strong>and</strong> SoG) to explain the observed variability in <strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong> <strong>salmon</strong> productivity(i.e., ln(recruits/spawner)). A brief overview of the approach used is provided in Section 3.3.6<strong>and</strong> the details of the methodology <strong>and</strong> results are described in Appendices 3 <strong>and</strong> 4, respectively.We tested three model sets with the <strong>data</strong> available for marine conditions in QCS <strong>and</strong> SoG (Table4.4-1). Each model set represents a set of covariates or independent variables that have complete<strong>data</strong> over a specified period of time. Within each model set, different models (i.e., combinationsof variables) can be tested to determine their ability to explain the observed variability in thedependent variable. In the present case, the dependent or response variable is <strong>sockeye</strong> <strong>salmon</strong>productivity (ln (recruits/spawner)). Models can only be directly compared to other models in thesame model set (i.e., using the same set of <strong>data</strong>) but not to models in other model sets. The timeframes of the three model sets tested in this section are brood years 1969-2004, 1980-2004, <strong>and</strong>1996-2004. The key differences among the model sets examined are that sea surfacetemperatures were not available for QCS until 1980, <strong>and</strong> chlorophyll was not available until1996. The conclusions of these results are presented below, with details in Appendix 4.For 1969-2004 (Table 4.4-2), the results show that the SoG temperature model (M8) <strong>and</strong> theQCS salinity <strong>and</strong> discharge model (M4) were the two models with the most support, but neitherperformed substantially better than the “global” model, which is the model that contains all thevariables in the model set (i.e., M1 in Table 4.4-2). For SoG during this period, temperature (M8)is more valuable for explaining the observed variability in <strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong> <strong>salmon</strong>productivity than salinity (M7). Overall, the analysis of this time period shows that there issupport for both QCS <strong>and</strong> SoG models – the top ranked model was for SoG, the second for QCS,<strong>and</strong> the third was the global model, including both regions. These results show that for theseparticular variables, over this particular time period, there is no clear evidence of any differencebetween the explanatory value of the two regions; however, the absence of temperature <strong>data</strong> forQCS is a substantial shortcoming of this model set, <strong>and</strong> chlorophyll is not included in any model.65

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