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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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<strong>Fraser</strong> <strong>and</strong> non-<strong>Fraser</strong> <strong>sockeye</strong> populations. Hierarchical Bayesian methods areincreasingly common in applied fisheries science, <strong>and</strong> this particular case would seemto benefit from information-sharing among multiple stocks.Response: As discussed above, we did not have time to implement such approaches, thoughwe have now exp<strong>and</strong>ed our description of alternative modelling approaches.I expected this report on <strong>cumulative</strong> effects to provide a "systems" view of <strong>sockeye</strong><strong>salmon</strong> dynamics. That is, factors affecting <strong>sockeye</strong> dynamics do not necessarilyoperate independently, unidirectionally (i.e., all arrows point to only <strong>sockeye</strong>), <strong>and</strong>linearly. Sockeye <strong>salmon</strong> populations influence, <strong>and</strong> are influenced by, many potentialfeedbacks within freshwater, river, <strong>and</strong> oceanic ecosystems.Response: We agree, <strong>and</strong> our conceptual model (while not representing all interactions forreasons stated above) do show various interactions amongst factors. However, our terms ofreference (Appendix 1) as well as those of the Cohen Commission(http://www.cohencommission.ca/en/TermsOfReference.php) are explicitly <strong>sockeye</strong>-centric,rather than ecosystem-centric. Therefore, we have been more focused on how variousecosystem stressors affect <strong>sockeye</strong>, rather than the reverse effects (how <strong>sockeye</strong> affectecosystems). To provide a more “systems” view, we’ve added some text under thediscussions of Plausible Mechanisms (e.g., in Section 4.2.1, we note that decliningabundances of <strong>sockeye</strong> result in less nutrients being transferred from marine to freshwaterecosystems, with potential negative effects on both subsequent generations of <strong>sockeye</strong> <strong>and</strong>other ecosystem components). In section 4.4.1, we discuss various ecosystem processesaffecting the degree of predation on <strong>sockeye</strong> in inshore areas. As discussed above, we havementioned feedbacks in Figures 3.3.1 <strong>and</strong> 2.3.1.This may reflect my ignorance, but has any research been done to determine whetherthe observed pattern in productivity is an expected result of Ricker-type stock-recruitdynamics? Are <strong>sockeye</strong> populations over-shooting some capacity limits <strong>and</strong> thereforeshowing natural signs of suppressed productivity? The abundances of <strong>sockeye</strong> duringthe 1990s <strong>and</strong> early 2000s were very high all over the northeast Pacific (includingAlaska), which may have lead to covariation in ocean growth <strong>and</strong> survival over broadspatial scales. I am not aware of recent research examining among-stock densitydependencein ocean survival of <strong>sockeye</strong>, even though it might be possible. Scientistshave argued for decades that massive enhancement of Japanese chum <strong>salmon</strong>suppresses growth of North American chum <strong>salmon</strong>, so I wonder why similar argumentshave not been explored for <strong>sockeye</strong>.Response: The regression models we applied included Ricker-model representations ofdensity dependence for each stock. Ruggerone et al. (2010) have an excellent summary oftrends in wild <strong>and</strong> hatchery <strong>salmon</strong> populations, <strong>and</strong> note that hatchery-raised chum form62% of the combined total wild <strong>and</strong> hatchery <strong>salmon</strong> abundance. They also discuss thepotential for a “tragedy of the commons” effect in the North Pacific. Our analyses of theeffects of pink <strong>salmon</strong> abundance reflect potential competitive <strong>impacts</strong> of wild plus141

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