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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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general, the potential mechanisms in this stage are similar to those described for Stage 3 (Section4.4) above.The high risk pathogens described earlier are known or suspected to potentially affect bothjuveniles <strong>and</strong> adults. However, although Parvicapsula minibicornis has been documented to behighly prevalent in <strong>sockeye</strong> <strong>salmon</strong> smolts, it is not found in adults, which suggests thatmortality due to this pathogen occurs within the early marine phase (Kent, 2011). Overall, verylittle is known about pathogens <strong>and</strong> disease in the marine environment (Kent, 2011).The potential mechanisms for predators to affect <strong>sockeye</strong> <strong>salmon</strong> populations are the same asabove (increased abundance, increased predation rate, or decreases in alternate prey) but theassemblage of potential predators is different. Christensen <strong>and</strong> Trites (2011) identify <strong>salmon</strong>shark <strong>and</strong> daggertooth as key predators of adult <strong>sockeye</strong> <strong>salmon</strong> that could plausibly have had anincreasing impact on <strong>sockeye</strong> <strong>salmon</strong> populations. Sockeye <strong>salmon</strong> is known to comprise a largeportion of the diet of <strong>salmon</strong> sharks. Blue sharks do not specialize on <strong>sockeye</strong> <strong>salmon</strong>, but do eat<strong>salmon</strong> in general <strong>and</strong> are much more abundant than <strong>salmon</strong> sharks. On the return journey backto the <strong>Fraser</strong>, there are many marine mammals that will prey on adult <strong>salmon</strong>. In some cases,<strong>sockeye</strong> <strong>salmon</strong> do not appear to be a substantial portion of any of their diets but, as illustratedby the spiny dogfish example in Section 4.4.2, this does not necessarily imply that such predatorsdo not have an impact on <strong>sockeye</strong> <strong>salmon</strong>. The effect of any predator on <strong>sockeye</strong> depends on thepredator’s abundance, the proportion of the predator’s diet which consists of <strong>sockeye</strong> <strong>salmon</strong>,<strong>and</strong> the resulting total biomass of <strong>sockeye</strong> consumed by the predator. Data collected by P.FOlesiuk (unpublished) on Steller sea lion scat samples was presented at both the PSC workshop<strong>and</strong> the Cohen Commission workshop. These <strong>data</strong> show that adult <strong>salmon</strong> is a commoncomponent of the diet of Steller sea lions, being found in approximately 12-30% of samples,varying by season (Peterman et al. 2010, A. Trites, workshop presentation). These samples werenot identified by species. Other research has suggested that <strong>salmon</strong> represent approximately 10%of the overall diet of Steller sea lions, <strong>and</strong> that <strong>sockeye</strong> <strong>salmon</strong> contribute to 9% of that portion(i.e. 0.9% of the total diet; A. Trites, workshop presentation). However, since Steller sea lionsconsume a large amount of biomass, a small proportion of that consumption could still plausiblyhave a meaningful effect on <strong>sockeye</strong> <strong>salmon</strong>. The technical report on predators did not includeestimates of total <strong>sockeye</strong> consumed by Steller sea lions. The bird predators described above arenot relevant to this life stage. Returning adult <strong>sockeye</strong> <strong>salmon</strong> are a very different prey then theirearlier post-smolt forms: larger, but fewer <strong>and</strong> faster.The biological <strong>and</strong> physical ocean conditions are fundamentally important for the health <strong>and</strong>survival of maturing <strong>sockeye</strong> <strong>salmon</strong> in the North Pacific Ocean. For example, oceantemperature has a critical influence on bioenergetics for <strong>sockeye</strong> <strong>salmon</strong> (McKinnell et al.,72

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