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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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There are many marine predators that may consume <strong>sockeye</strong> post-smolts as they migrate fromthe mouth of the <strong>Fraser</strong> northward along the coast. Christensen <strong>and</strong> Trites (2011) identify spinydogfish, coho <strong>salmon</strong>, chinook <strong>salmon</strong>, juvenile sablefish, humbolt squid, <strong>and</strong> arrowtoothflounder as potential fish predators. Potential bird predators include common tern, arctic tern,pelagic cormorant, Br<strong>and</strong>t’s cormorant, gulls, <strong>and</strong> common murre. Mortality due to predation islikely to have always been high during this life stage as the sheer abundance of post-smoltsmigrating up the coast would have always attracted a diversity of predators, but if the level ofpredation has increased in recent decades, the impact on the <strong>sockeye</strong> <strong>salmon</strong> population mayhave also increased. Marine mammal predators (including pinnipeds <strong>and</strong> cetaceans) have beendocumented eating <strong>salmon</strong> post-smolts but there is no evidence of marine mammal predation on<strong>sockeye</strong> <strong>salmon</strong> post-smolts (Christensen <strong>and</strong> Trites, 2011). However, knowledge on the diet,abundance, distribution <strong>and</strong> biology of potential predators is often scarce. For example, littleinformation is known on the diet of Pacific white-sided dolphins, but <strong>salmon</strong> might represent 30-60% of their diet during June through November (Christensen <strong>and</strong> Trites, 2011). Salmon is alsoknown to be an important prey species for Steller sea lions, although the evidence suggests thatSteller sea lions predominantly eat adult <strong>salmon</strong> rather than juveniles. Knowledge of specificpredator-prey associations is largely based on diet information for predators but such informationis largely qualitative <strong>and</strong> often non-existent for particular predators of interest (Christensen <strong>and</strong>Trites, 2011). Overall, Christensen <strong>and</strong> Trites (2011) emphasize that even if it could be shownthat the aggregate rate of predation on <strong>sockeye</strong> <strong>salmon</strong> has increased substantially over the pastseveral decades, it would likely still not be possible to determine whether predation itself wascontributing to the decline of <strong>sockeye</strong> <strong>salmon</strong> or predators are simply acting as the“executioners” of <strong>sockeye</strong> <strong>salmon</strong> that were already less healthy <strong>and</strong> slower due to some otherunderlying driver.Christensen <strong>and</strong> Trites (2011) also put forth an alternate theory regarding the potential impact ofpredation on <strong>sockeye</strong> <strong>salmon</strong>. They suggest that if there have been substantial declines in thepopulations of alternate prey species that are physically comparable to <strong>sockeye</strong> <strong>salmon</strong>,predators that might otherwise not eat or not prefer <strong>sockeye</strong> <strong>salmon</strong> might increase theirconsumption. In this situation, it would be possible for predators to have an increased impact on<strong>sockeye</strong> <strong>salmon</strong> while not actually increasing in abundance.Competition is another plausible mechanism of potential importance discussed by Christensen<strong>and</strong> Trites (2011). Ruggerone et al. (2010) summarize trends in wild <strong>and</strong> hatchery populations inthe North Pacific, <strong>and</strong> discuss the potential for a “tragedy of the commons” effect due toincreased numbers of fish competing for a finite pool of food resources. In section 4.7, weconsider the extent to which total pink <strong>salmon</strong> abundance (wild plus hatchery) can explain57

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