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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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how effects at different life history stages can accumulate over the whole life cycle, increasingthe <strong>cumulative</strong> stress on an individual <strong>salmon</strong> to the point where it dies. The accumulation ofstress may be concentrated in one life history stage or distributed across multiple life historystages. The stress experienced within each life history stage may be insufficient to causemortality, but the <strong>cumulative</strong> effect of stressors in multiple life history stages can cause death.However, mortality events at an early life history stage can also result in a compensatoryreduction in competitive stress for those fish which survived, reducing their <strong>cumulative</strong> stress<strong>and</strong> increasing their chances of survival. These two sets of processes illustrated in Figure 3.3-1<strong>and</strong> 2.3-1 (i.e., <strong>cumulative</strong> <strong>impacts</strong> from many stressors within each life history stage, <strong>cumulative</strong>effects on each fish over its life) occur concurrently within each generation of <strong>sockeye</strong>.Table 4.7-1 summarizes the results of our analyses by life history stage. We found only twofactors (marine conditions <strong>and</strong> climate change) which were likely to have been a primary factorin the observed declines in <strong>Fraser</strong> <strong>sockeye</strong> productivity (recruits/spawner) over the last twodecades. While en route mortality has definitely had an impact on the <strong>sockeye</strong> fishery <strong>and</strong>numbers of fish reaching the spawning ground, it is unlikely to have affected total productivity,since en route mortality is already included in the calculation of total recruits (i.e., recruits =spawners + en-route mortality + harvest). The effects of predators during the marine phase of the<strong>salmon</strong> life cycle (stages 3 <strong>and</strong> 4 in Table 4.7-1) were judged to be possible primary contributorsto these declines. Due to lack of <strong>data</strong> it is not possible to draw conclusions about thecontributions of pathogens, which is a particularly important <strong>data</strong> gap that we discuss further inour recommendations (Section 5). Aquaculture was not considered in our report as theCommission Technical Reports on this potential stressor were not available, but will beconsidered in an addendum to this report. All other factors (i.e., forestry, mining, large hydro,small hydro, urbanization, agriculture, water use, contaminants, density dependent mortality,human activity <strong>and</strong> l<strong>and</strong> uses in the Lower <strong>Fraser</strong> <strong>and</strong> Strait of Georgia) were judged to beunlikely as primary causes of long term productivity declines, though they may still have beencontributory factors. That is, stressors which we consider unlikely to be primary causes ofproductivity declines, may combine with other factors to create sufficient <strong>cumulative</strong> stress tokill <strong>salmon</strong> (i.e., through additive or greater than additive (synergistic) interactions) in somestocks in some years.The coastal migration phase of the <strong>sockeye</strong>’s life history provides a good example of multiplestressors interacting to cause <strong>cumulative</strong> <strong>impacts</strong>. There is indirect evidence that while oceantemperatures were not high enough to directly kill <strong>sockeye</strong> smolts in the summer of 2007, thesewarmer temperatures may have decreased the quantity <strong>and</strong> quality of available food <strong>and</strong>increased other stressors (e.g., metabolic dem<strong>and</strong>s during inshore migration, vulnerability topredators, the level of pathogens <strong>and</strong> harmful algae); see McKinnell et al (2011) <strong>and</strong> Peterman et88

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