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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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4.2.6 ConclusionsTable 4.2-1 follows the logic of the flow chart in Figure 3.3-1, showing our conclusionsregarding the effects of each stressor on life history stage 1 (including eggs, alevins, fry, <strong>and</strong>parr). Our conclusions relate to the overall trends in <strong>sockeye</strong> productivity over the last twodecades.Table 4.2-1. Evaluation of the relative likelihood that potential stressors encountered by <strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong><strong>salmon</strong> during life history stage 1 (including eggs, alevins, fry, <strong>and</strong> parr), have contributed to overalldeclines in productivity in recent decades. Some factors may have had effects on some stocks in some years(e.g., density dependence affecting Quesnel <strong>sockeye</strong>), but are unlikely to have been responsible for theoverall pattern across all <strong>Fraser</strong> <strong>sockeye</strong> stocks. See section 4.7 for further discussions of correlations.Factor Mechanism Exposure Correlation/Consistency Other LikelihoodEvidenceForestry b Yes Yes No No a UnlikelyMining Yes Low Not done No a UnlikelyLarge hydro Yes Yes No Against UnlikelySmall hydro Yes Low No No a UnlikelyUrbanization Yes Yes No No a Unlikelyabove HopeAgriculture b Yes Yes No No a UnlikelyWater Use Yes Yes No Yes UnlikelyContaminants Yes Yes No Yes UnlikelyDensity Yes Some No No UnlikelyDependentMortalitystocksPathogens Yes Few <strong>data</strong> Not done Yes NoconclusionpossiblePredators Yes Few <strong>data</strong> No No UnlikelyL. <strong>Fraser</strong> l<strong>and</strong> Yes Yes for No No Unlikelyusesag/for; Nofor othersClimate Yes Yes Weak evidence Mixed PossibleChangeevidencea It is difficult to establish hazard thresholds for the proportion of watershed area above which there are negative<strong>impacts</strong> on <strong>sockeye</strong> spawning <strong>and</strong> rearing. Such thresholds are better defined for contaminants <strong>and</strong> water use.bAgriculture <strong>and</strong> forestry rows include evidence from both Technical Reports 3 (Nelitz et al. 2011) <strong>and</strong> 12(Johannes et al. 2011). Forestry includes logging, Mountain Pine Beetle <strong>and</strong> log storage.With the exception of climate change, which we consider to be a possible factor, <strong>and</strong> pathogens(for which no conclusion is possible due to <strong>data</strong> gaps), it is unlikely that the above factors (i.e.forestry, mining, large <strong>and</strong> small hydro, urbanization, agriculture, water use, contaminants,density dependent mortality, predators, <strong>and</strong> Lower <strong>Fraser</strong> l<strong>and</strong> use), taken <strong>cumulative</strong>ly, were theprimary drivers behind long term declines in <strong>sockeye</strong> productivity across the <strong>Fraser</strong> Basin. We48

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