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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>data</strong>bases (e.g., corrections to past estimates of smolt emigration) are automatically corrected inthe integrated <strong>data</strong>base. This avoids the problem of having a centralized <strong>data</strong>base with duplicatebut out-of-date or incorrect versions of historical <strong>data</strong>. This approach is gradually beingimplemented in the Trinity <strong>River</strong> Restoration Program, <strong>and</strong> has also been recommended for otherrivers in the Western U.S., including the Klamath, Sacramento <strong>and</strong> San Joaquin. 15 There areconsiderable technical <strong>and</strong> institutional challenges in setting up such an approach, but thebenefits include fewer errors in <strong>data</strong> assembly, ease of inter-disciplinary integration, <strong>and</strong> muchmore timely application of quantitative analyses.In addition to improving the <strong>data</strong> available for underst<strong>and</strong>ing both the stressors affecting <strong>sockeye</strong><strong>and</strong> their life-stage specific survival rates, there needs to be improved application of quantitativemethods to these <strong>data</strong>. The goals of these analyses should be to reduce uncertainties critical tofisheries management decisions, <strong>and</strong> to improve our retrospective underst<strong>and</strong>ing of the factorsthat have affected <strong>sockeye</strong> survival rates <strong>and</strong> productivity. The quantitative methods that weapplied in this report were the simplest approaches that could be feasibly completed within thetime available. A small working group could consider other methods that should be applied tothe <strong>data</strong>base that we’ve assembled (as well as future improvements to it), including: simulation<strong>and</strong> statistical approaches incorporating non-linear <strong>and</strong> non-additive interactions; functionalregression analyses for continuously measured variables like temperature, salinity <strong>and</strong> discharge;control chart approaches to examine changes in the variability of both response measures <strong>and</strong>environmental variables; <strong>and</strong> Bayesian approaches which assign probability distributions to eachfactor <strong>and</strong> their interactions. Potential methods are more fully described in Appendix 3. Weemphasize the importance of extending these kinds of analyses to all 64 stocks assessed byPeterman <strong>and</strong> Dorner (2011), <strong>and</strong> others not included in their <strong>data</strong> set (e.g., Okanagan <strong>sockeye</strong>).The greater contrasts in both stock productivity <strong>and</strong> stressors provided by larger <strong>data</strong> sets willyield stronger insights on driving factors.Due to ecosystem complexity <strong>and</strong> year to year variability in environment-recruitmentcorrelations (see section 3.1 <strong>and</strong> English et al. 2011), we think that it will be very difficult todevelop reliable pre-season models to accurately predict <strong>sockeye</strong> returns. A more reasonableexpectation is that quantitative analyses will be primarily retrospective, <strong>and</strong> can yield only verygeneral forecasts (e.g., whether marine survival rates over the next two years are likely to bebelow average, about average, or above average). As discussed in English et al. 2011, in-season<strong>data</strong> <strong>and</strong> models will likely continue to be the primary tools used to manage harvest.15 See http://trrp.net/science/IIMS.htm for more information.106

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