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Fraser River Sockeye Fisheries and Fisheries Management - Cohen ...

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econstruction-based model developed by Bill Gazey was employed. This modelincorporated features of the cumulative-normal <strong>and</strong> cumulative-passage-to-date models,<strong>and</strong> implemented an objective method for combining the estimates from its componentmodels based on the relative uncertainty of these models. This model has since beenreplaced by a Bayesian time <strong>and</strong> density model using Winbugs software, similar inconcept to the Cumulative Normal model. This model incorporates historical informationon run-size, timing, spread of the migration <strong>and</strong> test fishing expansion line (inverse ofcatchability, see below) in the form of prior probability distributions or “Priors” as wellas in-season reconstructions of daily abundance <strong>and</strong> test fishing CPUE. Previously, aCumulative Passage model had also been employed but this model has been discontinuedas priors on timing <strong>and</strong> historical distributions make its use redundant in the currentmodel. The models described previously (PSC 1995) that used exclusively commercialcatch <strong>and</strong> effort data have also been discontinued, due primarily to the major changes infishing pattern, levels of effort <strong>and</strong> irregularity of the fisheries which provide the sourcedata for these models.The Pacific Salmon Commission conducts “Panel Approved Test <strong>Fisheries</strong>” in the marineareas “inside” Vancouver Isl<strong>and</strong> <strong>and</strong> in the <strong>Fraser</strong> <strong>River</strong> below Mission to collect CPUEdata <strong>and</strong> biological information on stock identification <strong>and</strong> species composition. DailyCPUE data in combination with the stock composition information <strong>and</strong> historicalestimates of catchability (q) are used to project stock abundances from the marine testfisheries. Catchability or “q” is defined as the proportion of a population removed by adefined unit of effort <strong>and</strong> the “Expansion line” is the inverse of catchability (1/q). DailyCPUE data are multiplied by expansion lines to generate estimates of abundance inmarine areas from test fisheries. The CPUE-based estimates are used until the stockspass the Mission Hydroacoustics site 6 days later in the case of Early Stuart, EarlySummer-run <strong>and</strong> Summer-run sockeye. During some years, Late-run sockeye (WeaverCreek <strong>and</strong> Harrison <strong>River</strong> sockeye) pass directly upstream, a phenomenon known as“Early Upstream Migration” (http://www.psc.org/pubs/LateRun/R-69_LateRun<strong>Sockeye</strong>Conf_2009_final.pdf). In these situations the projected abundancesfrom marine test fisheries are replaced with estimates from the Mission Hydroacousticsprogram 6-8 days later. However on the 2010 <strong>and</strong> 2011 cycle years, Late-run sockeyeare dominated by Late Shuswap sockeye, the majority of which continue to delay in theStrait of Georgia. Therefore the assessment of run-size, timing <strong>and</strong> escapement to theStrait of Georgia are derived from the marine test fisheries. During these years, most ofthe escapement of Late-run stocks passes Mission too late to be used in assessments forthe management of most fisheries although these data still form the best estimate ofpotential spawning escapement.I-2

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