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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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salinity. There is much evidence that very warm years tend to negatively affect certaincharacteristics of <strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong> <strong>salmon</strong> biology (McKinnell et al., 2001, Section 3.5).This broad scale shift in oceanographic conditions coincides with a “shift” in median <strong>Fraser</strong><strong>River</strong> <strong>sockeye</strong> <strong>salmon</strong> productivity that may have also occurred in 1992. McKinnell et al. (2011)propose that the underlying pattern of a marked shift in productivity occurring in 1992 provides abetter fit to the observed productivity <strong>data</strong> than does the idea of a gradual decline over time <strong>and</strong>that there are other comparable <strong>sockeye</strong> stocks on the west coast that exhibited similar declinesbeginning in 1992, though many of those stocks subsequently demonstrated recovery with the1998/99 la Niña. In 2007, the Gulf of Alaska was generally cool, which is not consistent with thepoor returns observed in 2009. In terms of biological ocean conditions, McKinnell et al. (2011)state that for the open ocean, “there is no trend in average nutrient concentrations in the southernGulf of Alaska (Station Papa) since the 1950s, no trend in average chlorophyll a since 1998, <strong>and</strong>no trend in average zooplankton biomass.Hinch <strong>and</strong> Martins (2011) report that it is possible that the survival of immature <strong>sockeye</strong> <strong>salmon</strong>has decreased in association with climate change. Although there are no lab <strong>data</strong> <strong>and</strong> little field<strong>data</strong> on the response of adult <strong>sockeye</strong> to climate change in the open ocean, it does appear that<strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong> <strong>salmon</strong> survival is negatively correlated to the sea surface temperature oftheir last few months at sea (Hinch <strong>and</strong> Martins, 2011, Section 1.4). They further report that seasurface temperatures in the Strait of Georgia <strong>and</strong> the Gulf of Alaska have been consistentlyincreasing since the 1950s, while sea surface salinity <strong>and</strong> pH have been decreasing over the sameperiod (Hinch <strong>and</strong> Martins, 2011, Section 1.5). However, there is also evidence that much of theobserved warming trend can be attributed to the 1977-1997 positive phase of the PDO, ratherthan longer-term changes in climate (Hinch <strong>and</strong> Martins, 2011, Section 1.5).Returning <strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong> <strong>salmon</strong> will encounter the same potential stressors associatedwith human activity <strong>and</strong> development surrounding the Strait of Georgia as described in Section4.4, though the extent of this exposure will vary based on the rate of northern diversion, asdescribed above in Section 4.5.2.4.5.4 Correlation/consistency with patterns in non-<strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong>productivityOur comments here are identical to those for Stage 3 in section 4.5.3. Many other <strong>sockeye</strong> stocksshare the same habitat of the North Pacific Ocean with <strong>Fraser</strong> <strong>River</strong> <strong>sockeye</strong> <strong>salmon</strong>. Stocks thatshare both geographic <strong>and</strong> temporal overlap in the open ocean will likely encounter similarpathogens, predators <strong>and</strong> ocean conditions during this stage. The extent to which such stocksshow similar trends in productivity to those of the <strong>Fraser</strong> <strong>River</strong> (see Peterman <strong>and</strong> Dorner, 2011)77

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