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Potential Effects of Contaminants on Fraser River Sockeye Salmon

Potential Effects of Contaminants on Fraser River Sockeye Salmon

Potential Effects of Contaminants on Fraser River Sockeye Salmon

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Collectively, the results <str<strong>on</strong>g>of</str<strong>on</strong>g> studies <strong>on</strong> immunosuppressi<strong>on</strong> indicate that exposure toendocrine disrupting compounds has the potential to adversely affect salm<strong>on</strong> during theirtransiti<strong>on</strong> to the marine envir<strong>on</strong>ment. If the c<strong>on</strong>centrati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> endocrine disruptingcompounds were sufficient to elicit these types <str<strong>on</strong>g>of</str<strong>on</strong>g> effects in the <strong>Fraser</strong> <strong>River</strong>, the resultantmortality <str<strong>on</strong>g>of</str<strong>on</strong>g> smolts during transiti<strong>on</strong> to the marine envir<strong>on</strong>ment could have c<strong>on</strong>tributed tol<strong>on</strong>g-term declines in sockeye salm<strong>on</strong> abundance.Exposure to endocrine disrupting compounds may be an even greater c<strong>on</strong>cern for sockeyesalm<strong>on</strong> returning to the <strong>Fraser</strong> <strong>River</strong> for several reas<strong>on</strong>s. <strong>Sockeye</strong> salm<strong>on</strong> are exposed topersistent endocrine disrupting compounds, such as PCBs, PCDDs, and PCDFs, duringoutmigrati<strong>on</strong> and during their residence in the marine envir<strong>on</strong>ment (Krummel et al. 2003).During upstream migrati<strong>on</strong>, adult sockeye salm<strong>on</strong> utilize lipid and protein stores tosupport g<strong>on</strong>adal development (females) and morphological alterati<strong>on</strong>s (males). Therigours <str<strong>on</strong>g>of</str<strong>on</strong>g> upstream migrati<strong>on</strong> and associated physiological changes can result in 50 - 90%depleti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> somatic energy reserves (Hendry and Berg 1999). As a result, thec<strong>on</strong>centrati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> these c<strong>on</strong>taminants in somatic or g<strong>on</strong>adal tissues can increasedramatically between the time fish enter the mouth <str<strong>on</strong>g>of</str<strong>on</strong>g> the <strong>Fraser</strong> <strong>River</strong> and arrive at theirnatal streams. DeBruyn et al. (2004) estimated that the c<strong>on</strong>centrati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> PCBs, PCDDs,and PCDFs in muscle tissue could increase by 4.8 to 10.4 times for various <strong>Fraser</strong> <strong>River</strong>sockeye salm<strong>on</strong> stocks, with the highest magnificati<strong>on</strong> rates predicted for the fish thatcomplete the l<strong>on</strong>gest migrati<strong>on</strong>. Predicted c<strong>on</strong>taminant magnificati<strong>on</strong> rates weresomewhat lower (i.e., 3.9 to 7.9) for g<strong>on</strong>ads. Such c<strong>on</strong>taminant magnificati<strong>on</strong> waspredicted to result in c<strong>on</strong>centrati<strong>on</strong>s in eggs that exceeded the toxicity threshold forsalm<strong>on</strong>id fishes <str<strong>on</strong>g>of</str<strong>on</strong>g> 3 ng/kg lipid, which is associated with 30% mortality <str<strong>on</strong>g>of</str<strong>on</strong>g> eggs (DeBruynet al. 2004). Although little informati<strong>on</strong> is available with which to make inferences, it ispossible that exposure <str<strong>on</strong>g>of</str<strong>on</strong>g> adult sockeye salm<strong>on</strong> to endocrine disrupting compounds insurface water during upstream migrati<strong>on</strong> could also compromise immunocompetence. Ifso, such exposures could make sockeye salm<strong>on</strong> more susceptible to infecti<strong>on</strong> by diseaseagents, particularly during migrati<strong>on</strong> periods characterized by elevated watertemperatures. Such effects could translate into increases in en-route mortality and/or prespawningmortality.6.2 <str<strong>on</strong>g>Potential</str<strong>on</strong>g> <str<strong>on</strong>g>Effects</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> <str<strong>on</strong>g>C<strong>on</strong>taminants</str<strong>on</strong>g> <str<strong>on</strong>g>of</str<strong>on</strong>g> Emerging C<strong>on</strong>cern <strong>on</strong> <strong>Sockeye</strong>Salm<strong>on</strong>The term “c<strong>on</strong>taminants <str<strong>on</strong>g>of</str<strong>on</strong>g> emerging c<strong>on</strong>cern” is used to describe a broad group <str<strong>on</strong>g>of</str<strong>on</strong>g>chemicals that were previously unknown or were not previously recognized as being <str<strong>on</strong>g>of</str<strong>on</strong>g>105

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