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Potential Effects of Contaminants on Fraser River Sockeye Salmon

Potential Effects of Contaminants on Fraser River Sockeye Salmon

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(i.e., with regulati<strong>on</strong>s initially targeted <strong>on</strong> reducing AOX discharges to zero by 2002, andsubsequently amended to be in line with those established in the United States). Datafrom various sources indicate that biological treatment tends to reduce diversity and mass<str<strong>on</strong>g>of</str<strong>on</strong>g> chlorinated compounds in the effluent from bleached kraft pulp mills (Bjorseth et al.1976; McKague 1988; Kringstad and Lindstrom 1984). Janz et al. (2001) also reportedthat the c<strong>on</strong>centrati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> endocrine disrupting compounds in pulp mill effluent declinedwith sec<strong>on</strong>dary treatment. However, the extent to which the changes in pulp producti<strong>on</strong>processes, implemented in the 1990s, have reduced releases <str<strong>on</strong>g>of</str<strong>on</strong>g> endocrine disruptingcompounds and/or other c<strong>on</strong>taminants to the envir<strong>on</strong>ment has not been fully evaluated(Johannessen and Ross 2002). In summary, the substances <str<strong>on</strong>g>of</str<strong>on</strong>g> greatest c<strong>on</strong>cern relative toc<strong>on</strong>taminati<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> aquatic habitats by pulp and paper effluents include:• C<strong>on</strong>venti<strong>on</strong>al variables (such as pH, BOD and TSS; Samis et al. 1999);• Nutrients (such as amm<strong>on</strong>ia and phosphorus; Johannessen and Ross 2002);• Major i<strong>on</strong>s (such as chlorides; Hakeem and Bhatnager 2010);• Metals (such as cadmium, copper, and mercury; Hakeem and Bhatnager 2010);• M<strong>on</strong>o-aromatic hydrocarb<strong>on</strong>s (such as benzene and toluene; Suntio et al.1988);• Polycyclic aromatic hydrocarb<strong>on</strong>s (PAHs; such as parent and alkylated PAHs;Engwall et al. 2009);• Chlorinated phenolics (chlorophenols, chloroguaiacols, and chlorocatechols;Suntio et al. 1988);• Polychlorinated dibenzo-p-dioxins and polychlorinated dibenz<str<strong>on</strong>g>of</str<strong>on</strong>g>urans (such as2,3,7,8-TCDD; Mah et al. 1989);• Resin acids (abietic acid, neoabietic acid, dehydroabietic acid, palustric acid,levopimaric acid, pimaric acid, and isopimaric acid; Suntio et al. 1988);• Fatty acids (such as palmitic acid, stearic acid, lignoceric acid, oleic acid,linoleic acid, and linolenic acid; Suntio et al. 1988);• Surfactants [such as alkylphenol ethoxylates (APEOs); Johannessen and Ross2002]; and,• Natural plant horm<strong>on</strong>es (Johannessen and Ross 2002).15

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