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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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insecticides, such as phorate, terbufos, or f<strong>on</strong><str<strong>on</strong>g>of</str<strong>on</strong>g>os. Elevated c<strong>on</strong>centrati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g>insecticides, such as azinphosmethyl and diazin<strong>on</strong>, have been detected in irrigati<strong>on</strong> ditches,run<str<strong>on</strong>g>of</str<strong>on</strong>g>f, and tributaries in the vicinity <str<strong>on</strong>g>of</str<strong>on</strong>g> cranberry bogs. Ginseng farms, which arefrequently sited adjacent to waterways, are also known to utilize substantial quantities <str<strong>on</strong>g>of</str<strong>on</strong>g>herbicides (such as fluazifop-p-butyl), insecticides (such as diazin<strong>on</strong>), and fungicides (suchas iprodi<strong>on</strong>e; Harris<strong>on</strong> et al.1991). Furthermore, use <str<strong>on</strong>g>of</str<strong>on</strong>g> pyrethroids in various agriculturaland other applicati<strong>on</strong>s represents an emerging c<strong>on</strong>cern due to their mobility and hightoxicity to aquatic organisms (Kemble et al. 2010).The results <str<strong>on</strong>g>of</str<strong>on</strong>g> this review, indicate that a wide variety <str<strong>on</strong>g>of</str<strong>on</strong>g> c<strong>on</strong>taminants can be released toaquatic ecosystems within the <strong>Fraser</strong> <strong>River</strong> Basin in run<str<strong>on</strong>g>of</str<strong>on</strong>g>f from agricultural operati<strong>on</strong>s.Based <strong>on</strong> the quantities <str<strong>on</strong>g>of</str<strong>on</strong>g> these substances that are used in the province, it is likely thatthe highest priority c<strong>on</strong>taminants associated with agricultural activities in the study areainclude (MDH 1999; Verrin et al. 2004):• C<strong>on</strong>venti<strong>on</strong>al variables (BOD, TSS);• Nutrients (i.e., nitrate, nitrite, amm<strong>on</strong>ia, urea, phosphorus);• Metals (i.e., arsenic, cadmium, copper, lead, zinc);• Organochlorine pesticides (i.e., chlordane, DDTs, dieldrin, endosulfan,hexachlorobenzene, lindane, n<strong>on</strong>achlor);• In-use herbicides (i.e., atrazine, 2,4-D, ethalfluralin, glyphosate, mineral oil,paraquat, pendimethalin, simazine, triallate, trifluralin);• In-use insecticides (i.e., azinphosmethyl, Bacillis thuringiensis, chlorpyrifos,diazin<strong>on</strong>, endosulfan, malathi<strong>on</strong>, mineral oil, parathi<strong>on</strong>)• In-use fungicides (i.e., captan, copper, chlorothal<strong>on</strong>il, dazomet, mancozeb,metam, metiram, lime sulphur); and,• Other pesticides (i.e., formaldehyde, formalin).3.1.2.3 Run<str<strong>on</strong>g>of</str<strong>on</strong>g>f <str<strong>on</strong>g>of</str<strong>on</strong>g> Municipal StormwaterRun<str<strong>on</strong>g>of</str<strong>on</strong>g>f <str<strong>on</strong>g>of</str<strong>on</strong>g> stormwater from urban centres (including associated road and railway rights-<str<strong>on</strong>g>of</str<strong>on</strong>g>way)can represent an important n<strong>on</strong>-point source <str<strong>on</strong>g>of</str<strong>on</strong>g> c<strong>on</strong>taminants to receiving watersystems. The locati<strong>on</strong>s <str<strong>on</strong>g>of</str<strong>on</strong>g> municipal developments in the <strong>Fraser</strong> <strong>River</strong> Basin are shown inFigure 3.19. While the nature <str<strong>on</strong>g>of</str<strong>on</strong>g> the substances that are released to surface waters is afuncti<strong>on</strong> <str<strong>on</strong>g>of</str<strong>on</strong>g> land use activities in the area (Table 3.22), the c<strong>on</strong>taminants that arecomm<strong>on</strong>ly associated with such run<str<strong>on</strong>g>of</str<strong>on</strong>g>f include road salts, metals, PAHs, oil and grease,38

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