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Proceedings - Teaching and Learning Centre - Simon Fraser ...

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<strong>Fraser</strong> River Action Plan 3rd Research Workshop<br />

Organochlorine <strong>and</strong> Trace Metal Contaminants in Mink (Mustela vison)<br />

<strong>and</strong> Otter (Lutra canadensis) in the Columbia <strong>and</strong> <strong>Fraser</strong> River Systems —<br />

Progress Report<br />

Introduction<br />

L. Harding, 1 C. Stevens 2 <strong>and</strong> J. Elliott 1<br />

1 Environment Canada<br />

2 Faculty of Medicine, University of British Columbia<br />

Mink (Mustela vison) <strong>and</strong> river otter (Lutra canadensis) are good indicators of contaminant uptake from aquatic<br />

food webs because they are resident, largely piscivorous, <strong>and</strong> at or near the top of the food chain (Moul <strong>and</strong><br />

Nichol, 1994). Mink <strong>and</strong> otter suffer reproductive failure <strong>and</strong> other forms of toxicity at the low parts per million<br />

levels of polychlorinated biphenyls (see reviews by Leonards et al., 1994; Smit et al., 1994 <strong>and</strong> Elliott et al.,<br />

1996). In this study, otter <strong>and</strong> mink were collected during 1995 in the upper <strong>and</strong> lower <strong>Fraser</strong> River <strong>and</strong> the<br />

Kootenay <strong>and</strong> Columbia River systems; in the last, collections were coordinated with those of the U.S. Fish <strong>and</strong><br />

Wildlife Service from the U.S.-Canada border downstream to the mouth of the Columbia. Chemical analysis of<br />

liver tissues was combined with biological measurements <strong>and</strong> pathological examination of various tissues <strong>and</strong><br />

organs. The purpose of this study was to repeat collections of mink <strong>and</strong> otter on these systems that were made in<br />

1991 (Elliott et al., 1996) again during 1995 to determine if there has been a reduction in organochlorine<br />

contaminants following improved regulation of pulp mill effluents in British Columbia.<br />

Methods<br />

Study Design<br />

The sampling design was based on detailed analysis for chlorinated organics of composites of livers from six<br />

to 10 individuals from each species at each location <strong>and</strong> individual analyses of the same specimens for<br />

metals, pesticides <strong>and</strong> total PCBs. Five locations were sampled (see maps): Upper <strong>Fraser</strong>, Lower <strong>Fraser</strong>,<br />

Upper Columbia (above Arrow Lakes), Kootenay system <strong>and</strong> Lower Columbia (below Hugh Keenlyside<br />

Dam). A preliminary sample of six mink was selected in March, 1995 to be analyzed individually to assess<br />

variability.<br />

Collections<br />

With the assistance of regional wildlife biologists of the B.C. Wildlife Branch, specimens were obtained<br />

fresh from registered trappers, tagged, wrapped in aluminum foil, placed in a plastic bag <strong>and</strong> frozen. A<br />

st<strong>and</strong>ard sample collection protocol was distributed to each trapper participating in the program. Each<br />

carcass was tagged with information on the trapper, the specimen, the location <strong>and</strong> the date trapped.<br />

Carcasses were shipped by air freight to Vancouver, or picked up <strong>and</strong> driven directly to the laboratory. As of<br />

February 6, 1996, 32 otter <strong>and</strong> 20 mink had been collected, as well as five marten (Martes americana) as a<br />

terrestrial analogue of the mink. Each specimen was sexed, measured <strong>and</strong> weighed <strong>and</strong> the head removed for<br />

aging by dental cementum annuli.<br />

Analysis<br />

During March, 1995, six mink were taken to the North Vancouver Environment Canada laboratory for<br />

dissection. The liver <strong>and</strong> kidneys were excised from each animal with a stainless steel knife <strong>and</strong> forceps<br />

(washed with hexane between dissections), weighed <strong>and</strong> placed in separate, hexane-washed, heat-treated<br />

jars. Femurs from each were placed in plastic bags <strong>and</strong> archived at -40°C. Kidney samples were submitted<br />

for trace metal analysis by ICP, low level cadmium <strong>and</strong> lead by flameless AA, <strong>and</strong> mercury by AAS. Liver<br />

samples were submitted to Zenon Environmental Laboratories Ltd. for dioxin/furan (low<br />

Page 35

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