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Coastal Cutthroat Trout as Sentinels of Lower Mainland Watershed ...

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78It is widely <strong>as</strong>sumed that most adult cutthroat utilizing the lower Fr<strong>as</strong>er River areanadromous, yet sea-run, river-run and lake-run life history strategies could becommon in the Fr<strong>as</strong>er-Harrison and <strong>Lower</strong> Fr<strong>as</strong>er tributaries. It is uncertain froma fish culture perspective whether all fish are anadromous stocks or a mixture <strong>of</strong>river, lacustrine and sea-run stocks, the latter risking “hybridization” amongdifferent life history forms that may be from separate breeding populations. Forexample, Voight and Hayden (1997) concluded that large-sized adult cutthroatmonitored by diving in the mainstem <strong>of</strong> the Smith River, northern California,were a mixture <strong>of</strong> resident, fluvial and sea-run forms. Life history pr<strong>of</strong>iling isrequired with a focus on microchemical analyses <strong>of</strong> marine rare earth elements(strontium, iridium, strontium: calcium ratios) from existing scale collections orfrom new scale, fin ray or otolith collections. Radio/sonic tracking <strong>of</strong> adultcutthroat from several tributaries including Wahleach Slough would also bebeneficial. It is possible that molecular genetic can detect differences in some <strong>of</strong>the discrete populations over the geographic range <strong>of</strong> the Region, but life historyand morphological pr<strong>of</strong>iling is more likely to be most effective in the <strong>Lower</strong>Fr<strong>as</strong>er where the current fish culture program is focused.• Quantify wild-hatchery stock interactions <strong>as</strong>sociated with the anadromouscutthroat program in the <strong>Lower</strong> <strong>Mainland</strong>, particularly in the <strong>Lower</strong> Fr<strong>as</strong>er andits tributaries.While the collapse <strong>of</strong> major cutthroat stocks in Oregon w<strong>as</strong> <strong>as</strong>sociated with poornear-shore marine conditions and land and water quality impacts, the hatcheryprogram w<strong>as</strong> also considered a factor to the degree that the program w<strong>as</strong>terminated in Oregon in 1997 (Hooton 1997). Thus in BC, <strong>as</strong> a pre-emptiveme<strong>as</strong>ure, stock status surveys are required <strong>of</strong> stocked and unstocked tributaries toexamine the ratio <strong>of</strong> wild to hatchery adult cutthroat, <strong>as</strong> well <strong>as</strong> residual hatcherycutthroat and steelhead. Similarly, the incidence <strong>of</strong> undesirable hybridization <strong>of</strong>cutthroat and steelhead needs to be examined via molecular genetic tools, usingunstocked streams <strong>as</strong> controls (Waples 1991).Further, an additional workshop review <strong>of</strong> anadromous cutthroat hatcherypractices is needed to provide guidance on sound me<strong>as</strong>ures to minimize oreliminate hatchery-wild interactions. This should be similar to the Ministry’s1990 genetics workshop (Ludwig 1992), which w<strong>as</strong> largely directed at steelheadtrout culture. The workshop needs to examine the full range <strong>of</strong> hatchery-wildinteractions to provide guidance on:- minimizing cutthroat-steelhead hybridization;- avoiding stock mixtures to minimize genetic homogeneity with loss <strong>of</strong> uniquestock adaptations including migration and timing <strong>of</strong> return or maturity;- mating procedures to minimize inbreeding depression and genetic drift;- avoiding recycling <strong>of</strong> hatchery versus wild brood fish; and- selection <strong>of</strong> broodstock sources and stocking locations.

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