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

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13accounted for much <strong>of</strong> the variability <strong>of</strong> cutthroat abundance in small coho-cutthroatstreams, using 119 sites from Bella Coola and south (r 2 = 0.55; Rosenfeld et al. 2000).Anadromous <strong>Cutthroat</strong> Only ReachesAnadromous + Resident <strong>Cutthroat</strong> ReachesResident <strong>Cutthroat</strong> Only Reaches700<strong>Cutthroat</strong> <strong>Trout</strong> Biom<strong>as</strong>s g/100 sq m60050040030020010000 1 2 3 4 5 6 7 8Average Summer Wetted Width m9Figure 1. Juvenile cutthroat trout standing crops (total cutthroat biom<strong>as</strong>s per 100 m 2 ) inRegion 2 stream reaches versus wetted summer stream width (adapted from Deleeuw andStuart 1982: widths averaged from 1-2, 2-3, 3-5, 5-8 and 8+ m).Biom<strong>as</strong>s data for rearing co<strong>as</strong>tal cutthroat trout were also plotted by DeLeeuw and Stuart(1982) against average percent stream gradient. This clearly showed that streams <strong>of</strong> zerogradient supported zero rearing cutthroat, and streams near 0 to 0.5 % gradient supportedfew cutthroat. Typically, zero gradient reaches are sloughs or ditches, particularly withinthe lower Fr<strong>as</strong>er Valley. In striking contr<strong>as</strong>t, higher gradients from 0.5 % to >7 %supported high biom<strong>as</strong>ses per unit area (Figure 2). Of note, resident trout reachessupporting higher biom<strong>as</strong>ses per unit area were within the 4-8 m range <strong>of</strong> summer wettedwidths with moderate gradients <strong>of</strong> 2 %, the latter likely <strong>as</strong>sociated with boulderysubstrates and lower competition with sympatric juvenile coho salmon.As for the lentic waters <strong>of</strong> sloughs, ponds and lakes, cutthroat use is related to postglacialaccess, and to availability <strong>of</strong> nursery streams <strong>as</strong> well <strong>as</strong> the quality (cover) andproductivity (food availability) <strong>of</strong> the main water body. Further, some sloughs andditches are frequently only migratory corridors. Velocities can be low, and summer t<strong>of</strong>all conditions (particularly water temperature and/or dissolved oxygen) can be unsuitablein summer (unless groundwater-fed). Conditions may improve in fall to spring (Slaneyand Northcote 2003). For example, although velocities and depths are suitable in somesections <strong>of</strong> Mountain Slough and lower McCallum Ditch near Ag<strong>as</strong>siz, they are

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