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Mitigation for the Construction and Operation of Libby Dam

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Burbot per Trap Day<br />

3<br />

2.5<br />

2<br />

1.5<br />

1<br />

0.5<br />

1995-2003<br />

Model<br />

Y = -0.387 + 4.014*X<br />

r 2 = 0.47; p = 0.04<br />

0<br />

0 0.1 0.2 0.3 0.4 0.5 0.6<br />

Catch per Net<br />

Figure 39. The relationship between mean burbot catch per net <strong>for</strong> spring sinking gillnets on<br />

<strong>Libby</strong> Reservoir <strong>and</strong> burbot catch rates (fish/trap day) <strong>of</strong> baited hoop traps in <strong>the</strong> stilling<br />

basin below <strong>Libby</strong> <strong>Dam</strong> 1995-2003.<br />

Total Fish Abundance<br />

The long-term trends in total fish abundance in <strong>the</strong> reservoir reflect <strong>the</strong> changes that<br />

have occurred in <strong>the</strong> reservoir since impoundment. Total catch (fish per net) <strong>for</strong> spring gillnets<br />

has significantly increased since impoundment (Figure 40; r 2 = 0.104; p = 0.09; Table 9) is<br />

indicative <strong>of</strong> an increase in <strong>the</strong> biomass <strong>of</strong> species that prefer reservoir habitats: peamouth<br />

chub, suckers, nor<strong>the</strong>rn pikeminnow, etc. However, <strong>the</strong>re is no significant trend in total catch<br />

(fish per net) <strong>for</strong> fall gillnets (Figure 40; r 2 = 0.003; p = 0.76; Table 10). Species composition<br />

<strong>for</strong> <strong>the</strong> catch <strong>of</strong> fall <strong>and</strong> spring gillnets has remained relatively stable since 1988 (Table 11).<br />

100

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