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Mitigation for the Construction and Operation of Libby Dam

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<strong>Libby</strong> Reservoir Gillnet Monitoring<br />

We documented changes in <strong>the</strong> assemblage <strong>of</strong> fish species sampled in <strong>Libby</strong> Reservoir<br />

since impoundment. Kokanee salmon, Kamloops rainbow trout <strong>and</strong> yellow perch did not occur<br />

in <strong>the</strong> Kootenai River prior to impoundment but are now present. Kokanee were released into<br />

<strong>the</strong> reservoir from <strong>the</strong> Kootenay Trout Hatchery in British Columbia (Huston et al. 1984).<br />

Yellow perch may have dispersed into <strong>the</strong> reservoir from Murphy Lake (Huston et al. 1984).<br />

The British Columbia Ministry <strong>of</strong> Environment (BCMOE) first introduced Kamloops rainbow<br />

trout in 1985. Eastern brook trout are not native to <strong>the</strong> Kootenai Drainage, but were present in<br />

<strong>the</strong> river be<strong>for</strong>e impoundment <strong>and</strong> continue to be rarely captured in gillnets within <strong>the</strong> reservoir.<br />

Peamouth <strong>and</strong> nor<strong>the</strong>rn pikeminnow were rare in <strong>the</strong> Kootenai River be<strong>for</strong>e impoundment, but<br />

have increased in abundance in <strong>the</strong> reservoir. Mountain whitefish, rainbow trout, westslope<br />

cutthroat trout <strong>and</strong> redside shiner were common in <strong>the</strong> Kootenai River be<strong>for</strong>e impoundment,<br />

but have decreased in abundance since impoundment.<br />

Kokanee<br />

Since <strong>the</strong> accidental introduction <strong>of</strong> 250,000 fry from <strong>the</strong> Kootenay Trout Hatchery in<br />

British Columbia into <strong>Libby</strong> Reservoir in 1980, kokanee have become <strong>the</strong> second most<br />

abundant fish captured during fall gillnetting. Fluctuations in catch have corresponded to <strong>the</strong><br />

strength <strong>of</strong> various year classes (H<strong>of</strong>fman et al. 2002), <strong>and</strong> have varied by year, with no<br />

apparent continuous trend in abundance (Figure 32). However, kokanee catch in <strong>the</strong> fall net<br />

series follows a general trend <strong>of</strong> decreasing abundance from 1988-1995 <strong>and</strong> an increasing<br />

trend in abundance from 1996-2003 (Figure 32). Average length <strong>of</strong> kokanee has varied<br />

among years. Average length <strong>and</strong> weight between 1988 <strong>and</strong> 2003 was 290.3 mm <strong>and</strong> 235.2 g<br />

respectively (Table 6), while maximum average size occurred in 1992 (350 mm, 411 g).<br />

However, <strong>the</strong> minimum mean length was observed in 2002 (Table 6).<br />

Catch per Net<br />

30<br />

25<br />

20<br />

15<br />

10<br />

5<br />

Spring<br />

r 2 = 0.008<br />

p = 0.739<br />

Fall (1988-1995)<br />

r 2 = 0.44;p = 0.073<br />

Y = 3773 - 1.89*X<br />

Fall (1996-2003)<br />

r 2 = 0.44;p = 0.072<br />

Y = -3964 + 1.99*X<br />

0<br />

1984<br />

1986<br />

1988<br />

1990<br />

1992<br />

1994<br />

1996<br />

1998<br />

2000<br />

2002<br />

Year<br />

Fall Floating Nets<br />

Spring Sinking Nets<br />

Figure 32. Average catch per net <strong>of</strong> kokanee <strong>for</strong> fall floating (1988-2003) <strong>and</strong> spring sinking<br />

(1984-2003) gill nets in <strong>Libby</strong> Reservoir.<br />

91

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