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Nearshore Habitat Use by Juvenile Chinook Salmon in Lentic ...

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<strong>Ch<strong>in</strong>ook</strong> / 100m .<br />

500<br />

400<br />

300<br />

200<br />

100<br />

0<br />

Beach (8)<br />

Bedrock (3)<br />

Emergent (4)<br />

LWD (5)<br />

Trib mouth (6)<br />

<strong>Ch<strong>in</strong>ook</strong> / m 2 .<br />

1.5<br />

1<br />

0.5<br />

a<br />

b<br />

ab<br />

ab<br />

c<br />

0<br />

Beach (8)<br />

Bedrock (3)<br />

Emergent (4)<br />

LWD (5)<br />

Trib mouth (6)<br />

FIGURE 47.—June nighttime nearshore abundance to 1 m depth (mean ± 2SE; top panel) and shorel<strong>in</strong>e density<br />

(mean ± 2SE; lower panel) of juvenile <strong>Ch<strong>in</strong>ook</strong> salmon <strong>in</strong> Lake Qu<strong>in</strong>ault, 2004. Bars with different letters are<br />

significantly diferent (ANOVA and Fisher’s LSD; P < 0.05). The ANOVA test was not significant for the<br />

nearshore abundance (top panel). Numbers <strong>in</strong> parentheses <strong>in</strong>dicate the number of replicates.<br />

Discussion<br />

Except for tributary mouths, few significant differences were observed <strong>in</strong> the use of<br />

different habitat types <strong>in</strong> Lake Qu<strong>in</strong>ault. Lack of pronounced differences may have been due to<br />

small sample sizes and high variability <strong>in</strong> <strong>Ch<strong>in</strong>ook</strong> salmon abundance between sites. There is<br />

little bedrock shorel<strong>in</strong>e <strong>in</strong> Lake Qu<strong>in</strong>ault and only three bedrock sites were established. The<br />

abundance of <strong>Ch<strong>in</strong>ook</strong> salmon at bedrock sites was substantially lower than other habitat types,<br />

yet we detected few significant differences between bedrock sites and other habitat types.<br />

78

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