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

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TABLE 9.—Diet composition of juvenile <strong>Ch<strong>in</strong>ook</strong> salmon at three locations (one shorel<strong>in</strong>e site and two<br />

sites at the mouths of tributaries) <strong>in</strong> south Lake Sammamish, April 16 to 21, 2003. n = the number of<br />

stomach samples analyzed; the range of <strong>Ch<strong>in</strong>ook</strong> salmon lengths is also given; %N = percent number; %O<br />

= percent occurrence (%); %W = percent weight; %IRI = percent <strong>in</strong>dex of relative importance.<br />

Lake shorel<strong>in</strong>e Laugh<strong>in</strong>g Jacobs Cr. Tibbetts Cr.<br />

n = 10, range = 60-85 mm FL n = 10, range = 52-80 mm FL n = 11, range = 53-74 mm FL<br />

Prey group %N %O %W %IRI %N %O %W %IRI %N %O %W %IRI<br />

Insecta<br />

Diptera<br />

Chironomid pupae and adults 69.7 90 67.1 81.3 65.8 100 76.5 81.6 48.9 100 56.3 70.6<br />

Chironomid larvae 4.1 50 0.9 1.6 4.8 100 3.1 4.5 19.1 63.6 2.7 9.3<br />

Other aquatic diptera 0 0 0 0 0.1 10 0.02 0.01 2.1 18.2 0.2 0.3<br />

Ephemeroptera 0.1 10 0.2 0.02 0 0 0 0 8.5 45.5 8.0 5.0<br />

Collembola 0.4 20 0.1 0.1 0 0 0 0 0 0 0 0<br />

Other aquatic <strong>in</strong>sects 0 0 0 0 0 0 0 0 3.2 18.2 5.4 1.0<br />

Homoptera (Aphididae) 0 0 0 0 0 0 0 0 0 0 0 0<br />

Other terrestrial <strong>in</strong>sects 0 0 0 0 0.2 20 0.1 0.03 4.3 36.4 10.8 3.7<br />

Crustacea<br />

Cladocera - Daphnia 16.6 40 19.3 9.5 27.2 50 8.2 10.1 1.1 9.1 0.04 0.1<br />

Other crustaceans 5.5 40 0.7 1.6 0.4 20 0.6 0.1 0 0 0 0<br />

Hydrachnida 2.5 50 0.1 0.9 1.1 30 0.2 0.2 3.2 18.2 0.1 0.4<br />

Oligochaeta 0.3 10 0.01 0.02 0 0 0 0 0 0 0 0<br />

Other 0.8 60 11.7 4.9 0.4 50 11.3 3.4 9.6 54.5 16.6 9.6<br />

In 2004, two tributaries, May Creek and Taylor Creek, were surveyed under high<br />

streamflow conditions as well as base streamflow conditions. Dur<strong>in</strong>g high streamflow<br />

conditions at May Creek, the percent of the diet of chironomids pupae and adults<br />

decreased from base flow conditions, while the percent of chironomid larvae,<br />

oligochaetes, and mayflies <strong>in</strong>creased (Table 10). The diet at May Creek dur<strong>in</strong>g high flow<br />

conditions also <strong>in</strong>cluded some prey items that are usually only found <strong>in</strong> flow<strong>in</strong>g waters.<br />

These prey items <strong>in</strong>cluded the immature stages of rhyacophilid caddisflies, black flies<br />

(Simuliidae), and heptagenid mayflies. Diet breadth was approximately 60% higher than<br />

at the lakeshore and base flow condition (Table 8); however, the diet overlap <strong>in</strong>dex was<br />

not significantly different (lakeshore, 0.69; base flow, 0.67). Cutthroat trout (n = 9) at the<br />

mouth of May Creek dur<strong>in</strong>g the high flow event were forag<strong>in</strong>g primarily on terrestrial<br />

prey items, which <strong>in</strong>cluded terrestrial isopods or sow bugs (36% <strong>by</strong> weight), oligochaetes<br />

(28%) and <strong>in</strong>sects (4%).<br />

Several larval longf<strong>in</strong> smelt (Spir<strong>in</strong>chus thaleichthys) were consumed <strong>by</strong> <strong>Ch<strong>in</strong>ook</strong><br />

salmon at the mouth of May Creek on April 1 (baseflow conditions), which represented<br />

8% of the diet <strong>by</strong> weight. Much of the consumption of larval smelt was observed <strong>in</strong> one<br />

<strong>in</strong>dividual (64 mm FL), which had consumed 29 smelt. Adult longf<strong>in</strong> smelt have been<br />

documented to spawn <strong>in</strong> May Creek (Moulton 1974; Martz et al. 1996).<br />

49

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