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Dames & Moore, 1999 - USDA Forest Service

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The banks are relatively nonvegetated, possibly as the result of human encroachment from the road (bridge)<br />

that crosses the upstream end of the location and the general increase in human activities associated with the<br />

USFS campgrounds nearby and the Lucerne boat dock. A mine adit is present approximately one-quarter<br />

mile upstream of the sampling station.<br />

Reference streams selected outside the Railroad Creek drainage were for the most part undisturbed, with the<br />

exception of Company Creek which is immediately downstream from the' Chelan Public Utilities District<br />

hydropower outfall and included a road crossing (Bridge). Bridge Creek and South Fork Agnes Creek were<br />

located within wilderness areas and, as such, receive minimal human impact. Human access to both creeks<br />

is attainable only by the Pacific Crest Trail.<br />

Based on the habitat analysis results, BC-1 had the best overall habitat. The only parameter noticeably<br />

suppressed at the Bridge Creek location was the "width to depth ratio." Unlike any of the other stations,<br />

approximately 25 percent of the Bridge Creek location consists of a single pool of five to six feet maximum<br />

depth which provide excellent trout cover and holding habitat for feeding. The remainder of the location is<br />

relatively wide, but consists of numerous large cobbles and boulders which provide relatively good instream<br />

cover for trout.<br />

South Fork Agnes Creek (SFAC-1) provides instream trout cover in the form of scattered cobbles and<br />

boulders and undercut banks and overhanging vegetation. Although the stream is relatively wide at this<br />

location, several pockets backwater (downstream from the cobble and boulders) provide good holding<br />

habitat for trout.<br />

Of all the reference locations (Railroad Creek and non-Railroad Creek), the Company Creek location (CoC-<br />

I) exhibits the most influence from human activity. As previously mentioned, CoC-I is located downstream<br />

from the outfall of a hydropower plant. .CoC- 1 also contains a road crossing (bridge). The stream has high<br />

gradient with numerous large cobble and boulders which provide excellent trout habitat. Vegetation is<br />

nearly nonexistent immediately adjacent to the bank.<br />

4.6.1.3 Benthic Macroinvertebrate Communities<br />

The benthic macroinvertebrate communities within Railroad Creek and the reference streams exhibit a wide<br />

range of conditions. .The benthic macroinvertebrate sampling and analysis procedure originally called'for<br />

six to eight replicates to be analyzed at each location, pending the results of a power analysis on six<br />

randomly selected replicates from each site. However, in an attempt to account for the anticipated<br />

variation at each location all eight replicates were analyzed. The results of sampling eight replicates per<br />

location were applied to six indices, the results of which provide indications of community health or<br />

impairment. The indices evaluated are species richness (diversity), ratio of scrapers to filtering collectors,<br />

ephemeroptera, plecoptera and trichoptera (EPT) and chironomid abundance, percent dominant taxon, EPT<br />

index, and the ratio of shredders to total number of individuals collected. In addition to these indices, total<br />

number of organisms per square meter were determined as an indication of productivity at each sampling<br />

location. The results of these evaluations are presented in Tables 4.6-2a and b. The results are presented as<br />

means for all eight replicates at a given-location. A listing of taxa and number. of individuals for each<br />

replicate at each location is presented in Appendix 0.<br />

G.\WPDATA\OO5REPORTSWOLDR.(-ZUUCzd,WC<br />

17693-005-019Uuly 19. <strong>1999</strong>:4:51 PM;DRAFT FINAL R1 REPORT

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