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Dames & Moore, 1999 - USDA Forest Service

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apparent lack of aquatic toxicity at RC-5a suggests that this reduction is more attributed tot he physical<br />

presence of flocculent.<br />

Fish survey results indicate reduced numbers at RC-5a (20 troutha)) compared to the reference densities<br />

of 59 and 384 troutlha. However, trout density at RC-10 (92 troutha) was greater than the density<br />

estimated for South Fork Agnes Creek (59 troutha). Additionally, four O+ year class trout (typically the<br />

life stage most sensitive to metals toxicity) were collected at RC-I0 which may reflect the lack of water<br />

quality criteria exceedances. Habitat evaluation scores were slightly higher at the reference stations.<br />

Reference stations BC-I and SFAC-I scored the highest of all aquatic sampling stations at 120 and 113,<br />

respectively. The onsite stations RC-5a and RC-10 scored slightly higher than the median score for all<br />

stations at 1 10 and 108, respectively.<br />

Comoanv Creek as a Reference for RC-3<br />

The RC-3 station at the mouth of Railroad Creek was also discovered to be unique relative to the Railroad<br />

Creek upstream reference stations (RC-6 and RC-I), primarily with respect to gradient (channel slope),<br />

watershed area size, elevation, and its proximity to Lake Chelan (inhabited by a naturally reproducing<br />

population of kokanee salmon). The only site, within the pool of candidate reference sites, remotely<br />

similar to RC-3 was a site on lower Company Creek. This lower Company Creek site was initially<br />

eliminated from the pool of reference sites because only five of the ten parameters were considered<br />

comparable to the RC-3 site. However, because no other site was considered more comparable to RC-3 it<br />

was subsequently decided that aquatic data would be collected at the lower Company Creek site and<br />

analyzed for possible use.<br />

The Company Creek station was situated immediately downstream of the Chelan County PUD hydroelectric<br />

plant, and immediately upstream of the confluence of the Stehekin River, which is a spawning ground for<br />

Kokanee salmon. The average total number of benthic macroinvertebrates collected in the eight replicate<br />

samples was 1266 per square meter. The actual values in the replicate samples ranged from 670 per square<br />

meter to 2950 per square meter. The total calculated number of fish caught at the Bridge Creek site was 571<br />

per hectare, predominantly rainbow trout. The fish length ranged From approximately 10 to 250 millimeters.<br />

Kokanee salmon were observed but not caught due to the sampling taking place during the spawning period.<br />

Based on the comparison with only one reference station, RC-3 appears to have reduced benthic<br />

macroinvertebrate densities. However, the Company Creek reference station was selected primarily to<br />

reflect conditions of a stream that was or could be frequented by spawning kokanee. As such,<br />

comparisons with the combined reference stations (non-Railroad Creek) provide a better indication of the<br />

benthic macroinvertebrate community conditions expected in lower Railroad Creek. Comparing the<br />

benthic macroinvertebrate results from RC-3 with the average densities of CC- I, BC- 1, and SFAC-I<br />

indicates a reduction of approximately 34%. Water quality criteria were exceeded during April and May,<br />

leaving relatively suitable conditions during the summer and fall months for colonization of benthic<br />

macroinvertebrates.<br />

Fish survey results at RC-3 indicated reduced trout density compared to the reference station (CC-I).<br />

RC-3 densities were approximately 25% lower than those estimated for CC- 1. The habitat evaluation<br />

score at RC-3 was 93, the second lowest score of all aquatic sampling stations, compared to a score of<br />

108 for CC- 1 indicating possibly less desirable habitat than CC- 1. Surface water samples collected at RC-<br />

\\DM-SEAI\VOLI\COMMOMWP\WPDATA\OO~WPORTSW~LDEN-~.~<br />

8-24<br />

17693-005-OI9Uuly 28, <strong>1999</strong>;10:24 AM;DRAFT FINAL RJ REPORT<br />

DAMES & MOORE

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