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Dames & Moore, 1999 - USDA Forest Service

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Reference Reaches - Upstream Railroad Creek<br />

RC-1. and RC-6 as References for. RC-9 and RC-7<br />

Control areas or reference reach segments of Railroad Creek were selected in order to evaluate the aquatic<br />

biota data collected from the segments of Railroad Creek adjacent to and downstream of the site. The<br />

selection process was based on ten primary factors, including channel slope, valley width, watershed area<br />

size, presence of glaciers, presence of lakes, dominant geology, elevation, drainage network, aspect, and<br />

presence of downstream fish barriers. Based on these criteria, it was discovered that the pool of candidate<br />

reference streams were situated both upstream of the site within the Railroad Creek watershed and in the<br />

North Lake Chelan Basin, north of the Railroad Creek watershed.<br />

It appears that the stream and habitat conditions observed at the RC-6 and RC-1 sampling stations are<br />

generally similar to those observed at the RC-9 and RC-7 stations in Railroad Creek, and are, therefore,<br />

considered appropriate control or reference reaches. Benthic macroinvertebrate communities appear<br />

suppressed within the reach of Railroad Creek that extends adjacent to tailings piles 1, 2, 3, compared to<br />

the reference stations based on the 1997 aquatic sampling results. While the density of benthic<br />

macroinvertebrates at station RC-7 indicates an affected community, it should be noted that the RC-9<br />

sampling station includes an apparent transition into the influence of tailings pile seepage originating near<br />

the south bank of the sampling station. The downstream portion of the station has obvious indication of<br />

staining fiom the tailings pile seeps, while the upstream portion is relatively free of any staining or<br />

flocculent-like material on the substrate. Of the eight benthic macroinvertebrate samples collected at this<br />

station, four were collected either upstream fiom the initial staining or near the north bank, while the<br />

remaining four were collected within the staining or along the south bank. The density of benthic<br />

macroinvertebrates within the samples collected upstream or along the north bank ranged from 260 to<br />

1,s 10 organisms per m2, while the density of benthic macroinvertebrates within the staining or along the<br />

south bank ranged from 10 to 300 organisms per m2. The benthic macroinvertebrate results indicate that<br />

the communities may be similar to the reference communities, while those immediately downstream of<br />

the flocculent are reduced compared to the reference stations.<br />

The 1997 fish survey results at RC-9 and RC-7 varied widely between the two stations (RC-9, 114<br />

trouthectare and RC-7, 10 trouthectare); however, the density of trout at RC-9 was within the range of<br />

the reference trout densities (64-93 troutfhectare). As indicated by the habitat evaluation scores, station<br />

RC-9 had the least desirable habitat (score 77) of all stations sampled, while RC-7 had the third lowest<br />

score (94). The reference stations for the reach, RC-6 and RC- 1 scored 1 1 1 and 105, respectively.<br />

Water quality samples were not collected at RC-9 during the 1997 investigation. The results of samples<br />

collected from RC-7 indicate exceedances of water quality criteria for acute toxicity during April (zinc),<br />

May (cadmium, copper, and zinc), and July (copper and zinc). Based on the benthic macroinvertebrate<br />

sampling results from RC-9, the physical conditions of the substrate within these stations may also<br />

adversely influence these communities. Comparison of the individual benthic macroinvertebrate and fish<br />

sampling results with the iron-stained and non-iron stained portions of RC-9 indicate that the occurrence<br />

of iron flocculent within a portion of the reach has a greater influence on fish and macroinvertebrate<br />

populations than dissolved metal concentrations.<br />

\U)M~SEAI\VOLI\COMMOMWP\WPDATA\~~~WPORTSWOLDEN-ZWUI-O.~OC<br />

8-22<br />

17693-005-019Uuly 28. <strong>1999</strong>;10:24 AM;DRAFT FINAL RI REPORT

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