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Dames & Moore, 1999 - USDA Forest Service

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curve developed for RC-4 was used to estimate flows from the continuous water level recorder (known as<br />

a "Troll") to create a continuous hydrograph for this station. The rating curve data was also used to<br />

estimate concurrent flows at all stations enabling direct flow comparisons and relationships between<br />

stations to be developed.<br />

All of the discharge measurements that were made at RC-2 and RC-4 were used to develop the ratings.<br />

unless a concurrent stage measurement was not available. Additionally, flow measurements that deviated<br />

by more than 20 percent from the average rating curve were excluded from the rating because these<br />

measurements were assumed to represent either unacceptable measurement error or a changed condition<br />

which did not persist in the remainder of the data base.<br />

Three flow measurements were excluded based on this criteria, including the June 16. 1997, measurement<br />

at RC-4, and the July 10, 1997, measurement at RC-2 collected by <strong>Dames</strong> & <strong>Moore</strong> and the July 25,<br />

1996, measurement at RC-2 collected by the USFS; additional discussion regarding the excluded flow<br />

measurements and their significance is presented in Section 4.3. The other findings of the streamflow<br />

surveys are also presented in Section 4.3.<br />

3.2.2 Water Quality Sampling<br />

Referring to Figure 3.2- 1 and 3.2-2, Table 3.0- 1 under "Surface Water," and Tables 3.2- 1 through 3.2-5,<br />

surface water samples were collected from Railroad Creek during the four sampling events in 1997 and<br />

one event in May 1998, from Copper Creek at stations CC-I (south and upstream of the tailings piles),<br />

CC-2 (near the confluence with Railroad Creek) during four sampling events, and from CC-Dl (the<br />

Copper Creek diversion) during the five sampling events. Samples were also collected during four<br />

sampling rounds from two stations in the 1500-level main mine portal drainage, P-l and P-5.<br />

Miscellaneous surface water samples were collected in select Railroad Creek tributaries and at all aquatic<br />

habitat sampling locations (except RC-9).<br />

Surface water quality samples were collected using a Teflon depth integrated sampler, which collects<br />

samples of the complete water column. .The sampler was slowly lowered to the bottom of the stream<br />

allowing a constant inflow rate through the water column. The samples were also composited across the<br />

width of the stream by sampling at evenly spaced locations across the channel, and combining these<br />

discrete samples into one composite for the station. The depth integrated sampler could only be used<br />

when the water depth was greater than approximately one foot, and consequently could not be used to<br />

sample the portal drainage. For comparative purposes, discrete depth integrated samples were also<br />

collected (in addition to the width composite sample) at south bank locations at stations RC-I, RC-4 and<br />

RC-2.<br />

The surface water samples were tested in the field for pH, specific conductance, temperature, dissolved<br />

oxygen, and redox potential. Laboratory analyses included total and dissolved metals (aluminum, arsenic,<br />

barium, beryllium, cadmium, calcium, chromium, copper, iron, lead, magnesium, manganese, mercury,<br />

molybdenum, nickel, potassium, selenium, silver, sodium, thallium, uranium, and zinc), ortholtotai'<br />

phosphorous, cyanide, total dissolved solids, total suspended solids, chloride, nitrite-nitrate, sulfate,<br />

silicates, alkalinity, color, and hardness as specified in the SAP and QAPP. Tailings pile 1 was reportedly<br />

used historically as a dump area for Howe Sound Company and Holden Village; thus, TPH and PCBs<br />

were analyzed at selected locations upsmam (RC-6), adjacent to (RC-2) and downstream (RC-3) of the<br />

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17693-005019Uuly 19. <strong>1999</strong>;2:07 PM;DRAFT FINAL RI REPORT

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