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Dames & Moore, 1999 - USDA Forest Service

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of water exiting from the portal. Samples were submitted for total recoverable and dissolved metals<br />

analyses and conventional parameters. Field measurements (pH, specific conductivity, temperature.<br />

oxidation/reduction potential, and ferrous iron) were collected and recorded in the field.<br />

The data at P-1 were compared to WQC and for those metals where WQC is not available, to surface water<br />

background and MTCA Method B cleanup levels for surface water. Additionally, as the water exiting the<br />

portal is indicative of groundwater from the bedrock aquifer, the data were compared to the Washington<br />

State groundwater criteria as provided in WAC 173-200 and under MTCA Method B cleanup levels for<br />

groundwater. The following PCOCs were identified at P- 1.<br />

b<br />

Regulatory<br />

Guidance<br />

Surface Water<br />

Criteria<br />

Groundwater<br />

Criteria<br />

May 1997<br />

Cd, Cy Pb, Zn, pH<br />

As. Be, Cd, Cu, Pb, Zn,<br />

Sod, pH<br />

May 1998<br />

Cd. Cu, Pb. Zn, pH<br />

Cd, Cu. Fe. Pb, Zn,<br />

Sod, TDS, pH<br />

Dissolved aluminum, barium, thallium, and uranium concentrations are above surface water background<br />

in May. Aluminum and barium continue to exceed background concentrations in July. Manganese is<br />

above background from May to September. Concentrations were not above available MTCA Method B<br />

levels. Cadmium, copper, and zinc consistently are above surface water WQC in May. Lead is above<br />

WQC in May and July.<br />

The PCOCs identified based on groundwater criteria are similar to those identified for surface water.<br />

Cadmium, copper, and zinc are above criteria in May and July. Arsenic and beryllium indicate a single<br />

exceedance in May 1997. Sulfate is consistently above criteria from May through September. Cadmium<br />

is the only metal that is above criteria in September.<br />

Concentrations of dissolved aluminum, cadmium, copper, iron, lead, manganese, and zinc decreased from<br />

May to September 1997. Dissolved cation concentrations (calcium, potassium and sodium) increased<br />

during the same timeframe. Field measurements indicated that pH values changed from acidic (4.8 SU)<br />

in May to neutral (7.0 SU) in September.<br />

Increased concentrations of dissolved aluminum, cadmium, copper, iron, manganese, and zinc were<br />

detected in the sample collected in May 1998 as compared to May 1997 data. The increased<br />

concentrations are likely related to the timing of the sampling event and position on the hydrograph.<br />

Stream flow measurements were similar for each of the sampling events in 1997 and 1998 with flows of<br />

2.63 cfs in 1997 and 2.54 cfs in 1998.<br />

5.3.4.2 Confluence with Railroad Creek (P-5)<br />

July 1997<br />

Cd, Cy Pb, Zn, pH<br />

Cd. Cu, Pb, Zn, SO4,<br />

PH<br />

Grab samples were collected from the 1500-level main portal drainage prior to the confluence with Railroad<br />

Creek at location P-5 during MayIJune, July, and September 1997 and in May 1998 to evaluate source<br />

loading and transport to Railroad Creek. Samples were also collected weekly from May 18, 1997 to June<br />

16, 1997. The samples were submitted for the same suite of analyses as the portal opening (P-I). Field<br />

measurements were also collected. The data,is summarized in Table 5.3-30.<br />

\\DM-SEAI\VOLI\COMMOMWP\WDATAWO5\REPORTSWOLDEN-NUU-O-Od~ 5-32<br />

17693-005-0 19Vuly 28.<strong>1999</strong>; 1 1 :09 AMDRAFT FINAL R1 REPORT<br />

September 1997<br />

Cd, Cu, Zn<br />

Cd, SO4, TDS

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