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Dames & Moore, 1999 - USDA Forest Service

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5.4.4 Groundwater Summary<br />

Groundwater samples were collected from monitoring wells located in Holden Village. west of Holden<br />

Village near the baseball field, on the Site downgradient of the maintenance yard, in tailings piles 1, 2,<br />

and 3, east of tailings pile 3, and from a single well located at Lucerne. Samples were also collected from<br />

lysimeters completed within tailings piles 1 and 3. Seep samples were included as part of the<br />

groundwater quality assessment based on the apparent relationship to underground water sources.<br />

Samples were collected from seeps located on the Site and on the banks of Railroad Creek upgradient,<br />

adjacent to, and downgradient of the Holden Mine.<br />

Samples were collected during sampling events in the spring, summer, and fall of 1997. The samples<br />

were analyzed for dissolved metals, conventional parameters, and field parameters as outlined in the<br />

SAPS and QAPPs. Select groundwater and seep samples were analyzed for organic constituents (PCBs '<br />

and TPH).<br />

The data collected from monitoring wells and seeps were compared to MTCA cleanup levels and WAC<br />

173-200 to assess PCOCs. The sample collected at Lucerne was also compared to federal MCLs as the<br />

water from this well is a current drinking water source for the Lucerne community. PCOCs were<br />

identified if metal concentrations were above MTCA cleanup levels, outside of WAC 173-200 criteria, or<br />

above MCLs. Data collected at SP-21 were compared to surface water quality criteria rather than<br />

groundwater criteria as this location is available to support aquatic life. Arsenic, beryllium, cadmium,<br />

copper, iron, lead, manganese, and zinc were identified as PCOCs at one or more monitoring well<br />

locations. Arsenic, beryllium, cadmium, copper, iron, manganese, and zinc were above groundwater<br />

criteria at various seeps in the west and east portions of the site. Additionally, pH, sulfate, and total<br />

dissolved solids were commonly assessed as PCOCs at both monitoring well and seep locations. The<br />

PCOCs at seeps were generally similar to PCOCs identified in monitoring wells in the same geographic<br />

areas. Cadmium, copper, and zinc were identified as PCOCs at SP-21. A summary of PCOCs by<br />

individual sample location is provided at the end of each subsection in Section 5.4.2. A general summary<br />

of PCOCs is tabulated in Table 5.4-7.<br />

The primary potential concern regarding seeps at the Site and in the Site area is the relation to surface<br />

water quality in Railroad Creek. Aluminum, cadmium, copper,'iron, manganese, and zinc concentrations<br />

were evaluated at each seep location. Additionally, the relationship of seeps within each geographical<br />

area as designated in Section 4.0 were discussed based on metal results. The relationship of the seeps to<br />

surface water quality is discussed in Section 6.0 as part of the fate and transport discussion.<br />

Lysimeter data were compared to monitoring well data at each location sampled. These data were not<br />

used to assess PCOCs. .<br />

5.5 SEDIMENT<br />

5.5.1 Railroad Creek<br />

Sediment in Railroad Creek consists primarily of large grain size, including boulder, cobble and large<br />

gravel. Previous evaluations of sediment grain size completed by PNL (1 992) upstream and adjacent to the<br />

Site indicate that the cobble and boulder fraction of streambed sediment is on the order of 90%. PNL (1992)<br />

further reports that the boulderlcobble fraction diminishes to 70% downstream of the Site (and upstream of<br />

\KIM-SEA I\VOLI\COMMOMWP\WDATA\005WPORTS\HOLDW-2W-O.do~ 5-5 5 DAMES & MOORE<br />

17693-005-019Uuly 28,<strong>1999</strong>;11:09 AM;DRAFT FINAL RI REPORT

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