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Dames & Moore, 1999 - USDA Forest Service

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9.2.4.1 Portal Drainage<br />

The chemical loading analyses completed during the RI accounted for the overland flow and<br />

groundwater loading sources of dissolved metals to Railroad Creek.<br />

Conclusions associated with the water quality and chemical loading of component inflow<br />

sources including the portal drainage, groundwater, the waste rock piles, mill building, Copper<br />

Creek diversion and seeps SP-12 and SP-23 are provided below.<br />

Water quality measured at P-1 (main portal)'and P-5 (confluence with Railroad Creek) as overland flow<br />

indicates that metals presented in the following table were above regulatory surface and groundwater quality<br />

regulatory levels.<br />

Surface<br />

Water<br />

Criteria<br />

Groundwater<br />

Criteria<br />

Locations<br />

P- 1<br />

P-5<br />

P-1<br />

, July 1997<br />

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

C4 Cu, Pb. Zn, pH<br />

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

PH<br />

These dissolved metals concentrations are influenced by seasonal changes in groundwater flow discharging<br />

from the main portal. The loading analysis reflects these differences.<br />

MayIJune - The portal drainage discharge flows were as high as approximately 3.5 cubic feet<br />

per second (cfs) in ~a~ 1997 and approximately 1.8 cfs in May 1998, and accounts for more<br />

than 65 percent of the load of dissolved cadmium, copper, and zinc to the creek during the<br />

spring snowmelt period.<br />

OctoberISeptember - Discharge flow rates were measured as low as approximately 0.10 cfs.<br />

The drainage accounts for less than 1 percent of the copper load, and approximately one-third<br />

of the cadmium and zinc load to Railroad Creek.<br />

The portal drainage overland flow represents the primary source of dissolved copper, cadmium and zinc to<br />

Railroad Creek during spring conditions; however during the fall, the concentrations of these metals is<br />

greatly reduced.<br />

9.2.4.2 Groundwater<br />

May 1997<br />

C4 Cu, Pb, Zn, pH<br />

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

As, Be, Cb Cu, Pb, Zn,<br />

SO,, pH<br />

September 1997<br />

Cd, Cu, Zn<br />

cd, zn, pH<br />

Cd, SO4, TDS<br />

The groundwater geochemistry in the east and west portions of the Site is different due to the different source<br />

rock types (mine ore deposit versus tailings) and differences in oxygen availability and water flow.<br />

Groundwater data from monitoring wells and expressed as seeps and springs were used to evaluate<br />

groundwater quality associated with the Site, particularly for the west side of the Site.' Groundwater<br />

underlying the Site is not currently being used as drinking water.<br />

West Portion of the Site<br />

May 1998<br />

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

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

Cd, Cu, Fc. Pb, Zn, SO,,<br />

TDS, pH<br />

The west portion of the site includes the following source areas: underground mine and Honeymoon Heights,<br />

portal drainage, west waste rock piles, and the mill building. Groundwater monitoring wells are not present<br />

in these areas; therefore, seep water quality was used to evaluate groundwater quality exceedances, source<br />

G:\WPDATA\WSWPORTSWO~DM-ZUU\~-O~~~~~ 9-4<br />

17693-00S-019Uuly 28. <strong>1999</strong>;10:07 AM;DRAFT FINAL RI REPORT<br />

'<br />

I

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