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Dames & Moore, 1999 - USDA Forest Service

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MINTEQA2 indicates that the seep waters are saturated with respect to basic aluminum sulfate, alunite,<br />

barite, and goethite. Copper concentrations are low in both cases, hence, copper concentrations do not<br />

appear to be in equilibrium with any copper minerals. Analyses of ferricrete (formed by the precipitation<br />

of iron oxyhydroxides such as goethite) have indicated copper concentrations up to 2,340 m@g. Copper<br />

is expected to co-precipitate with goethite. The seeps tend to contain more zinc than copper but ferricrete<br />

proportionately contains much less zinc than copper. Copper tends to attenuate as groundwater<br />

containing ferrous iron is oxidized and goethite precipitates. Zinc attenuates to a lesser degree.<br />

Tailings Piles 2 and 3<br />

Mechanisms in the tailings pile 2 and 3 are identical to tailings pile 1. The seeps are geochemically<br />

identical except that seeps SP-3, SP-4 and SP-5 are more dilute than SP-1 and SP-2. This is attributed to<br />

partial mixing of Railroad Creek groundwater with seepage from the tailings pile and longer contact paths<br />

with neutralizing materials. The fate of the seeps is the same as seeps SP- 1 and SP-2 from tailings pile 1.<br />

6.6 RAILROAD CREEK<br />

6.6.1 Surface Water Loading Analysis<br />

6.6.1.1 Introduction<br />

Dissolved metals enter Railroad Creek as seep flow, drainage flow and groundwater baseflow.<br />

A chemical and flow mass balance analysis was performed for reaches of Railroad Creek that receive mine<br />

drainage and reaches located upstream and downstream of mine influences. The purpose of the mass<br />

balance was to:<br />

(1)<br />

(2)<br />

(3)<br />

(4)<br />

assess metal contribution in drainage water from point sources measured during the RI in<br />

relation to metal concentrations in Railroad ~ &ek upstream of mine influences<br />

determine the point source discharges that contribute the highest metal concentrations to<br />

Railroad Creek<br />

assess if specific reaches within Railroad Creek contain non-point-source.or "unaccounted"<br />

(assumed to be baseflow) metal load, and<br />

evaluate the chemical loading analyses in relation to the water balance of select reaches of<br />

Railroad Creek<br />

Flow and metal co'ncentrations of seeps and drainages were measured during the FU to assess contribution of<br />

these inputs to Railroad Creek during the May and September 1997 sampling rounds. Flow and water<br />

quality measurements in Railroad Creek were repeated at selected stations in late ApriVMay 1998.<br />

The effects of seep, drainage and groundwater inputs to the surface water quality of Railroad Creek are<br />

observed by the changes in seasonal water quality conditions in a downstream direction. Dissolved metals<br />

entering Railroad Creek in groundwater, seepage flow and flow from the 1500-level main portal drainage<br />

and other drainages attenuate within Railroad Creek by dilution, acid buffering and adsorption reactions in<br />

\U)M-SMI\VOLI\COMMOMWP\~W)~\hoLdm-Z\n7M).dos<br />

6-39<br />

17693-005-01 9Uuly 27.<strong>1999</strong>,4: 1 1 PM;DRAFT FINAL Rl REPORT

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