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Dames & Moore, 1999 - USDA Forest Service

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In general, concentrations in the upstream stations did not fluctuate with seasonal or stream flow variations.<br />

Iron and hardness were inversely proportional to stream flow. Metal concentrations at the adjacent and<br />

downstream stations were generally higher than the upstream locations. The widest variation occurred in<br />

May. Concentrations were often similar by September. Concentrations for most metals increased<br />

downstream of RC-1 at RC-4. Concentrations fiom RC-4 to RC-2 were similar or slightly decreased with<br />

the exception of iron, which increased substantially at RC-7. Concentrations generally decreased from RC-<br />

2 down to RC-3. Cadmium, copper, iron, and zinc concentrations are plotted from upstream station RC-6 to<br />

downstream station RC-3 on Figures 5.3-10 through 5.3-13. Field measurements for pH, specific<br />

conductance, and dissolved oxygen were similar fiorn upstream to downstream stations in Railroad Creek.<br />

Samples collected fiom the south banks at RC-4 and RC-2 in 1997 were compared to samples collected<br />

across the width of the creek. Concentrations of aluminum, cadmium, copper, manganese, and zinc detected<br />

on the south bank of RC-4 during May 1997 were above concentrations detected across the creek width.<br />

Concentrations in July and September were similar between the bank and creek width samples, with the<br />

exception of copper. Data collected fiom the south bank at RC-2 were similar to data collected fiom the<br />

width of the creek.<br />

The south bank results from RC-4 and RC-2 were compared to state and federal WQC. Metals above WQC<br />

in May, June, and July were generally comparable to the metals above WQC in samples collected across the<br />

creek width. The September 1997 data compared to state WQC indicates that copper and zinc at RC-4 and<br />

zinc at RC-2 are above WQC. The data from RC-4 indicates that copper is also above federal WQC during<br />

this timeframe.<br />

The weekly sampling performed at RC-2 indicated a continued decrease for most metals over time and with<br />

decreasing stream flows.<br />

Copper, cadmium, iron and zinc were identified as PCOCs in surface water in Railroad Creek at the stations<br />

adjacent to and downstream of the Site. Aluminum and manganese concentrations were greater than<br />

background concentrations.at stations adjacent to and downstream of the Site. The highest concentrations of<br />

metals in 1997 correlated with the highest flow in Railroad creek measured in MayIJune 1997. In several<br />

cases, metal concentrations measured in 1998 in stations adjacent and downstream of the Site were higher<br />

than concentrations detected in 1997. The higher concentrations are likely related to the sampling event<br />

occurring nearer the initial hydrograph rise (Section 4.0). Metal concentrations did not exceed MTCA<br />

Method B cleanup levels (for constituents without WQC) at any stations on Railroad Creek.<br />

5.3.4 Portal Drainage<br />

Samples were collected from the 1500-level main portal drainage at two stations, P-1 and P-5. P-1 is<br />

located at the exit of the mine portal and P-5 is located at the confluence with Railroad Creek and,upstream<br />

of RC-4 (Figure 5.3-1 and 5.3-2). The data is summarized in Table 5.3-30. Additionally, one sample (VP-<br />

1) was collected from the 1500-level ventilator portal located west of the portal. Data are summarized on<br />

Table 5.3-30a.<br />

5.3.4.1 Exit of Mine Portal (P-1)<br />

.a Surface water grab samples were collected from the mine drainage at the 1500-level main portal opening (P-<br />

I) during May, July, and September 1997 aid May 1998 to assess the water quality and seasonal variations<br />

\DM-SEA I\VOLI\COMMOMWP\WPDATA\~~~\REPORTSWOLDEN-ZUUU~.~OE 5-3 1 DAMES & MOORE<br />

17693-005-019Uuly 28. <strong>1999</strong>.1 1:09 AMDRAFT FINAL RI REPORT

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