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Dames & Moore, 1999 - USDA Forest Service

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discussed in' Section 6.8.2 of this report. It is possible that during baseflow periods the interaction between<br />

surface water and groundwater is limited for those portions of Railroad Creek adjacent to the tailings piles,<br />

with interaction increasing immediately downstream of tailings pile 3. This is indicated by the apparent<br />

flow loss between RC-2 and RC-5, followed by an apparent gain in Railroad Creek flow measured<br />

approximately 100 feet downstream of RC-5, as discussed above.<br />

Other observations with respect to surface water and groundwater interaction include the relationship<br />

between precipitation and flow rates in Railroad Creek and the 1500-level main portal drainage. Referring<br />

to Figures 4.3-4a and 4.3-7b, both Railroad creek and the portal drainage appear to respond relatively<br />

rapidly (i.e., within approximately one day) to precipitation events that occur during the spring snowrnelt<br />

period. This appears to suggest that the soil and bedrock are saturated during this period of time. However,<br />

as the snowmelt diminishes through the summer months, the response to precipiiation becomes less<br />

pronounced for both the portal drainage and Railroad Creek, likely due to the soil and bedrock becoming<br />

less saturated.<br />

4.3.7.5 Summary of Baseflow Survey<br />

Railroad Creek upstream of the Site appears to be a gaining stream between RC-6 and RC-1 (Figure 4.3-3a).<br />

However, adjacent to the Site, flow gains and losses are variable. It appears that, at least during parts of the<br />

year, flow is lost between upstream stations RC-I and RC-4, and immediately downstream of RC-2. Flow<br />

appears to be gained due to groundwater inflow (subtracting inflow from Copper Creek and the Copper<br />

Creek diversion) between RC-4 and RC-2 during spring. Gains and losses potentially attributed to<br />

groundwater flow are within the accuracy of the measurements during the fall and are, therefore,<br />

inconclusive when considered independent of other site information.<br />

4.3.8 Hydrologic Conditions During the 1998 Wand Comparison With 1997 Rate<br />

During 1998, stream flow measurements were collected in Railroad Creek with a data logger installed at the<br />

RC-4 and portal drainage P-l stations (Figure 4.3-3a). In general, the discharge of Railroad Creek during<br />

the May 1997 sampling appeared higher than the discharge during the May 1998 sampling (compare<br />

Figures 4.3-4 and 4.3-4a). The discharge in the portal drainage was also higher in 1997 than 1998 (compare<br />

Figures 4.3-7 and 4.3-7a).<br />

Based on these data, both the 1997 and 1998 Rl spring runoff water quality samples were apparently<br />

collected on the rising limb or near the peak of the initial hydrograph rise (Figures 4.3-4 and 4.3-4a).<br />

4.3.9 Interstitial Iron-Oxide Precipitate and Ferricrete<br />

4.3.9.1 Summary of Historical Findings<br />

The U.S. Bureau of Mines (USBM) completed an assessment of the Railroad Creek substrate in April 1994.<br />

The assessment included the mapping of the presence or absence of interstitial iron-oxide precipitates and<br />

ferricrete. The methods employed the probing of the substrate as part of the sampling of interstitial fluid<br />

(see Section 5.4.3). The probing did not allow the differentiation between non-cemented and cemented<br />

interstitial iron-oxide precipitates. However, it appeared that the cemented iron-oxide precipitates<br />

(ferricrete) were generally limited to the banks of Railroad Creek near the northeast comer of tailings pile 1<br />

G:\WPDATA\WSWPORTSWOLDEN-2Wd.DOC<br />

17693-005-0 19Wuly 19.<strong>1999</strong>;4:5 1 PM,DRAFT FINAL RI REPORT

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