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Dames & Moore, 1999 - USDA Forest Service

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Assessment by Mining Consultant<br />

The Draft RIIFS Work Plan included entry of the mine for sampling of the mine water and precipitates.<br />

and to evaluate the structural integrity of the 1500-level tunnels. The possible mine entries were<br />

determined to be the 1500- and 1100-level portals. However. due to worker safety issues related to<br />

entering the mine, the underground mine maps were evaluated by a mining engineer, J.S. Knowlson &<br />

Associates of Seattle, Washington, subcontracted by <strong>Dames</strong> & <strong>Moore</strong>. The evaluation also included<br />

- additional map review and visits to the relevant portals by a <strong>Dames</strong> & <strong>Moore</strong> geologist and a mining<br />

subcontractor (Atlas Fausett of Kellogg, Idaho). The results of the assessment have been incorporated<br />

into Section 4.1.3.1.<br />

3.7 TASK 7 - WINSTON HOME SITES ASSESSMENT<br />

The Winston home sites area located west of Holden Village (Figures 3.0-3 and 3.1-5) included 103<br />

houses which were demolished by the USFS. Fuel oil stored in both aboveground tanks (ASTs) and<br />

underground storage tanks (USTs) were used to heat the houses. Some of the USTs remain as indicated<br />

by the presence of apparent fill and vent pipes across the area. It is our understanding that the USFS had<br />

not completed an inventory of USTs. Therefore, the scope of work included performing an inventory of<br />

the tanks and a series of trackhoe-excavated test pits as discussed in Section 3.1-3.<br />

The inventory of the USTs was based on the.presence of fill and vent pipes. The locations and types of<br />

fill pipes, as well as the condition of the tanks (if observed) were documented, when possible, on a map of<br />

-, the Site which included the surveyed locations of some of the remaining walls and other surface features<br />

as references. The results of the inventory are presented in Section 4.1.2.6.<br />

3.8 TASK 8 - FIELD SCREENING<br />

Field screening was used extensively across the Site during each of the sampling events. Screening was<br />

performed using a combination of field meters and qualitativelquantitative field chemistry tests.<br />

Temperature, pH, specific conductance, and turbidity were measured and recorded in surface water,<br />

groundwater, and seeps collected during the Phase I Rl.<br />

In addition, oxidation/reduction potential and dissolved oxygen were added in May through July 1997 as<br />

part of the Phase I Rl. During the Phase I RI, a qualitative chemical test for ferrous iron was performed<br />

on groundwater and seep samples to aid in establishing significant changes in site chemistry based on<br />

determination of a reducing or oxidizing environment. The colormetric test included adding a reagent to<br />

a sample of seep and/or groundwater.<br />

In addition to field measurements, field screening for pH and specific conductance was performed at<br />

additional locations based on field observations. These locations were not specified in the SAP, but<br />

included areas where water entered or potentially entered Railroad Creek that may result in a loading<br />

source. Additional samples were collected if the field results indicated that the resulting water w~<br />

affected by mine related activities (low pH andlor high specific conductivity) and/or the flow rate was<br />

substantial. This resulted in several additional seep locations being identified on the Site for sampling<br />

which were not presented in the SAP.<br />

~:\wpdn(.\005\~poru~oldcn~2\ri~-0~d0~ 3-19<br />

17693-005-019Uuly 19, <strong>1999</strong>;2:07 PM;DRAFT FNAL RI REPORT

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