Service Description: This feature class represents data collected by an EPA in-house team in the Six and Seven-mile Canyons during a 3.5 week period from three mill sites with associated tailings piles located between Virginia City and Mark Twain using the Incremental Sampling Method (ISM). The EPA published this data in support of the Carson River Mercury NPL Site in Nevada as part of the ongoing OU1 soil characterization and conceptual site model (CSM) validation effort under the Long-term Sampling and Response Plan (LTSRP).
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Description: The current conceptual site model (CSM) includes data gaps related to the extent of mercury contamination throughout the site, as well as the presence of other metal contaminants in soil. This study focuses on three areas in OU01: the Six Mile Canyon Area in Dayton, NV, the California Pan Mill Area in Virginia City, NV, and the Sacramento Mill Area just north of Virginia City, NV. Surface and near surface soils with COC concentration greater than the project action limits present a potential risk for direct contact and soil migration. Data gaps exist in the understanding the sources, extent, and migration pathways of contaminants at this area and the applicability of the Incremental Sampling (IS) and (X-ray Fluorescence (XRF) approach to comply with the LTSRP. The project will address these data gaps through incremental sampling and real time XRF.
Data was compiled and evaluated for the IS Study where field sample collection techniques were evaluated as part of this study using XRF. Sample processing included seiving, to compare ISM with the current LTSRP method based on four five-point composite samples per residential parcel. The goal to is to validate the CSM and improve the screening of vast areas of mercury-contaminated soils while continuing to evaluate the performance of X-ray fluorescence (XRF) instrumentation for the simultaneous analysis of mercury (Hg), lead (Pb) and arsenic (As) in soil affected by the mining operations associated with the Comstock Lode. however sample processing will be. The most effective processing and analytical techniques will be selected for use in a follow-up study which will evaluate field sample collection. It is anticipated that the most effective and efficient sampling and analysis techniques will be incorporated into future investigations for the Carson River area.
General Comments: The location coordinates represent the center point of the Decision Unit (DU) as calculated by GIS. For DUs that cross roads or driveways (SMCD2 and SMCSCR-South) the midpoint may plot in the middle of the road. The center point for SMCCBS was selected manually due to the unusual shape of the DU. The calculated GIS center point falls outside of the DU. DU columns provided on each tab for easy sorting and QC check. It is not a critical data point since the DU name is embedded in the Sample ID. For Source Units (SU) samples, the DU column is N/A if the SU was located outside of a DU, this column is filled out if the SU was located inside of a DU. Date represents sample collection date.
Tab-Specific Comments: XRF field results did not use unique Lab ID sample #s so left that column blank. Did not establish specific XRF reporting limits for this project. Manually added a “U” for the XRF ND samples to match the lab formats. Region 9 lab results for the XRF comparison samples: Left all the ICP metals in the database. R9 lab DMA data only reported Pb, As, Se, and Hg per the team decision. SPLP Extraction #2 results for the samples selected for leaching analysis - removed the rows that identify the extraction procedure and contained no lab data. SPLP Extraction #3 results for the samples selected for leaching analysis - removed the rows that identify the extraction procedure and contained no lab data. Notes column indicates this is DI water extraction.
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Copyright Text: U.S. EPA
Spatial Reference: 102100 (3857)
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