Dames & Moore, 1999 - USDA Forest Service

Dames & Moore, 1999 - USDA Forest Service Dames & Moore, 1999 - USDA Forest Service

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Lead was present in the maintenance yard and lagoon area soil at concentrations exceeding MTCA Method A level; however, because no toxicity criteria exist for this constituent, site-specific risks could not be evaluated. While exposure concentrations exceed MTCA Method A and USEPA guidelines for residential sites, the exposure times expected at the site are significantly less than the assumed residential exposure time upon which the guidelines are based. Therefore, concentrations of lead in soil in these two areas are not expected to cause effects in exposed populations. Total petroleum hydrocarbons were present in soil at the maintenance yard and lagoon area at levels exceeding MTCA Method A level. Because no toxicity criteria exist for these complex mixtures. site- specific risks were not evaluated. However, as with lead, exposure times and durations in these areas are expected to be significantly lower than would be assumed for development of the Method A level. and therefore TPH is soil at these locations is not expected to be of concern for the limited time period that maintenance workers and recreational users are exposed populations. In addition, remedial actions in these areas should significantly reduce soil TPH concentrations. 7.1.5.2 Sediment Sediment sample results were divided into four.areas based on physical location, as follows: 1) Railroad Creek adjacent to the Site, 2) Railroad Creek downgradient of the Site, 3) Copper Creek, and 4) Copper Creek diversion. Constituents exceeding screening criteria in the four areas were selected as IHSs and evaluated in the site-specific risk assessment. Cancer risks and noncancer hazard quotients for all IHSs in all exposure areas were below the allowable MTCA cancer risk and hazard quotient. Cancer risks ranged from 1.08 x lv7 for beryllium in all three areas to 4.72 x lo4 for arsenic in Railroad Creek sediments adjacent to the site. The hazard quotients ranged from 6.25 x 10" for beryllium in all four areas to 1.68 x 10" for molybdenum in Railroad Creek sediments adjacent to the site. 7.1.53 Air Based on historical air monitoring data, the only constituent selected as an IHS for air during the screening process was manganese. The site-specific hazard quotient calculated for manganese in air was 4.0 x lV1, which is below the allowable MTCA hazard quotient. There were no cancer risks calculated for this media since the IHS was not a carcinogen. In order to evaluate current conditions and the potential for soiVtailings in each exposure area to be transported to air via fugitive dust emissions, a simple USEPA model was utilized to develop a particulate emission factor (PEF) for each exposure area. Each exposure area was then screened using conservative cleanup criteria calculated from the PEF. Screening of constituent concentrations resulted in the elimination of the vegetable garden, baseball field. wilderness area, maintenance yard, and tailings as areas of concern. Constituents exceeding screening criteria in the remaining three surface soil areas were selected as IHSs and evaluated in the site-specific risk assessment for transfers to air. Cancer risks based on transfers from soil to air for all IHSs in all exposure areas were below the allowable MTCA cancer risk and hazard quotient. Cancer risks ranged from 3.96 x lug for arsenic in the USFS guard station soil (transferred to air) to 5.69 x 1 o4 for chromium in Holden village soil (transferred to air). There were no hazard quotients calculated for this exposure pathway. G:\wpdma\00S~UIoldm2\ni7QQda 17693405419Uuly 27.1999:5:16 PMDRAFT FINAL RI REPORT 7-36 DAMES & MOORE

7.1.5.4 Surface Water and Fish Surface water sample results were divided into three areas based on physical location, as follows: 1) Railroad Creek adjacent to the Site, 2) Railroad Creek downgradient of the Site, and 3) Copper Creek. Screening of constituent concentrations resulted in the elimination of Railroad Creek as an area of concern. Only one constituent (molybdenum) exceeded screening criteria in Copper Creek and was selected as an IHS for surface water and fish. Risks for Copper Creek surface water were evaluated for both incidental ingestion of surface water during recreational activities, and ingestion of fish by sport fishermen. Hazard quotients for molybdenum were 6.44 x 1w2 for ingestion of water and 3.18 x 10" for ingestion of fish. both of which are below the allowable MTCA hazard quotient. There were no cancer risks calculated for this media since the IHS was not a carcinogen. The findings of no significant risk for ingestion of fish is supported by the data collected in 1989/1991 and 1992 by PNL and Ecology. PNL and Ecology collected fish muscle tissue from three locations in Railroad Creek, including at Lucerne, and from 25-Mile Creek (a reference site south of Lucerne). PNL concluded there were no significant overall locational differences in metal concentrations for muscle tissue, and that results indicated little risk to human health through consumption of trout. Screening of this muscle tissue data against U.S. EPA risk-based concentrations confined that residual metals in edible tissues are well below levels of concern, both at the site and downgradient of the site. (287) 7.1.5.5 Seeps, 1500-Level Main Portal Drainage, and 1500-Level Ventilator Portal Seepage Seep, 1500-level main portal drainage and 1500-level ventilator portal seepage data were evaluated separately. No constituents were selected as IHSs for ventilator portal drainage. Constituents exceeding screening criteria in seeps and mine portal drainage were selected as IHSs and evaluated in the site-specific risk assessment. Noncancer hazard quotients for all IHSs in both media were below the allowable MTCA hazard quotient. There were no cancer risks calculated for these media since IHSs were not carcinogens. The hazard quotients ranged from 1.15 x 1 c2 for manganese in the 1500-level main drainage to 5.2 1 x 10" for cadmium in the 1500-level main portal drainage. Lead w& present in both seeps and the 1500-level main portal drainage at concentrations exceeding the MTCA Method A level; however, because no toxicity criteria exist. for this constituent, site-specific risks could not be evaluated. While exposure concentrations exceed MTCA Method A level, the exposure frequencies and water ingestion rates expected at the site are significantly less than those upon which the cleanup criteria is based. Therefore, concentrations of lead in seeps and 1500-level main portal drainage are not expected to cause effects in potentially exposed populations. 7.1.5.6 Sauna Dipping Pool (Copper Creek Diversion) Risks associated with the sauna dipping pool were evaluated by screening water from the Copper Creek diversion against drinking water criteria. No constituents detected in the Copper Creek diversion exceeded screening criteria and therefore this route of exposure was eliminated from further evaluation. 7.1.5.7 Groundwater . Groundwater at the site is not considered useable for drinking water purposes and therefore was not screened for exceedances of drinking water criteria. Groundwater collected at the Lucerne USFS well was G:\~W)~U,aldm-Z\ri\7-O.doc 7-3 7 17693005019Uuly 27. 1999.5:16 PMDRAFT FINAL RI REPORT

7.1.5.4 Surface Water and Fish<br />

Surface water sample results were divided into three areas based on physical location, as follows:<br />

1) Railroad Creek adjacent to the Site, 2) Railroad Creek downgradient of the Site, and 3) Copper Creek.<br />

Screening of constituent concentrations resulted in the elimination of Railroad Creek as an area of concern.<br />

Only one constituent (molybdenum) exceeded screening criteria in Copper Creek and was selected as an<br />

IHS for surface water and fish. Risks for Copper Creek surface water were evaluated for both incidental<br />

ingestion of surface water during recreational activities, and ingestion of fish by sport fishermen. Hazard<br />

quotients for molybdenum were 6.44 x 1w2 for ingestion of water and 3.18 x 10" for ingestion of fish. both<br />

of which are below the allowable MTCA hazard quotient. There were no cancer risks calculated for this<br />

media since the IHS was not a carcinogen.<br />

The findings of no significant risk for ingestion of fish is supported by the data collected in 1989/1991<br />

and 1992 by PNL and Ecology. PNL and Ecology collected fish muscle tissue from three locations in<br />

Railroad Creek, including at Lucerne, and from 25-Mile Creek (a reference site south of Lucerne). PNL<br />

concluded there were no significant overall locational differences in metal concentrations for muscle<br />

tissue, and that results indicated little risk to human health through consumption of trout. Screening of<br />

this muscle tissue data against U.S. EPA risk-based concentrations confined that residual metals in<br />

edible tissues are well below levels of concern, both at the site and downgradient of the site. (287)<br />

7.1.5.5 Seeps, 1500-Level Main Portal Drainage, and 1500-Level Ventilator Portal Seepage<br />

Seep, 1500-level main portal drainage and 1500-level ventilator portal seepage data were evaluated<br />

separately. No constituents were selected as IHSs for ventilator portal drainage. Constituents exceeding<br />

screening criteria in seeps and mine portal drainage were selected as IHSs and evaluated in the site-specific<br />

risk assessment. Noncancer hazard quotients for all IHSs in both media were below the allowable MTCA<br />

hazard quotient. There were no cancer risks calculated for these media since IHSs were not carcinogens.<br />

The hazard quotients ranged from 1.15 x 1 c2 for manganese in the 1500-level main drainage to 5.2 1 x 10"<br />

for cadmium in the 1500-level main portal drainage.<br />

Lead w& present in both seeps and the 1500-level main portal drainage at concentrations exceeding the<br />

MTCA Method A level; however, because no toxicity criteria exist. for this constituent, site-specific risks<br />

could not be evaluated. While exposure concentrations exceed MTCA Method A level, the exposure<br />

frequencies and water ingestion rates expected at the site are significantly less than those upon which the<br />

cleanup criteria is based. Therefore, concentrations of lead in seeps and 1500-level main portal drainage are<br />

not expected to cause effects in potentially exposed populations.<br />

7.1.5.6 Sauna Dipping Pool (Copper Creek Diversion)<br />

Risks associated with the sauna dipping pool were evaluated by screening water from the Copper Creek<br />

diversion against drinking water criteria. No constituents detected in the Copper Creek diversion exceeded<br />

screening criteria and therefore this route of exposure was eliminated from further evaluation.<br />

7.1.5.7 Groundwater<br />

. Groundwater at the site is not considered useable for drinking water purposes and therefore was not<br />

screened for exceedances of drinking water criteria. Groundwater collected at the Lucerne USFS well was<br />

G:\~W)~U,aldm-Z\ri\7-O.doc 7-3 7<br />

17693005019Uuly 27. <strong>1999</strong>.5:16 PMDRAFT FINAL RI REPORT

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