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West Clay Properties January 2014 <br /> 639 West Clay Street <br /> Claim No: 8542 <br /> the affected groundwater will be used as a source of drinking water in the foreseeable future. <br /> Other designated beneficial uses of impacted groundwater are not threatened, and it is highly <br /> unlikely that they will be, considering these factors in the context of the site setting. Remaining <br /> petroleum hydrocarbon constituents are limited and stable, and concentrations are decreasing. <br /> Corrective actions have been implemented and additional corrective actions are not necessary. <br /> Any remaining petroleum hydrocarbon constituents do not pose a significant risk to human health, <br /> safety or the environment. <br /> Rationale for Closure under the Policy <br /> • General Criteria: The case meets all eight Policy general criteria. <br /> • Groundwater Risk from Residual Petroleum Hydrocarbons: The case meets Policy <br /> Criterion 1 by Class 2. The contaminant plume that exceeds water quality objectives is less <br /> than 250 feet in length. There is no free product. The nearest water supply well or surface <br /> water body is greater than 11,000 feet from the defined plume boundary. The dissolved <br /> concentration of benzene is less than 3,000 micrograms per liter(Ng/L) and the dissolved <br /> concentration of methyl tert-butyl ether(MTBE) is less than 1,000 pg/L. <br /> • Indoor Vapor Risk from Residual Petroleum Hydrocarbons: The case meets the Policy <br /> Exclusion for Active Station. Soil vapor evaluation is not required because the Site is an <br /> active commercial petroleum fueling facility and the release characteristics do not pose an <br /> unacceptable health risk. <br /> • Direct Contact Risk from Residual Petroleum Hydrocarbons: The case meets Policy <br /> Criterion 3a. Maximum concentrations in soil are less than those in Policy Table 1 for <br /> Commercial/Industrial use, and the concentration limits for a Utility Worker are not <br /> exceeded. There are no soil sample results in the case record for naphthalene. However, <br /> the relative concentration of naphthalene in soil can be conservatively estimated using the <br /> published relative concentrations of naphthalene and benzene in gasoline. Taken from <br /> Potter and Simmons (1998), gasoline mixtures contain approximately 2 percent benzene <br /> and 0.25 percent naphthalene. Therefore, benzene can be directly substituted for <br /> naphthalene concentrations with a safety factor of eight. Benzene concentrations from the <br /> Site are below the naphthalene thresholds in Policy Table 1. Therefore, the estimated <br /> naphthalene concentrations meet the thresholds in Table 1 and the Policy criteria for direct <br /> contact by a factor of eight. It is highly unlikely that naphthalene concentrations in the soil, <br /> if any, exceed the threshold. <br /> Objections to Closure and Responses <br /> According to the Path to Closure page in GeoTracker, the County opposes closure because: <br /> • Conceptual site model is inadequate. <br /> RESPONSE: Adequate data is available in GeoTracker to prepare a conceptual site model <br /> consistent with the Policy. <br /> • Secondary source remains. <br /> RESPONSE: Secondary source as defined by the Policy was removed by excavation in <br /> 2003. <br /> The case does not meet Policy groundwater criteria. <br /> RESPONSE: The case meets Policy Criterion 1 by Class 2. <br /> • The case does not meet Policy indoor vapor criteria. <br /> RESPONSE: The case meets the Policy Exclusion for Active Station. <br /> Page 2 of 14 <br /> i <br />