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• i <br /> David Stavarek, R.G. <br /> June 29, 1998 <br /> Page 3 <br /> deterministic risk assessment. This assumption is consistent with that described in Cal/EPA <br /> (1992) cited in the Workplan. <br /> 3. The Workplan states on page 26 that"there is virtually no evidence of surface soil <br /> contamination" and"Therefore,the fugitive dust pathway . . . will not be evaluated as an <br /> exposure pathway of concern." A number of contaminants have been identified in soil, and <br /> therefore this statement is unsupported. Further, it is unclear from the Workplan how <br /> extensively surface soil has been sampled analyzed for contamination. The fugitive dust <br /> pathway may need to be assessed as an exposure pathway of potential concern. It is <br /> recommended that the contribution to overall risk for a fugitive dust exposure scenario <br /> (inhalation of PMto) be included for on-site workers. <br /> 4. Direct contact with soil. According to the authors, "there are few locations with potential <br /> surficial impacts,"and therefore, "direct exposure pathways (e.g., incidental ingestion, <br /> dermal contact) will be evaluated for these locations only, and will not be.evaluated for the <br /> site as a whole." Exposure scenarios generally assume that exposures occur randomly across <br /> receptors and the location as defined in the Conceptual Site Model. Please describe the <br /> procedure to be used for estimating the exposure dose at the point of contact. Also, in the <br /> text, the word"surficial"is used; the correct word is superficial. <br /> 5. In the HRA,please provide details on the extent of soil and groundwater contamination. <br /> Specifically, provide information on the depth at which soil samples were taken from, and <br /> whether samples were composites. For groundwater, describe whether samples were taken <br /> from a screened well, and at what depth the samples were taken from. In both cases,provide <br /> some basic QA/QC information. <br /> SECTIONS. DATA EVALUATION <br /> 1. Representative values for contaminants in soil and groundwater. According to page 9, the <br /> HRA will be prepared under the PEA Guidance requirements, which requires that"screening <br /> evaluations . . . use . . . the highest concentrations of each contaminant detected on-site to <br /> estimate the site's potential threat" (PEA Guidance,page 2-8). The Workplan proposes the <br /> use of 95%UCL of the mean,which departs from the PEA Guidance recommendation. <br /> Please clearly state the concentration estimate to be used in the HRA, i.e., the maximum for <br /> the deterministic approach, and the distributional values for the probabilistic approach. <br /> 2. On-site risk assessment. Although there may be evidence that off-site groundwater is <br /> contaminated, the risk assessment should not include nor be interpreted as to extending to <br /> off-site locations and/or receptors. This is because there is no sufficient nor appropriate <br /> evidence on contaminants or conceptual (off)site model beyond property bounds. The risk <br />