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IFinal Baseline Human Health Risk Assessment <br /> San Joaquin Human Services Agency Building <br /> December 2001 <br /> to the EPA and is referenced in this document as Environmental Quality Management (2000) <br /> The spreadsheets and accompanying user's guide were used to perform the indoor air dispersion <br /> modeling and risk-based calculations for the Human Services Agency site A description of the <br /> spreadsheet tools used to model concentrations from groundwater to indoor air are discussed in <br /> more detail below <br />' 3.1 Groundwater to Indoor Air Spreadsheet Tool <br /> The groundwater to indoor air modeling spreadsheet tool consists of a workbook in Microsoft, <br /> Excel The workbook used in this screening-level approach is called GW-ADV XLS The <br /> advanced model for groundwater contamination model was used since site-specific building <br />' parameters vary widely from the residential parameters used in the screening-level model The <br /> advanced model was populated with conservative default factors when model input parameters <br />' were not known, and site-specific factors for key variables such as building volume (width, <br /> length, height), air exchange rates, depth to groundwater, and groundwater temperature (see <br /> 10) Table 2) <br />' 3.2 Approach <br /> Indoor air modeling for current and future workers was conducted using the advanced <br />' groundwater model and site-specific input parameters obtained from regional- and site-specific <br /> sources Parameters and results are discussed in detail below <br /> 3.2.1 Site-Specific Parameters <br />' Groundwater to indoor air modeling and risk calculations were also performed for current and <br /> Ifuture indoor workers using site-specific parameters for both building and soil parameters(where <br /> available) The 90`h percentile concentration for benzene in groundwater (12 9 mg/L from a <br />' combination of MW-2 and MW-2A) was used as the site-specific exposure point concentration <br /> for the J&E screening model Due to the extreme variability across the site and even within the <br />' groundwater monitoring results in MW-2 and MW-2A, the use of the 90'h percentile is very <br /> . conservative These monitoring wells are located near the hot spot of a known fuel tank leak <br />' Monitoring at other locations around the building location have consistently yielded non-detect <br />' San Joaquin County GW Monitoring Report2(Appendix 17)v 2 3 12/27/2001 <br />