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McDowell&Davis Towing <br /> ` Risk Assessment and Conceptual Site Model <br /> 1) Onsite outdoor inhalation of contaminant vapor sourced from subsurface <br /> -- contaminated soil <br /> 2) Onsite outdoor inhalation of contaminant vapor sourced from contaminated <br /> L groundwater <br /> 3) Offsite outdoor inhalation of contaminant vapor sourced from subsurface <br /> contaminated soil <br /> 4) Offsite outdoor inhalation of contaminant vapor sourced from contaminated <br /> groundwater <br /> 5) Onsite indoor inhalation of contaminant vapor sourced from subsurface <br /> contaminated soil <br /> 6) Onsite indoor inhalation of contaminant vapor sourced from contaminated <br /> groundwater <br /> 7) Offsite ingestion of contaminated groundwater. <br /> 4.0 ASTM - RBCA RISK BASED CORRECTIVE ACTION EVALUATION <br /> The ASTM — RBCA model calculates exposures to selected contaminates based on the <br /> route of exposure and site conditions. Factors included in the model include attenuation <br /> due to vapor or groundwater migration or outdoor exposures, contaminant concentration <br /> due to indoor exposures, and duration of exposure controlled by the use of or proposed <br /> use of the property or location of the identified receptor. Locals used for commercial <br /> purposes will have a lesser daily exposure than residential locals. Model site-specific <br /> parameters are shown in Appendix A. <br /> Lifetime cancer risks are estimated through the calculation of a chronic daily intake and <br /> the determination of the added probability of incurring cancer through long-term <br /> exposures. Acceptable risk levels for exposures to carcinogens have been established at 1 <br /> in 1,000,000 (1.0E-6). System toxicants are evaluated through a hazard quotient, which <br /> compares the calculated chemical intake against an established reference dose. Hazard <br /> quotients greater than 1 indicate possible' non-carcinogenic effects in sensitive <br /> `' populations. <br /> }. Potential risk from exposures to offsite ingestion of contaminated groundwater at'th� <br /> nearest identified water well were calculated as 3.6 E-9, carcinogenic risk for benzene, <br /> 3.3E-5 hazard quotient for ethyl benzene, 7.4E-3 hazard quotient for MTBE, 5.6E-9 <br /> hazard quotient for Toluene, and 8.9-E5 hazard quotient for xylenes. Out run sheets from <br /> the modeling are presented in Appendix <br /> Potential risk from offsite outdoor air residential exposures to contaminated vapors from <br /> subsurface soil and contaminated groundwater were calculated as 6.5 E-9, carcinogenic <br /> risk/3.1E-4 hazard quotient for benzene, 3.1E-4 hazard quotient for ethyl benzene, 6.2E- <br /> �, 5 hazard quotient for MTBE, 6.4E-4 hazard quotient for Toluene, and 1.2E-3 hazard <br /> quotient for xylenes. <br /> Potential risk from onsite outdoor air commercial exposures to contaminated vapors from <br /> subsurface soil and contaminated groundwater were calculated as 4.75 E-9, carcinogenic <br /> risk/2.7E-4 hazard quotient for benzene, 9.3E-5 hazard quotient for ethyl benzene, 5.3E- <br /> 5 <br />