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} <br /> • • I <br /> Ms.Lori Duncan <br /> November 15,2011 <br /> RE:2911 E. Fremont St,Stockton,CA <br /> Page 10 of 14 <br /> Based upon the two lines of evidence summarized above,it appears that indoor air concentrations are due <br /> in part to vapor intrusion from subsurface contaminants. <br /> Risk Evaluation <br /> Due to detected concentrations of gasoline constituents in indoor and outdoor air samples collected at the <br /> site, L&P evaluated the potential risk of contaminants in both indoor and outdoor air. <br /> Tier 1 Risk Evaluation <br /> As an initial evaluation,L&P compared detected concentrations of TPHg,benzene,toluene,ethylbenzene, <br /> xylenes,and naphthalene to CHSSLs. The CHSSLs are concentrations of selected hazardous chemicals in <br /> soil,soil gas,or indoor air that the California Environmental Protection Agency(Cal/EPA)considered to <br /> be below thresholds of concern for risks to human health. The thresholds of concern used to develop the <br /> CHHSLs are an excess lifetime cancer risk of one-in-a-million(10-6)and a hazard quotient of 1.0 for non- <br /> cancer health effects. The CHHSLs were developed using standard exposure assumptions and chemical <br /> toxicity values published by the U.S. Environmental Protection Agency (USEPA) and Cal/EPA <br /> (CaUEPA-OEHHA, 2005). <br /> In general, if a contaminant is present in soil, soil gas, or indoor air at concentrations below their <br /> respective CHHSLs,it is assumed that they do not pose a significant health risk to people who may work <br /> at the site. If a contaminant is present at a concentration exceeding its respective CHHSL, however, it <br /> does not necessarily indicate that adverse impacts to human health are present or will occur; it suggests <br /> that further evaluation is warranted and mitigation may or may not be necessary. Further evaluation could <br /> include additional sampling and analysis, consideration of ambient samples, and/or using site specific <br /> parameters to calculate potential human health risk at the site. <br /> As summarized in Table 3,TPHg,benzene,toluene,ethylbenzene,and xylenes were detected in all four air <br /> samples collected at the site, regardless of whether the samples were indoor air or ambient air samples. A <br /> comparison of concentrations of contaminants in air with the respective CHHSLs are summarized below. <br /> TPHg: No CHHSL has been established for TPHg. As tve, L&P compared concentrations of <br /> TPHg in air to Environmental Screening Levels (ESL5) f r indoor alr n commercial/industrial settings,as <br /> established by the California Regional Water Quality Cool Board RWQCB),San Franciso Bay Region <br /> (May 2008). Similar to the CHHSLs, the ESLs establish conservative reference concentrations for <br /> comparison to actual site data for a conservative evaluation of the possible health risk Concentrations of <br /> TPHg in ambient air samples were below the ESL of 14 micrograms per cubic meter µg/m3 while <br /> concentrations of TPHg in indoor air were above the ESL. It should be noted that the ESL for TPHg is based <br /> upon conservative noncancerous exposure (hazard quotient of 0.2) rather than the hazard quotient of 1.0 <br /> utilized by Cal/EPA to establish CSHHLs. <br /> Benzene: Concentrations of benzene in ambient air and indoor air samples exceeded the CHHSL of 0.14 <br /> µg/_ m',although the concentrations in indoor air(1.3 to 1.6µg/m3)exceeded those in ambient air(0.45 to <br /> 0.71 µg/m3). <br /> 10759-EXC SUMMARY LTR <br />