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Steven Sasson -7- February 5, 1996 <br /> i <br /> RfDG = Oral reference dose, mg/kg-day (6 mg/kg-day) <br /> RfD, = Inhalation reference dose, mg/kg-day' (6 mg/kg-day) <br /> ABS = Absorption fraction, dimensionlessz (0 15) <br /> The hazard index for the soil route of exposure was 0 006 The hazard index for the air route of <br /> exposure was 0 009 The total hazard index (adding the hazard indices for the air and the soil <br /> routes of exposure) was 0 015 This value is well below the departure level of 1 Therefore, the <br /> presence of hydraulic fluid at the levels encountered are not expected to pose a significant threat to <br /> human health <br /> It is important to reiterate that this is an extremely conservative assessment First, the soil <br /> pathway of exposure is most likely non-existent due to the location of the residual hydraulic fluid <br /> in the soil Second, the concentration of volatile compounds in the air is based on benzene <br /> Benzene is more volatile than hydraulic fluid, therefore, a higher concentration in air was <br /> estimated for benzene than what is actually the case for hydraulic fluid. Third, this assessment <br /> assumed that the property was being used by children for residential purposes The property is <br /> actually a commercial center Therefore, exposures are expected to be a lot lower than those <br /> represented by a residential scenario <br /> 2.2 Ground Water Assessment <br /> • When evaluating the impacts of releases of chemicals to the environment, it is necessary to assess <br /> the potential for adverse effects on both human health and the environment The effects on the <br /> environment can be assessed by examining the potential impact of chemicals on ground water At <br /> this site, there was a possibility that hydraulic fluid in the soli could migrate to ground water To <br /> assess this possibility, the SICPHS requested that a quarterly ground water monitoring program be <br /> implemented Three monitoring wells were installed and monitored in December of 1994 <br /> Ground water samples were collected two additional times from the same three wells in October <br /> and December of 1995 by The ground water samples collected from the three monitoring wells <br /> were analyzed for TPH calibrated as hydraulic fluid in accordance with Modified USEPA Method <br /> 8015 (GTI 1995a,b) The laboratory analytical results did not detect TPH as hydraulic fluid in the <br /> samples analyzed from any of the sampling events The absence of TPH in the ground water is an <br /> indication that no hydraulic fluid has migrated from the soil to the ground water Since most of <br /> the hydraulic fluid was removed from the soil, it is not likely that there will be any future impact <br /> to ground water. <br /> It is possible, using the same equations presented in the PEA Guidance Manual (DTSC 1994) to <br /> calculate a safe concentration of hydraulic fluid in the ground water This number would give an <br /> ' The oral reference dose was used for the inhalation reference dose This assumes equal absorption by the <br /> oral and inhalation routes <br /> 2 <br /> In the absence of an absorption fraction for hydraulic fluid, that for organic chemicals, 0 15,as suggested by <br /> the PEA guidance manual(I)TSC 1994) was used <br />