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Kennedy/Jenks Consultants <br /> The distribution of TPHg in groundwater is presented on Figure 13, TPHd on Figure 14, and <br /> TPHmo on Figure 15. <br /> ' Figure 13 indicates that the lateral extent of TPHg in groundwater appears to be bounded on the <br /> north, east, and south by samples where TPHg was not detected at concentrations exceeding <br /> analytical reporting limits. The western extent of TPHg is not known and TPHg was detected in <br /> sample OU5-AO110-GW-14-20 at a concentration of 1,900 pg/I. The highest concentrations of <br /> TPHg were observed in the groundwater sample OU5-AO110-GW-4-20. Elevated TPHg <br /> concentrations and visible hydrocarbon product were observed in samples <br /> OU5-AO110-GW-14-20 and OU5-AO110-GW-17-20, suggesting that elevated TPHg <br /> concentrations may extend farther to the west or northwest. <br /> Figure 14 illustrates that the lateral extent of TPHd in groundwater to the north and east has not <br /> been characterized. The TPHd concentrations in the northernmost and easternmost samples <br /> are lower than TPHd concentrations in samples from the central portion of AOI 10 and, <br /> assuming a single TPH source area in AOI 10, it is probable that the TPHd does not extend <br /> much farther to the north and east in groundwater. Elevated TPHd concentrations and visible <br /> hydrocarbon product were observed in offsite samples OU5-AO110-GW-14-20 and <br /> OU5-AO110-GW-17-20, suggesting that elevated TPHd concentrations may extend farther to <br /> the west or northwest. <br /> Figure 15 illustrates that the lateral extent of TPHmo to the north and east has not been <br /> characterized. The TPHmo concentrations in the northernmost and easternmost samples are <br /> lower than TPHmo concentrations in samples from the central portion of AOI 10 and, assuming <br /> a single source area in AOI 10, it is probable that the TPHmo in groundwater does not extend <br /> much farther to the north and east. Elevated TPHmo concentrations and visible hydrocarbon <br /> product were found in offsite samples OU5-AOl10-GW-14-20 and OU5-AO110-GW-17-20, <br /> suggesting that elevated TPHmo concentrations may extend farther to the west or northwest. <br /> The distribution of TPH in groundwater illustrated on Figures 13 through 15 is consistent with a <br /> release in the OU5-AO110-GW-4 area (or near the pipe discovered by Geocon) and a northwest <br /> groundwater gradient. <br /> 5.8 Background Arsenic Concentrations <br /> The arsenic concentration in every soil sample exceeded the residential and industrial PRGs <br /> and CHHSLs, regardless of the sample location. This finding is typical of background arsenic <br /> concentrations in northern California soils. <br /> Background arsenic concentrations for California soils have been discussed in several <br /> publications. Using 50 benchmark soils from across the state, Bradford et al. (1996) estimated a <br /> mean arsenic concentration of 3.5 mg/kg and a median concentration of 2.7 mg/kg. The <br /> Lawrence Berkeley National Laboratory (LBNL 1995) determined a mean arsenic concentration <br /> of 5.39 mg/kg and a 95% Upper Confidence Limit (UCL) concentration of 14.0 mg/kg in <br /> colluvium and fill at the Lawrence Berkeley National Laboratory in Berkeley, California. <br /> Shacklette and Boerngen (1984) report a geometric mean concentration of 5.5 mg/kg for <br /> arsenic in western U.S. soils. <br /> DRAFT Phase I Remedial Investigation Report Page 37 <br /> Former Tracy Railyard, Tracy, California <br /> g:lis-groupladminl ob10510565777.18_uprr\09-feports\ri rptltexldoc <br />