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Chevron Environmental Management Company Soil and Groundwater Investigation Report <br /> Tracy Byron Road Project <br /> kilogram(mg/kg)were not reported in soil samples collected from 15 of the 36 soil borings. TPHc <br /> concentrations ranged from 5.1 mg/kg to 8,300 mg/kg. <br /> In general the highest concentrations of TPHc were detected in soil samples collected from 5 to 12 feet <br /> bgs. In many of these borings, this interval represents the vadose zone; the interval between ground <br /> surface and the depth of first encountered groundwater. Soil samples collected between 5 and 12 feet bgs <br /> containing concentrations of TPHc greater than 1,000 mg/kg were collected from borings SB-2, SB-10, <br /> SB-11, SB-19, SB-22, SB-23, SB-25, SB-26, SB-28, SB-34, SB-35, and SB-36. In samples collected <br /> deeper than 12 feet bgs, elevated concentrations of TPHc were detected in borings SB-3 (980 mg/kg at 22 <br /> feet bgs), SB-6 (8 10 mg/kg at 18 feet bgs), and SB-30 (8 10 mg/kg at 14 feet bgs). <br /> Detectable concentrations of TPHc were not reported in 25 of the 35 soil samples collected from the total <br /> depth of each boring. A soil sample collected at 41 feet bgs from SB-22 was not analyzed due to <br /> concerns of sample cross-contamination from SPO encountered in the borehole. Detectable <br /> concentrations of TPHc in the bottom samples ranged from 5.1 mg/kg to 39 mg/kg. <br /> Benzene was not reported at or above the laboratory detection limit in any of the soil samples collected <br /> from the 36 borings. Toluene was not detected in 28 of the 36 soil borings. Detectable concentrations of <br /> toluene ranged from 0.04 mg/kg to 0.2 mg/kg. Ethylbenzene was not detected in 25 of the 36 soil <br /> borings. Detectable concentrations of ethylbenzene ranged from 0.006 mg/kg to 1.1 mg/kg. Total <br /> xylenes were not detected in 25 of the 36 soil borings. Detectable concentrations of total xylenes ranged <br /> from 0.03 mg/kg to 9.5 mg/kg. Soil sample chemical analytical results are presented in Table 1 and on <br /> Figures 3a, 3b, 3c, and 3d. <br /> Soil samples from boring SB-29 did not contain any detectable PAHs. However, detectable <br /> concentrations of PAHs were reported in 35 of the 36 soil borings. Phenanthrene and pyrene were the <br /> two most frequently reported PAHs and were detected in 89 and 78 of the 100 soil samples submitted for <br /> analysis,respectively. Reported concentrations of phenanthrene ranged from 0.0003 mg/kg to 3.8 mg/kg. <br /> Reported concentrations of pyrene ranged from 0.0004 mg/kg to 1.5 mg/kg. Benzo(a)pyrene and <br /> dibenzo(a,h)anthracene were not detected in soil samples submitted from 15 and 27 of the 36 soil borings, <br /> respectively. Reported concentrations of benzo(a)pyrene ranged from 0.0004 mg/kg to 0.30 mg/kg. <br /> Reported concentrations of dibenzo(a,h)anthracene ranged from 0.0005 mg/kg to 0.050 mg/kg. Soil <br /> sample chemical analytical results for PAHs are presented in Table 2, and on Figures 3a, 3b, 3c, and 3d. <br /> Copies of the soil chemical analytical reports are included in Appendix D. <br /> 5.2 GRAB GROUNDWATER SAMPLE ANALYSES <br /> All groundwater samples collected by SAIC were submitted to Friedman&Bruya, Inc. (F&B) in Seattle, <br /> Washington(California certified laboratory# 1727)under SAIC chain-of-custody procedure. Selected <br /> groundwater samples were analyzed for BTEX by EPA Method 8021 B,total petroleum hydrocarbons <br /> quantified as diesel (TPHd; C10—C25)by EPA Method 8015 Modified with and without silica gel <br /> cleanup, and PAHs by EPA Method 8270 C SIM. For silica gel cleanup an aliquot of the sample extract <br /> for TPHd analysis was passed through a l0-gram column of silica gel and re-analyzed for TPHd by EPA <br /> Method 8015 Modred. In addition, selected grab groundwater samples were submitted for analysis of <br /> total dissolved solids (TDS)by EPA Method 160.1. Grab groundwater samples were analyzed for TDS <br /> to gauge groundwater quality as it pertains to a potential drinking water resource. TDS samples were <br /> submitted to North Creek Analytical, Inc. of Seattle,Washington under F&B chain of custody. In <br /> addition to SAIC's grab groundwater samples,the RWQCB collected split groundwater samples from <br /> borings SB-34 (GW-34-19) and SB-35 (GW-35-18). The RWQCB submitted their samples to a separate <br /> analytical laboratory under RWQCB chain of custody. <br /> 5.2.1 Grab Groundwater Sampling Analytical Results <br /> Concentrations of TPHd were detected above the laboratory reporting limit in 9 of the 15 groundwater <br /> samples analyzed by EPA Method 8015 Modified, without silica gel cleanup. Concentrations of TPHd <br /> ranged from 59 micrograms per liter(tig/L) in groundwater sample GW-12-13 to 8,900 µg/L in <br /> 6 <br />