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Wendy L. Cohen -3- 5 May 1994 <br /> I have reviewed further HLA's 1 I October 1993 Plume Characterization Investigation Report and <br /> sections of PRC Environmental Management, Inc.'s July 1993 and the revised February 1994 Site <br /> Investigation Report for the nearby Naval Communication Station. <br /> HLA's report states that the concentrations of TPHD in ground water at several locations decreased <br /> near Hooper Drive and then increased moving west and southwest of Hooper Drive. The report also <br /> states that a nondetect line was apparent for benzene, toluene, ethylbenzene, and xylene [BTEX <br /> (samples 49, 50, 41, 42, and 47)] parallel to Hooper Drive and that low concentrations of BTEX <br /> appeared southwest of that area (Plate 2, Sample 51). The report concluded that another potential <br /> source of petroleum hydrocarbon constituents likely exists on Navy property. The report further <br /> states that the presence of chlorinated solvents in ground water in the vicinity of Site 4 appears to <br /> present a greater potential threat to ground water quality than the concentrations of TPHD in the area <br /> south and west of Hooper Drive. <br /> The PRC report states that Site 4 was used for temporary storage of leaking and/or damaged <br /> containers from 1972 to 1983, a site investigation has been completed, and DDT-contaminated <br /> surficial soil is the key problem at this site. PRC recommended removal of surface soil containing <br /> DDT at Site 4. Regarding the petroleum hydrocarbon contamination at Shell, PRC recommended <br /> that the Navy request Shell to control and clean up the hydrocarbon plume migrating in ground water <br /> beneath the Navy property, and evaluate Shell's monitoring wells for abandonment based on <br /> recognition of a confined aquifer and excessive screen lengths. <br /> Comments <br /> 1. As stated in the Plume Characterization Investigation Report, BTEX was detected at low levels <br /> in Sample 51, southwest of Hooper Drive. This is just one sample and the result was not <br /> verified. Additional samples should have been taken to confirm these results. <br /> 2. The TPHD detected west of Hooper Drive is within the range of TPHD detected east of Hooper <br /> Drive. This could be the same plume. <br /> 3. Attachment 1 presents the results of soil and ground water sampling around Site 4 at the USN <br /> property. The soil samples were obtained from sample locations 17-20. Ground water samples <br /> were taken from MWs 3, 4, and 20. The soil sample results show the presence of oil and grease <br /> (33-4,800 mg/kg) and pesticides at all four sampling locations, long chain hydrocarbons (130 <br /> mg/kg) in sample 19, toluene (0.001 mg/kg) and pentachlorophenol (0.081 mg/kg) in sample 17, <br /> and tetrachloroethane in sample 18 (0.003 mg/kg) and sample 20 (0.099 mg/kg). The ground <br /> water sample results show nondetectable levels of BTEX, TPH, and oil and grease in MWs 3 <br /> and 20. MW 4 contained TPH (1.7 µg/1), oil and grease (3 mg/1), and phenol (26 µg/1). MWs 3 <br /> and 20 had 160 and 4 µg/1, respectively, of 1,2-dichloroethene (DCE). MW 3 also had 1,1- <br /> dichloroethane; 1,1-DCE; trichloroethylene; tetrachloroethylene; and vinyl chloride. Based on <br /> these results, Site 4 does not appear to be the source of petroleum hydrocarbons detected west of <br /> Hooper Drive during Shell's Phase III hydropunch investigation. <br /> 4. It is not known if the chlorinated hydrocarbon compounds and pesticides being detected in the <br /> vicinity of Site 4 are present in the hydropunch investigation area since these chemicals were not <br /> analyzed during Shell's investigation. The presence of these compounds in the hydropunch <br /> investigation area would suggest that contaminants from Site 4 are migrating towards this area. <br />