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8.0 DISCUSSION AND CONCLUSIONS - PHASE 11 SITE INVESTIGATION <br /> u 8.1 Discussion of 30 to 50 feet bgs. As discussed above based on <br /> the seven borings in this study, the silty gravels <br /> are underlain by clayey silts with and without <br /> 8.1.1 Existing Above Ground Storage gravel and groundwater was measured beneath <br /> Tanks Location the site at a depth of 65 feet bgs. Based on the <br /> above, and the RWQCB Guidance document, the <br /> nitrate concentration reported in the soil sample <br /> y One 550-gallon gasoline and one 550-gallon would not require mitigation. <br /> diesel farm ASTs have reportedly been present on <br /> Site for the last 5 or 6 years since the removal of DDE, a breakdown product of DDT, was detected <br /> the two former gasoline USTs. Initial interviews at a concentration of 33 ug/kg. As previously <br /> with Mr. Lopez(foreman) had indicated that the discussed, use of DDT on the Site was <br /> diesel AST had previously been present at the discontinued when the federal E.P.A.banned its <br /> r.., current location of the secondary containment use in 1973. To evaluate if the detected <br /> structure. Surficial soils in the immediate concentration of DDE was a concern, the <br /> vicinity of the former AST were concealed by the concentration of DDE detected in the composite <br /> installation of the secondary containment soil sample was compared to risk-based soil <br /> structure; any potential spillage or leakage stains screening concentrations developed by Region IX <br /> if they were present are no longer visible. of the United States Environmental Protection <br /> Analytical testing of soil samples collected from Agency(U.S. EPA) (EPA, 1996). These soil <br /> boring SB-1, drilled adjacent to the existing ASTs, screening concentrations or Preliminary <br /> did not report detectable concentrations of TPHg, Remediation Goals (PRGs) are conservative (i.e., <br /> TPHd, or BTEX compounds in any of the health-protective), multipathway values <br /> samples. Based on the analytical and field developed by EPA to protect the health of <br /> evidence the existing ASTs and former AST at humans potentially exposed to soil through <br /> this location are eliminated as a REC. Further ingestion, dermal (skin) contact, and dust <br /> inquiries with Mr. Lopez and Mr. Selover, inhalation. Standard risk equations, EPA toxicity <br /> v indicated that the diesel AST cited above had values, and conservative exposure assumptions <br /> also been previously located near former USTs (e.g., soil ingestion rate and exposure duration) <br /> for at least twenty years. This area was were used to develop the PRGs, which are <br /> investigated as part of the borings drilled in the regularly updated. For a residential land use <br /> ` vicinity of the former USTs. A discussion of the scenario, the PRG for DDE is 1.3 mg/kg; for an <br /> UST area is presented in Section 8.1.3. industrial scenario, the PRG is 5.6 mg/kg. The <br /> detected concentration of 0.033 mg/kg (33 ug/kg) <br /> r., is substantially below both PRGs, suggesting that <br /> 8.1.2 Agricultural Chemical Mixing human health risks are unlikely to result from <br /> Areas - Composite Soil Sampling exposure to DDE at the three agricultural mixing <br /> areas onsite. <br /> V <br /> Only three of the analytes(nitrate, DDE, and Diuron was detected at a concentration of 0.37 <br /> diuron) were present at detectable levels in the mg/kg near the method reporting limit of 0.20 <br /> composite sample collected at the agricultural mg/kg. Diuron(trade names e.g., Karamex and <br /> chemicals mixing areas. Nitrate was detected in Krovar) is a pre-emergent herbicide commonly <br /> the composite sample (reported as NO3) at a used to control weeds prior to germination. <br /> concentration of 278 mg/kg. The Regional Water Diuron, as one of the phenylureas, is strongly <br /> Quality Control Board, Central Valley Region adsorbed to soils(Ware, 1989) It is therefore <br /> (RWQCB) guidance for remediation of nitrate likely to be concentrated in the surficial soils and <br /> impacted soils at retail fertilizer facilities unlikely to pose any threat to groundwater <br /> (RWQCB, 1996) suggests a cleanup level of beneath the Site. As previously discussed, <br /> approximately 900 mg/kg of nitrate as NO3 for interviews with Mr. Lopez indicated that several <br /> sites with loamy soils and a depth to groundwater herbicides had been used to control weeds <br /> r+ <br /> G:\WP\GDH\GH36371Z.151 Harding Lawson Associates 16 <br /> Y.r <br />