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mM KLEINFFLDER <br />The range of concentrations for these metals did not exceed the Total Threshold Limit <br />Concentration (TTLC) Regulated Level for classification of the metals as a hazardous waste per <br />California Code of Regulations 22CCR §66261.24. Additionally these concentrations were not <br />greater than 10 -times the Soluble Threshold Limit Concentration (STLC) Regulated Level for <br />these metals as expressed in 22CCR §66261.24. The factor of 10 -tunes the STLC Regulated <br />Level is commonly used as an indicator as to whether or not a STLC analysis is appropriate to be <br />ran on the sample. The concentrations of nine of the eleven soil samples were found to be below <br />the residential and industrial PRGs for these metals in soil, <br />Arsenic was detected in three soil samples in this area at concentrations exceeding the residential <br />and industrial PRG of 0.39 and 1.6 mg/kg, respectively. However the mean value of arsenic in <br />soil in the western United States according to a U.S. Geological Survey Professional Paper 1270, <br />titled "Element Concentrations in Soils and Other Surflcial materials of the Conterminous United <br />States," dated 1984 (EPA 1270 Professional Paper), is 5.5 mg/kg. Based on this source and from <br />Kleinfelders experience in the San Joaquin Valley, it is Kleinfelder's opinion that the arsenic <br />concentrations detected in this area are likely reflective of background concentrations. <br />Mercury was detected in one soil sample at a concentration of 0.16 mg/kg. This value is below <br />the former (11/1/00) Residential PRG for "mercury and compounds" with a non carcinogenic <br />hazard of 23 mg/kg. The most current PRGs as of 10/1/02 however have a goal of 0.0 mg/kg for <br />"elemental" mercury and no longer have a goal for "mercury and compounds". Because the <br />analytical results reported are for total mercury, which would include mercury and compounds, a <br />direct comparison is not possible at this time to the new elemental mercury goal. <br />POND AREA <br />Three 4 -point composite samples were collected in the pond areas and analyzed for TPH-D and <br />TPH-MO, and organochlorine pesticides. Table 4 summarizes the petroleum and pesticide <br />results. No TPH-D or organochlorine pesticides were detected. TPH-MO was detected in two of <br />the 4 -paint composite soil samples at concentrations ranging from 59 to 6.5 mg/kg. These <br />values appear to be deminimus quantities of TPH-D and based on Kleirlfelder's experience <br />would not generally trigger additional sampling or enforcement actions by regulatory <br />enforcement agencies. <br />FORMER CHEMICAL STORAGE AREA <br />Six discrete soil samples were collected in a former organophosphate pesticide chemical storage <br />area. The samples were collected at depths ranging from 0 to 3 feet bgs. No organophosphate <br />pesticides were detected in any of the six shallow soil samples collected in this area (see Table <br />7), Based on this information, Kleinfelder does not recommend further assessment in this area <br />for organophosphate pesticides. <br />362741 5T03R1919 Page 13 of 19 <br />D 2004 Kleinfelder, Inc. January 5, 2004 <br />