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UST Closure Report <br /> Sharpe Defense Distribution Region West <br /> Lathrop,California Page 19 <br /> MTBE was detected in concentrations greater than 10 gg/kg (detection limit) in 22 of the 42 soil <br /> samples from the excavation stockpile that were analyzed. In these, MTBE ranged from 13 to <br /> 210 gg/kg. However, the concentrations of MTBE were greater than method detection limits in <br /> 82% (18 of the 22) samples collected from stockpiles SPA and SPB, but only 20% (4 of the 20) <br /> samples from the stockpile SPD. This could be the result of the mixing and some degree of <br /> aeration that the soil underwent while transferring the soil from stockpiles SPA and SPB to SPD. <br /> The 20 samples from stockpile SPD were initially analyzed for the oxygenates by EPA Method <br /> 8020. The 7 samples with concentrations of MTBE above the method detection limit were <br /> reanalyzed for oxygenates by EPA Method 8260. These showed that EPA Method 8020 yielded <br /> `false positive' results for MTBE in three samples (SPD-3, SPD-10 and SPD-12). <br /> The concentration of MTBE ranged from 13 to 80 gg/kg in the 18 samples from stockpiles SPA <br /> and SPB in which it was detected. The 22 samples from the stockpile contained an average of <br /> 34 gg/kg MTBE, assuming that those with concentrations below the detection limit contained <br /> 10 gg/kg MTBE (i.e. the detection limit). The concentration of MTBE ranged from 14 to <br /> 210 gg/kg in the 4 samples from stockpile SPD in which MTBE was detected. The other <br /> parameters analyzed in the sample with 210 gg/kg MTBE were all below detection limit except <br /> TPH-D (9.2 mg/kg) and very high total lead (200 mg/kg). However, total lead was not detected <br /> in the other two samples with relatively high concentrations of MTBE (24 gg/kg in SPD-4 and <br /> 27 gg/kg in SPD-8). <br /> Concentrations of the other five oxygenate parameters analyzed in the samples from stockpiles <br /> SPA and SPB (ethanol, tertiary-butanol, DIPE, ETBE and TAME) were all less than the <br /> detection limits. Only the samples from stockpile SPD with concentrations of MTBE above the <br /> method detection limit of EPA Method 8020 were analyzed for oxygenates by EPA Method <br /> 8260. The concentrations of these five oxygenates were all below the method detection limit. <br /> 5.4 Product and Vapor Return Pipe Line Soil Samples <br /> The concentrations of MTBE were somewhat above the method detection limit of 10 gg/kg in <br /> three of the 11 samples collected from the floor of the trenches excavated to remove product and <br /> vapor return piping (PL- series, Figure 6). Two of the samples were from the site of the small <br /> dispenser west of the truck fill stand (12 and 23 gg/kg MTBE in PL-1 and PL-2, respectively). <br /> The third was from the south end of the truck fill stand, the site of overhead dispensers for <br /> gasoline and diesel fuel (sample PL-10 with 16 gg/kg MTBE). The concentrations of the other <br /> five oxygenates were below method detection limits in all 11 samples. <br /> TPH-D was detected in concentrations above the method detection limits in 7 of the 11 samples <br /> from the trenches. Concentrations of TPH-D in those samples ranged from 3.9 to 68 mg/kg. <br /> Only three of the samples were collected from the site of fuel dispensers; the other 4 from areas <br /> ® of 90° bends in the direction of product pipes. And only two of the 7 samples with detectable <br /> TPH-D also contained concentrations of MTBE greater than the method detection limits: PL-2 <br /> from the western product dispenser (25 gg/kg) and PL-11 from just northwest of UST #21 <br /> N:\PROJECTS\3546\Reports\3546 UST Closure Report Draft.doc March 24,1999 <br />