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Updated Site Conceptual Model and First Quarter 2002 Monitoring and Remediation Report <br /> Cleanup and Abatement Order No 5-00-707 EAI Project No 1232 <br /> 5.5 Analytical Testing Results <br /> 5 5 1 Units A and B Wells <br /> For Units A and B, similar or lower hydrocarbon concentrations were generally observed <br /> during this sampling event when compared to the prior quarters data Figure 17 summarizes <br /> the TPH-G, BTEX, and MTBE concentrations in ground water for the March 2002 ground <br />' water sampling event No MTBE, TBA, DIPE, ETRE, TAME, or EDB above laboratory <br /> reporting limits were detected in any of the ground water samples <br /> 5 5 2 Units C and_D Wells (MW-8D, MW-23S/D, and MW-24S/D) <br /> Similar or lower hydrocarbon concentrations were generally observed during this sampling <br /> event when compared to the prior quarters data The exceptions were wells MW-23S and MW- <br /> 23D, where significantly higher concentrations of hydrocarbons were observed (see Table 1) <br /> Well MW-23S was selected for deep air sparging on the Unocal site Sparging on well MW- <br /> 23S was performed on February 20, 2002, approximately 10 days prior to a ground water <br /> monitoring event All other air sparging wells on Unocal and Montgomery sites were cut off <br /> the air sparging header to allow the compressor to develop the pressure sufficient to overcome <br /> the column of water above well MW-23S perforation (approximately 60 feet) Sparging was <br /> performed for one hour at a compressor pressure discharge of 45 psig No increase in VOC <br /> held reading and analytical testing at the inlet of the oxidizer was observed <br /> Analytical results of ground water in wells MW-23S and MW-23D showed a sharp increase in <br /> the concentration of dissolved hydrocarbons, e g , <50 gg/L of TPH-G in December 2001 to <br /> 25,000 gg/L of TPH-G in March, 2002 for well MW23-S (see Table 6) Apparently, deep <br /> sparging resulted in mixing ground water in the vicinity of the sparging wells It is difficult to <br /> assess the affected area, however, using a rule of thumb that radius of influence is equal to the <br /> distance from the ground water surface to the sparging point, it is assumed that an area within a <br /> 60-foot radius was affected <br /> No further dee sparging will be conducted until after review and evaluation of ground water <br /> quality data from the next monitoring event in dune 2002 Based on these data, a <br /> recommendation regarding deep sparging will be made <br /> 5 5 3 Well MW-9 and Other Perimeter Wells <br /> In September 2001 and December 2001, down gradient well MW-9 contained TPH-G at <br /> concentrations of 1,070 gg/L and 58 gg/L, respectively In March 2002, the TPH-G <br /> concentration in this well was below the detection limit of<50 gg/L This indicates that the <br /> remediation system is able to contain the plume Further, the limits of the plume appear to be <br />' defined by perimeter wells MW-17, MW-15, MW-14, MW-13, MW-18, MW-27, MW-9, MW- <br /> 7 and MW-5 These sentinel wells will continue to be monitored to assure the plume is stable <br /> . and not migrating <br /> BHM 1232RQ231 <br /> -10- <br /> ENVIRONMENTAL AUDIT, INC <br />