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1 S ' <br /> I <br /> i Groundwater Flow Direction: South-southeast <br /> Groundwater Gradient: 0.001 ftlft <br /> } <br /> SVE SYSTEM QUARTERLY OPERATION AND PERFORMANCE <br /> Equipment Inventory: 2.3 HP Fuji Blower, two 1,000 Ib carbon vessels <br /> i <br /> Operating Mode: Operational <br /> APCD Permit No.: N-4887-1-0(ATC) _ <br /> Influent TPHG Concentration End of Period: 16 Mg/M3 <br /> + Influent Benzene Concentration End of Period: X0.15 mg/m3 <br /> i Flow Rate End of Period: 45.3cfm } <br /> HC Destroyed this Period (lab): 181 lbs <br /> Cumulative HC Destroyed: 3682.89 lbs. <br /> I <br /> Percent Time Operational: 75(average) <br /> DISCUSSION: <br /> i <br /> i <br /> At the time of the first quarter 2004 monitoring event, groundwater elevations had increased between 1.92 <br /> and 2.12 feet since the previous sampling event (October 21, 2002). Depth to water measurements were <br /> normalized to mean sea level (MSL), and were used to construct a groundwater elevation contour map <br /> (Figure 2). The groundwater elevation in well S-2 appeared anomalous and was not used in contour <br /> construction. The groundwater flow direction on January 7, 2004, was calculated to be towards the <br /> south-southeast at an average gradient of 0.001 ft/ft. South-southeast groundwater flow direction has <br /> ( � consistently been observed during previous monitoring events. <br /> TPHG (240 pg/L) and MTBE (110 µg/L) were reported in well MW-8. Benzene was not reported in any of <br /> the wells. TBA was reported in wells MW-1 through MW-4, and MW-6 through MW-10 with the highest r <br /> concentration (56 µg/L) reported in well MW-8. BTEX, DIPE, ETRE, or TAME were not reported in any of + <br /> h the wells: Analytical results from the January 7, 2004, sampling event are generally consistent with <br /> historical analytical data. TPHG, benzene, and MTBE data have been summarized on Figure 3. <br /> On February 11, 2004, Stratus conducted a carbon change-out. The SVE system was re-started on <br /> f Februarys 17, 2004 to verify system'airflow rates and then shut down. The system was restarted on <br /> February19, 2004, and samples were collected. The system was shutdown on March 12, 2004, as TPHG <br /> l was repo4ed in the midfluent air sample collected on March 11, 2004. <br /> { Between February 11 and March 12,2004, Stratus conducted seven site visits to operate and maintain the <br /> SVE system, and to collect the compliance air samples. The SVE system extracted approximately 181 <br /> pounds of TPHG during the first quarter 2004, and has extracted a cumulative mass of approximately <br /> 3682.89 pounds of TPHG since the first installation of SVE system (August 2000). On March 4, 2004, the <br /> { SVE system exceeded the 70cfm permit requirement by 5.9 cfm, the system was revisited on March 11, <br /> 2004, avid flow was recorded at 45.3 cfm. The destruction efficiency of the activated carbon system j <br /> k appears to be low due to high variations in influent soil vapor concentrations, Due to the high degree of <br /> fluctuation in influent soil vapor concentrations, Stratus proposes to reinstall a 100 cfm catalytic oxidizer at <br /> the site to extract and abate soil vapors. I <br /> I I` <br /> I <br /> PAUSA Gasoline10065%Qtrly120041USA_65_IQ04.DOC STRATUS <br /> I '3 <br />