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Approximate Depth to Groundwater 43 30 to 47 60 feet below too of well casco <br /> . Groundwater Flow Direction South-southeast <br /> Groundwater Gradient 0 004 ft/ft <br /> SVE SYSTEM QUARTERLY OPERATION AND PERFORMANCE <br /> Equipment Inventory Solleco 100 cfm electric catalytic oxidizer <br /> Operating Mode Catalytic <br /> APCD Permit No N-4887-2-0 <br /> Influent TPHG Concentration End of Period 40 milligrams per cubic meter m Im3 <br /> Influent Benzene Concentration End of Period a0 15 mglm3 <br /> Flow Rate End of Period 77 <br /> HC Destroyed this Period (lab) 40 83 lbs as TPHG <br /> Cumulative HC Destroyed 4,114 12 lbs as TPHG <br /> Percent Time Operational 939 <br /> DISCUSSION <br /> At the time of the first quarter 2005 monitoring event, groundwater elevations had increased between 1 06 <br /> and 1 81 feet in wells MW-1 through MW-4, and MW-6 through MW-10 since the previous monitoring <br /> event (October 4, 2004) Depth-to-water measurements were normalized to mean sea level (MSL), and <br /> were used to construct a groundwater elevation contour map (Figure 2) Well S-1 was dry The <br /> . groundwater flow direction on January 12, 2005, was generally to the south-southeast at an average <br /> gradient of 0 004 ft/ft. South-southeast groundwater flow direction has consistently been observed during <br /> previous monitoring events <br /> MTBE (0 85 pg/L) was reported in well MW-8 TPHG, BTEX, TBA, DIPS, ETRE, TAME, methanol, or <br /> ethanol were not reported in any of the wells Analytical results are generally consistent with historical <br /> analytical data TPHG, benzene, and MTBE data have been summarized on Figure 3 <br /> System Description <br /> Soil Vapor Extraction and Abatement SVE System <br /> The SVE system consists of a Solleco 100 cfm electric catalytic oxidizer (Model 100 ECAT) with a 5 <br /> horsepower (hp) blower Upon system start-up (October 20, 2004), petroleum hydrocarbon laden soil <br /> vapors were extracted from wells S-1, S-2, and MW-8 using the 5 HP blower package of the SVE system <br /> rated at 100 cfm at 14 inches of mercury Figure 2 presents the locations of the vapor extraction wells, <br /> remediation system, and other pertinent site features The extracted soil vapors were abated in the <br /> catalytic oxidizer prior to discharge to the atmosphere The SVE system has an in-built hour meter and <br /> recordings are used to determine the operational uptime Sample ports(influent, cat-influent, and effluent) <br /> are designated to collect air samples The results of air samples are used to estimate the destruction <br /> efficiency of the system <br /> Remedial activities at the site were initiated with a SVE system consisting of a 150 cfm Stealth Bobcat <br /> catalytic oxidizer (cat-ox) and was operated at the site between August 15, 2000 and August 15, 2002, <br /> under permit N-903-2-0 Due to low influent concentrations, the cat-ox system was replaced with a SVE <br /> system consisting of a 2 3 HP Fuji Blower and two 1,000 lbs vapor phase carbon units, which operated at <br /> the site between August 1, 2003 and March 12, 2004, under permit N-4887-1-0 The vapor phase carbon <br /> adsorption system was replaced with the currently operating Solleco 100 cfm electric cat-ox in October <br /> K%USA Gasoime10065IQtr1y12005%USA_65_1 Q05 DOC 577�ftiTUS <br />