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Chevron Products Company Page 1 <br />Pormer Chevron service station #9-5775, 301 West Kettleman Lane, Lodi. California August 15. 2002 <br />0 INTRODUCTION <br />SECOR International Incorporated (SECOR), on behalf of Chevron Products Company <br />(Chevron), presents operating data for the groundwater extraction (GWE) system at 301 <br />Kettleman Lane, Lodi California (Figure 1). Chevron discharges treated groundwater at <br />the subject site under City of Lodi Wastewater Discharge Permit #310. This report <br />presents July 2002 data collected between June 25 and July 30, 2002. <br />GROUNDWATER EXTRACTION SYSTEM <br />Extraction and treatment of groundwater was initiated on July 3, 2000. The GWE system <br />consists of extraction wells EX -1, EX -2 and EX -3 (Figure 2). These wells are equipped <br />with submersible pumps connected through mechanical piping to a series of granular <br />activated carbon (GAC) vessels prior to an industrial sewer discharge point. Pumping <br />through the wells from areas affected by petroleum hydrocarbons prevents migration of <br />these hydrocarbons off-site. A treatment system schematic is shown on Figure 3. <br />To assess effectiveness of the GWE system, process samples were collected weekly <br />during this reporting period. Sample locations include an influent port (INFL), prior to <br />the first GAC vessel, between the first and second GAC vessels (MID -1), between the <br />second and third GAC vessels (MID -2), and prior to discharge (EFFL) to the industrial <br />sewer. During these sampling events, INFL, MID -1, MID -2, and EFFL samples were <br />analyzed for total petroleum hydrocarbons as gasoline (TPHg), benzene, toluene, ethyl - <br />benzene, and total xylenes (BTEX compounds), methyl tertiary butyl ether (MtBE), <br />tertiary amyl methyl ether (TAME), ethanol, methanol, ethylene dibromide (EDB), and <br />1,2-dicholoethane (1,2 -DCA). Maximum concentrations of detected constituents are <br />presented below. Current and historical analytical results are presented as Table 1. <br />Sampling <br />Port <br />Maximum Constituent Concentration (gg/1) <br />July 2 throw h July 30, 2002 <br />MtBE TBA ELBE TAME Ethanol <br />Methanol <br />11V17L <br />71 <br />13 <br />4.7 <2.0 <br /><100 <br /><400 <br />MID -1 <br /><2.0 <br /><10 <br /><2.0 <2.0 <br /><100 <br /><400 <br />MID -2 <br /><2.0 <br />12 <br /><2.0 <2.0 <br /><100 <br /><400 <br />EFFL <br /><2.0 <br /><10 <br /><2.0 <2.0 <br /><100 <br /><400 <br />Explanations: <br />< indicates the constituent was not <br />present at or above the method 12orting limit shown <br />Between June 25 and July 30, 2002, the GWE system discharged a total of 575,633 <br />gallons of treated groundwater over a period of 36 days (Table 2). As of June 30, 2002, <br />the GWE system has treated a total of 3,639,376 gallons. Calculated discharge rates <br />during the July monitoring period ranged from 9.34 to 9.78 gallons per minute (gpm). <br />During the July monitoring period the system extracted approximately 0.1 pounds of <br />TPHg, 0.001 pounds of benzene, and 0.3 pounds of MtBE. To date, the system has <br />extracted approximately 7.9 pounds of TPHg, 0.2 pounds of benzene, and 84.1 pounds of <br />MtBE. Plots of GWE system mass removal trends and influent groundwater TPHg, <br />benzene, and MtBE concentrations versus time are shown on Figures 4 and 5 <br />[:1Chevron1957751Periodic Monitoring\O & M1ReportslMonth1y\Discharge Reports120021[uly 20021July 2002 DR.doe <br />