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Chevron Products Company Page 1 <br />firmer Chevron Service Station #9-5775, 301 West Kettleman Lane. Ladi. California _„_ �_- Mav 15.2002 <br />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 April 2002 data collected between March 29 and April 30, 2002. <br />GROUNDWATER EXTRACTION SYSTEM <br />Extraction and treatment of groundwater was initiated on July 3, 2000. The GWE <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 />Aril 3 through April 30, 2002 <br />MtBE I <br />TBA <br />EtBE TAME <br />Ethanol <br />Methanol <br />INFL <br />150 <br /><5.0 <br />12 1.3 <br /><5.0 <br /><100 <br />MID -1 <br /><0.50 <br /><5.0 <br /><0.50 <0.50 <br /><5.0 <br /><50 <br />MID -2 <br /><0.50 <br /><5.0 <br /><0.50 <0.50 <br /><5.0 <br /><50 <br />EFFL <br /><0.50 <br /><5.0 <br /><0.50 <0.50 <br /><5.0 <br /><200 <br />Explanations: <br />< indicates the constituent was not present at or above the method reporting <br />limit shown <br />Between March 29 and April 30, 2002, the GWE system discharged a total of 389,424 <br />gallons of treated groundwater over a period of 32 days (Table 2). As of April 30, 2002, <br />the GWE system has treated a total of 2,345,247 gallons. Calculated discharge rates <br />during the April monitoring period ranged from 6.59 to 10.41 gallons per minute (gpm). <br />During the April monitoring period the system extracted approximately 0.1 pounds of <br />TPHg, 0.001 pounds of benzene, and 0.5 pounds of MtBE. To date, the system has <br />extracted approximately 7.7 pounds of TPHg, 0.2 pounds of benzene, and 83.1 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 />]AChevron1957751Periodic Monitoringl0 & M\Reports\Monthly\Discharge Repons120021April 20021April 2002 DR.doc <br />