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Ms Lon Duncan <br /> Page 2 of 3 <br /> .� included in Attachment B <br /> Groundwater Monitoring <br /> Monitoring wells MWl through MW4 were momtored for water level elevations and wells MWl, MW2 <br /> and MW4 were purged and sampled on March 12, 2002 No samples were collected from well MW3 due <br /> to the presence of free product The depth to water in wells MW 1, MW2, and MW4 was monitored using <br /> an electronic water level indicator The depth to water and depth to product in well MW3 was measured <br /> usmg an electronic water/hydrocarbon interface probe <br /> Groundwater elevations were calculated by subtracting the measured depth to groundwater in each well <br /> from the respective wellhead elevation The depth to groundwater in the wells on March 12, 2002 ranged <br /> from 22 47 to 23 19 feet below ground surface (bgs) Groundwater rose approximately 0 81 feet since last <br /> measured on December 12, 2001, and flowed in a northeasterly direction with an average gradient of <br /> approximately 0 0027 (or approximately 14 feet per mile) A potentiometnc surface map generated using <br /> the March 12,2002 monitoring data is shown on Figure 2 Groundwater monitoring data are summarized in <br /> Table 2 Monitoring data sheets are included in Attachment C <br /> Groundwater Sampling <br /> Due to the presence of free product in well MW3, groundwater samples were only collected from wells <br /> MW1, MW2 and MW4 A minimum of three well casing volumes of water was purged from each well <br /> using a bailer prior to collecting groundwater samples The physical parameters of temperature, pH and <br /> • electrical conductivity were measured during the purging process All downhole equipment was <br /> decontaminated between wells using a solution of laboratory-grade detergent,then double rinsing in separate <br /> containers of clean rinse water <br /> Groundwater samples were collected using a dedicated, single-use, disposable bailer after the physical <br /> parameters had stabilized and water levels recovered to within 80% of their pre-purged levels The samples <br /> were placed into an ice chest cooled to approximately 4°C and transported to Argon Laboratories (FLAP <br /> 423 59)under chain of custody protocol Well purge logs are included in Attachment C <br /> GROUNDWATER ANALYTICAL RESULTS <br /> Groundwater samples were analyzed for VOCs, including oxygenated gasoline additives and the lead <br /> scavengers 1,2-dichloroethane (1,2-DCA) and ethylene dibromide (EDB) using EPA method 8260B No <br /> samples were collected from well MW3 due to the presence of free product <br /> No oxygenated gasoline additives, EDB or 1,2-DCA were detected in the groundwater samples collected <br /> from wells MWl,MW2,or MW4 PCE was detected in wells MW1,MW2,and MW4 at concentrations of <br /> 24 parts per billion(ppb), 19 ppb, and 17 ppb, respectively Chloroform was also detected in wells MW1, <br /> MW2, and MW4 at 4 4 ppb, 2 8 ppb, and 3 8 ppb, respectively MW1 and MW2 contained cis-1,2- <br /> dichloroethene at concentrations of 2 7 ppb and 2 1 ppb,respectively <br /> Only PCE was detected at levels exceeding its primary Maximum Contaminant Level (MCL) established by <br /> the State of California Department of Health Services The established primary MCL for PCE is 5 0 ppb <br /> Groundwater analytical results are summarized in Table 3 Attachment D contains laboratory reports and <br /> chain of custody documentation <br /> G 1Data\GROUNDZEIGABBARD`reporls11Q1v42002 doc <br />