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Mr Dann L Rouse <br /> Exxon Company, U S A <br /> August 4, 1999 <br /> Page 3 <br /> Between May 26 and 27, 1999, Delta geologists observed Woodward Drilling advance eight soil <br /> ' borings and complete two of them as ground water monitoring wells onsite Soil borings SB-4 through <br /> S13-9 were advanced in the vicinity of the former UST basin to depths ranging from 26 5 to 36 5 feet <br /> bsg The borings for monitoring wells MW-9 and 1AW-10 were each advanced to a depth of 26 5 feet <br /> ' bsg The locations of monitoring wells and soil borings are shown in Figure 2 Each boring location <br /> was sampled and logged at a minimum vertical interval of five feet Sol] samples collected in the field <br /> were logged according to ASTM 2488-84 Unified Soil Classification System, visual manual method <br /> ' Additionally, each sample was screened in the field for the presence of petroleum hydrocarbon vapors <br /> using a Photoionization Detector(PID) Soil boring logs were prepared for each boring and are included <br /> as Enclosure C The boring logs included descriptions of soil types encountered, PID readings and <br /> methods used to advance and maintain the borings <br /> All ,oil samples collected were submitted to Sequoia Analytical (a Cali tom ia-certified laboratory) in <br /> Redwood City, California for analysis of benzene, toluene, ethylbenzene, and total xylenes (BTEX) <br /> ' using EPA Method 8020, total purgeable petroleum hydrocarbons (TPPH) as gasoline using EPA <br /> Method 8015 Modified, and methyl tertiary butyl ether(MTBE)using EPA Method 8260 Selected soil <br /> tramples were additionally analyzed for fuel oxygenates tertiary amyl methyl ether, tertiary butyl <br /> ' alcohol, di-isopropyl ether, 1,2-dibromoethane, 1,2-dichloroethane, ethanol, ethyl tertiary butyl ether, <br /> and MT BE by EPA Method 8260B <br /> 1bSoil Sample Analytical Results <br /> Soil samples collected from the boring for MW-9 were below the laboratory's reporting limits for all <br /> ' analyte , Samples from the soil boring for MW-10 were below the laboratory's limits for all analytes <br /> with the exception of MTBE reported at 0 018 milligrams per kilogram (mg/kg) in the soil sample <br /> collected at 16 5 feet bsg Benzene was detected in samples identified as SB-5-16 5 and SB-5-26 5 at <br /> ' 0 0831 mg/kg and 0 00367 mg/kg, respectively Detectable concentrations of TPPH as gasoline were <br /> reported in soil samples collected from the borings for SB-4, SB-5, S13-8, and SB-9 at concentrations <br /> ranging from 0 864 mg/kg (SB-4-11 5) to 797 mg/kg (SB-9-11 5) MTBE was reported in soil samples <br /> ' collected from borings for SB4 through SB-8 at concentrations ranging from 0 0056 mg/kg (SB-6-31 5) <br /> to 0 863 mg/kg(SB-4-16 5) Cumulative soil sample analytical results from drilling events by Delta are <br /> summarized in Table 1 Copies of the laboratory analytical reports with chain-of-custody <br /> documentation for the current drilling event are included in Enclosure C <br /> Well Construction Development,Measurements and Sam lin <br /> ' Groundwater monitoring wells MW-9 and MW-10 were each installed to a depth of 20 feet bsg Each <br /> well was constructed of 2-inch diameter flush threaded Schedule 40 PVC casing and screened with <br /> ' 0 010 machine slotted casing The screen interval begins at 5 feet bsg and extends to 20 feet bsg The <br /> annular space of each well was filled with No 2112 Lonestar sand from the total depth drilled to <br /> 6 inches above the top of the screen interval and a 1 foot bentonite seal was emplaced above the filter <br /> ' pack The remaining annulus was filled with a cement grout containing approximately 1-percent <br /> bentonite to within six inches of surface grade Monitoring wells MW-9 and MW-10 were completed at <br /> the surface with a flush grade 8-inch diameter traffic-rated well box set in concrete dyed to match the <br /> existing asphalt surface Well construction details are illustrated in Enclosure D <br />