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II Ms Vicki McCartney April 4, 2406 i <br /> Page 2 <br /> vrn <br /> • <br /> Five Direct Push (DP) borings (GP-1 through GP-5) were made in August 2001' The borings were advanced <br />' to groundwater, and a discrete water sample was collected from each <br /> Three groundwater monitoring wells (MW-1 through MW-3) were installed in September 2000 (Figure 1) <br /> Quarterly groundwater monitoring and sampling was initiated in September 2000 <br /> In May 2002, one deep soil boring was made and two shallow sod borings were made and converted into <br /> monitoring wells MW-4 and MW-5 A dual-phase extraction (DPE) test was conducted from June 10 through <br /> 15, 2002 The DPE test was conducted by simultaneously extracting soil vapor and groundwater from well <br /> e MW-1 <br /> Four cone penetration tests (CPT) were conducted in September 2003 Discrete groundwater samples <br /> collected from HydroPuncho borings made adjacent to the CPT borings indicated the presence of methyl tert- <br />' butyl ether(MTBE) and benzene in groundwater northeast of the property beneath a city street <br /> In October 2004, Shaw submitted the Corrective Action Plan for Parkinson's Hammer 1-5 Arco(CAP) The <br /> CAP was tentatively approved, pending results from a deeper monitoring well located in the street east of the <br /> station and submission of contaminant mass calculations These activities are currently in progress <br /> Routine groundwater monitoring has been performed at the site since September 2000 There are five <br /> groundwater monitoring wells at the site, all with total depths of approximately 24 feet <br /> Groundwater Monitoring <br />' On October 17, 2005, groundwater samples and depth-to-water data were collected from monitoring wells <br /> MW-1 through MW-5 Groundwater samples were analyzed for total petroleum hydrocarbons as gasoline <br /> (TPHg), benzene, toluene, ethylbenzene, and xylenes (BTEX), 1,2-dibromoethane (EDB), 1,2-dichloroethane <br /> (1,2-DCA), and five gasoline oxygenates MTBE, di-isopropyl ether (DIPE), ethyl tert-butyl ether (ETBE), tert- <br /> amyl methyl ether (TAME), and tert-butyl alcohol (TBA) using U S Environmental Protection Agency(EPA) <br /> Methods 8015M/8021 B and 8260B Field and laboratory procedures are presented in Attachment 1 <br />' Certified analytical reports, chain-of-custody documentation, and field data sheets are presented in <br /> Attachment 2 <br />' Elevations and Gradient <br /> Groundwater elevations measured at the site were an average of 0 87 feet lower than measured in the <br />' previous sampling event of July 18, 2005 Groundwater flow was inferred to be to the northeast at an <br /> average gradient of 0 001, which was consistent with previous sampling events Groundwater elevation data <br /> are presented in Table 1 A groundwater elevation contour map based on the October 17, 2005, data is <br />' shown on Figure 1 <br /> Final Concentrations <br /> TPHg-range hydrocarbons were reported in samples from wells MW-1 and MW-3 at concentrations of 1,500 <br /> • micrograms per liter(µg/L) and 110 pg/L, respectively Benzene was reported in the samples from wells <br />' N 7-hPub18M01A A=\2005 RplsNQ4M4 da Shaw Environmental,Inc <br />