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1 <br /> 6.2 Extent of Groundwater Contamination <br /> f <br /> The groundwater, which starts at seven feet below grade, is impacted with <br /> petroleum products. Four monitoring wells were installed. MW-1 is located 40 <br /> feet northwest of the tank site, MW-2 is located 60 feet southeast of the tank <br /> site, MW-3 is located 40 feet south of the tank site, and MW-4 is located 10 feet <br /> north of the tank site. MW-2 and MW-3 have remained non detect for TPH-G during <br /> the different sampling periods. MW-1, which was positive for TPH-G, has shown <br /> a slight decline in levels from 200 ppb, to 170 ppb, to 160 ppb. MW-4 has the <br /> heaviest concentrations of TPH of all the existing monitoring wells. It has also <br /> shown a decline from free product in 1992, to 4500 ppb and then 4100 ppb in 1993. <br /> Water samples were also taken from sax of the seven soil borings. Sample results <br /> found no contamination at 60 feet north of the tank site (BH-1) and 20 feet east <br /> of the tank site (BH-3). Contamination was observed 10 feet east of the tank <br /> site at 3100 ppb of TPH (BH-2) , 30 feet west of the tank site at 20,000 ppb TPH <br /> (BH-6), 10 feet northwest of the tank site at 160,000 ppb of TPH (BH-4) , and 10 <br /> feet southwest of the tank site at 300,000 ppb of TPH (BH-5). <br /> I 7. 0 PROPOSED REMEDIATION WORK PLAN <br /> 71. Soil Contamination <br /> Pacific Ram Environmental proposed to remediate the contaminated soils at the <br /> same time as the site will be characterized. Appendix III shows the suspected <br /> area contaminated. Soil boring BH-3 and BH-7, which were non detect, are on the <br /> edge of the suspected area and they define the outh&rn and western lateral_ <br /> extent of the soil plume. The soil area north and west of the tank ate have <br /> not been fully characterized. `��^ <br /> During the remediation of the soil plume an additional 60 borings will be <br /> constructed within the suspected contaminated area. Barings will first be <br /> constructed around the property boundaries. Soil borings will move toward the <br /> tank removal site, the suspected contaminated area, in ten feet increments. As <br /> soon as a detectable amount of contamination is observed, this boring will be <br /> marked as the lateral extent of the plume. Additional borings, at five feet <br /> increments, will then be constructed, as specified in the remediation plan. All <br /> i soil found inside the lateral boundaries of the plume will be considered <br /> contaminated and will be remediated. <br /> If soil borings indicate that the contamination is not coming from the tank <br /> excavation area, all construction of additional borings, or soil remediation will <br /> cease. Barings will then be constructed to determine the new location of the <br /> contaminants and this information will be detailed in the Site Assessment Report. <br /> 7. 2 Water Contamination <br /> Pacific Rim Environmental have agreed to remediate the contaminated groundwater <br /> at the same time as the site will be characterized. Appendix III shows the <br /> suspected areas of water contamination. Since the existing monitoring wells MW- <br /> 2 and MW-3 are non detect, this will be rpnr-th and eastern extent of the ,�� <br /> contaminated plume. M-1 will be considered the western ex ent of the plume. <br /> MW-1 is not at non detect, but since it is on the edge of the property lane, it� <br /> should be assumed that the plume is not traveling in this direction. <br /> 3 <br />