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Ripona Market October 28,2004 <br /> Corrective Action Plan <br /> unstable and often flowed into the borehole under hydraulic pressure The <br /> "heaving sands" flowing into the open augers restricted the insertion of the drill <br /> bit and sampling tools As noted on the logs "heaving sands" prevented the <br /> collection of soil and water samples at several of the planned intervals <br /> Groundwater flow has been consistently to the northeast with a shallow gradient <br /> as shown in the Figure 4 August 2004 map of groundwater elevations <br /> Groundwater elevations have fluctuated between 35 and 42 feet A cumulative <br />' hydrograph of the site groundwater elevations is shown in Figure 8 <br /> 3.0 Contamination Characteristics <br /> 3.1 Soil Contamination <br />' Gasoline hydrocarbons and aromatic compounds were not detected in any of the <br /> soil samples collected in the exploratory bonngs Moderate concentrations of fuel <br /> oxygenates were detected in soil samples collected at depths of 25 and 30 feet in <br /> bonngs located in the vicinity of the former underground storage tanks An <br /> MTBE contamination cross section is shown as figure 6 <br />' 3.2 Groundwater Contamination <br /> Very low concentrations of toluene were detected in Boring B2 (0 5 ug/l @ 60 <br /> 10 ft), Boring B3 (1 1 ug/l @ 38 ft ) and Bonng B4 (1 9 ug/1 @ 45 ft ) Very low <br /> concentrations of gasoline were detected in Boring B4 (0 07 mg/l @ 45 ft) <br /> I Moderate concentrations of MTBE were detected in a water sample collected <br /> from well MW-2 located adjacent to the former underground storage tanks Trace <br /> concentrations of MTBE were detected in a water sample collected from the deep <br /> I well, MW-4 MTBE groundwater contamination is shown in map view in figure <br /> 6 and in cross section in figure 4 MTBE groundwater contamination is limited to <br /> the vicinity of well MW-2 and defined vertically at a depth of 55 to 60 feet <br /> vertically <br /> 3.3 Contaminants of Concern <br /> Contaminants of concern have been identified as MTBE probably sourced from <br /> the former underground storage tank as been identified as a potential <br /> carcinogen and has demonstrated taste and odor impacts on water quality <br /> Laboratory analyses have consistently reported MTBE with the highest <br /> concentration of all analytes All plume modeling and fate and transport modeling <br /> was conducted using MTBE <br /> 3.4 Contaminant Distribution <br /> MTBE contamination is limited to in area immediately around the former <br /> underground storage tanks Soil impacts were detected at the water table in a <br /> 7 <br />