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Mr Mike Infurna <br /> Page 3 <br /> • Department (EHD) staff expressed concern that the inactive wellbore could function as a conduit for <br /> contaminant migration and directed that the well be properly destroyed <br /> The inactive water supply well was destroyed by perforating the casing with explosives and grouting <br /> with cement Prior to abandonment, the total depth of the well was measured by running a <br /> downhole video camera into the well to visibly ensure no obstructions were present The well was <br /> found to be 136 feet deep with perforations from 116-125 feet In order to perforate the well <br /> casing, detonating cord (with booster charges placed at 10-foot intervals) was placed in the well <br /> from total depth to 15 feet below grade Cement was then pumped into the well in one continuous <br /> operation until the well was full The water displaced by the cement was contained in the <br /> excavation surrounding the well, which was lined with plastic sheeting, and pumped into a DOT <br /> approved 55-gallon drum The dozer blade of a backhoe was placed over the well in order to <br /> contain the cement effected from the well when the charges were detonated <br /> After the charges were detonated, the well pad and upper well casing were removed using a <br /> backhoe More cement was added to the borehole until completely full The cement was allowed <br /> to spill and form a mushroom cap below ground surface Native soil was used to complete the <br /> excavation to grade Attachment B contains a copy of the well destruction permit issued by EHD, a <br /> copy of the Inspection Report Issued by EHD, and a copy of the well log created by Water Well <br /> Technologies using downhole video equipment <br /> GROUNDWATER ANALYTICAL RESULTS <br /> TPHg and BTEX compounds were not detected in the samples from wells MW5, MW7 and <br /> MW1D Benzene was not detected in well MW3 TPHg was detected in the samples collected <br /> from the remaining site wells at concentrations ranging from 470 parts per billion (ppb) in MW6 <br /> to 140,000 ppb in MW 1 Benzene levels in these wells ranged from 3 9 ppb in UH7 to 17,000 <br /> ppb in well MW 1 Analytical results are summarized in Table 2 Attachment C contains <br /> laboratory reports and chain of custody documentation <br /> EDB was not detected in any well The gasoline additive 1,2-DCA was not detected in wells <br /> MW3 and MW7 1,2-DCA was present in each of the other wells at concentrations ranging from <br /> 0 S ppb in MW1D to 1,700 ppb in MW1 MTBE was reported in the samples collected from <br /> wells MW6 and UH7 at low concentrations of 2 1 ppb and 0 S ppb, respectively TBA was <br /> detected in sample collected from well MW3 at a concentration of 13 ppb No other oxygenates <br /> or additives were detected Analytical results for oxygenates and additives are summarized in <br /> Table 3 Attachment C contains laboratory reports and chain of custody documentation <br /> SUMMARY <br /> All site monitoring wells were sampled Concentrations of petroleum hydrocarbons in the <br /> shallow, onsite monitoring wells were similar to those recorded in the past However, <br /> . concentrations of TPHg and BTEX in deep well MW 1 D have shown a dramatic decrease from <br /> previous monitoring events TPHg, ethylbenzene and xylenes have been non-detect in MW 1D <br /> G 1GROUNDZEIHARRYS\Repores\QMR1200513QM2005a doc <br />