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Mr. Chris Dressel <br />S61072.400.0002 <br />January 27, 2014 <br />Page 4 <br />evaluating where off -Site sources may be contributing to the groundwater impacts that have been <br />observed at the Site. <br />In addition, groundwater samples from nested temporary locations at up to eight additional locations <br />downgradient (i.e., north and east of the Site) are proposed to be collected from within City right -of -way <br />in Lafayette Boulevard and in the vicinLWRI \W ",vy 7RwHr" SrRSHrWDnd from within City right -of -way in <br />Main Street between the railroad tracks and Monroe Street to evaluate the downgradient distribution of <br />chlorinated VOCs. <br />In general, our proposed approach entails defining the vertical extent of chlorinated volatile organic <br />compounds (VOCs) upgradient of AMW -1 S (shallow), AMW -11 (intermediate), and AMW -1 D (deep) <br />(located at the immediate southwest corner of the Site) by installing four relatively shallow, intermediate, <br />and relatively deeper temporary sampling points (installed at four nested sampling locations) within the <br />area generally bounded by hendall Street (and alley to the west), Edward Street, Scott Street, and <br />Indiana Avenue south and west of the Site; then installing relatively shallow and relatively deeper <br />temporary sampling points in the vicinity of Lafayette Boulevard (4 nested sampling points) and Main <br />Street (4 nested sampling points) as discussed above. <br />This task will begin with the advancement of temporary screens using direct -push technologies (e.g., a ST- <br />15 Hydropunch) to a shallow depth (i.e., 26 to 30 feet below ground surface (bgs)), an intermediate depth <br />of approximately 35 to 39 feet bgs, and, for upgradient locations, at a deeper depth of approximately <br />45 to 49 feet bgs, subject to approval of these IocationVlrRP V1N &O-bVVBRDrGRI 3uEU : RrIW(B3: ). <br />The locations may be adjusted slightly in the field based on field observations such as utility locations, etc. <br />Hull will work with the drilling subcontractor and the appropriate City and St. Joseph County authorities to <br />arrange for access for the work and to clear utilities and to prepare appropriate permits for drilling in the <br />right -of -way. Adjacent property owners will be notified by certified mail prior to the initiation of any <br />drilling activities. Drill cuttings and sample purge and decontamination water will be containerized and <br />placed at a location designated by the City. <br />At each location where groundwater sampling is to be conducted, the borehole will initially be advanced <br />to the deepest depth proposed for that location, at which point the outer casing of the sampling system will <br />be withdrawn to expose a four foot long stainless steel wire wrapped screen. Once the screen is exposed, <br />Hull will measure the static water level and lower a decontaminated Waterra foot -valve sampling pump or <br />peristaltic pump to purge the equivalent of five well volumes of water to develop the aquifer surrounding <br />the screen. Following extraction of each well volume, Hull will measure pH, temperature and conductivity <br />to demonstrate that representative groundwater is being samplHd. ,n addition, Hull's rHprHsH ntativH will <br />note if there is a visible sheen on the extracted water. After development, the temporary well will be <br />allowed rest for approximately 20 minutes prior to sample collection. Following purging, Hull will collect <br />groundwater samples that will be pumped through the Waterra or bladder pump tubing at a flow rate of <br />less than 100 ml/min. pamples will be transferred directly into laboratory - preserved sample containers <br />and placed on ice in a cooler. <br />Following collection of each sample, Hull will retrieve and decontaminate the Waterra foot -valve pump by <br />washing it with Alconox and water and rinsing it with deionized water. In addition, the sample tubing will <br />be replaced between each sampling interval. The groundwater sample in the upper portions of the <br />aquifer (i.e., shallow and intermediate, as appropriate) will be collected by withdrawing the screen to the <br />appropriate depth and purging and collecting a groundwater sample as described above. The process <br />for purging and collecting the relatively shallower groundwater sample will then be completed as <br />