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tevine4ficke-fle(gIn <br /> ENGINEERS.HYMOGEOLOCISTS A AppLIEdE <br /> Based on these data, we may decide to construct a multiple-completion well cluster in the borehole <br /> to facilitate monitoring of each of the major permeable layers in the B-zone. At a minimum, we are <br /> Proposing to construct new monitoring well which would screen the lowest permeable zone within <br /> the B-zone aquifer. The final evaluation of the integrity and appropriateness of MW-21 would be <br /> performed after completion of this well installation. <br /> Based upon LFR's success in collecting groundwater samples from the B-zone aquifer during the <br /> Plume perimeter pilot boring and monitoring <br /> discrete depth groundwater samples in well installation program, LFR recommends that <br /> the vicinity of MW-21 be obtained from a mud-rotary pilot <br /> boring using a PIPP sampler. LFR does not plan to use cone penetrometer testing (CPT)/PIPP <br /> technology, as recommended by LPL in its March 31, 1997 letter, for the following reasons: <br /> • While CPT/PIPP sampling using a direct-push CPT rig may be capable of reaching the upper <br /> water-yielding unit in the B-zone aquifer(approximately 90 to 95 feet bgs in the MW-21 <br /> boring), neither LFR nor the CPT subcontractor, Gregg In Situ, Inc., believe that a CPT rig <br /> will be capable of reaching the bottom water-yielding unit in the B-zone aquifer (approximately <br /> 135 to 138 feet bgs in the MW-21 boring). <br /> • MW-21 is located in an area where A-zone groundwater contains high concentrations <br /> (exceeding 2,500 micrograms per liter) of tetrachloroethylene. The ability to completely grout <br /> the CPT/PIPP borings to 140 feet (the total depth of the borings) is uncertain. This uncertainty <br /> exists because the CPT rods must fust be completely removed from the hole and a set of <br /> grouting rods must be pushed down the same hole. The resulting open hole could potentially <br /> collapse or permit cross contamination between the A- and B-zone aquifers. <br /> • Mud rotary drilling combined with the installation of a permanent conductor casing through the <br /> overlaying A-zone is considered the optimum method to minimize the potential for cross <br /> contamination between the A- and B-zones. Conductor casing would facilitate installation of a <br /> replacement monitoring well, if necessary. <br /> The proposed field program to evaluate the groundwater quality distribution in the vicinity of <br /> MW-21 is designed to minimize the disruption to the operations of Lincoln Center. The proposed <br /> program would also minimize the quantity of waste generated, reducing the costs associated with <br /> disposal of contaminated drilling mud. To meet these goals, a single conductor casing would be <br /> installed for the boring through the A zone so that a range of monitoring well completions could be <br /> constructed in the B zone. Constructing either a single well or, if appropriate, multiple completion <br /> B-zone wells in this manner would greatly reduce the time typically required to install multiple <br /> wells in separate boreholes. <br /> Our recommended method for drilling the B-zone boring and collecting PIPP groundwater <br /> samples, well construction methods, a proposed sampling schedule, and a traffic control plan for <br /> the work are presented below. Background and data evaluation discussions related to this <br /> investigation were presented in LFR's March 18, 1997 letter. <br /> LCM W21-3.LTR:SRL 2 <br />