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Supplemental Investigation Report,Problem Assessment Report and Work Plan <br /> Cleanup and Abatement Order No 5-00-707 _ EAI Proiect No 1232 <br /> A Mini Rae photoionization detector (PID), or equivalent instrument, will be used on the soil <br /> sample contained in the second tube from the bottom of the shoe at each sampling interval <br /> within the borings, to determine if volatile hydrocarbon vapors are emanating directly from the <br /> soil Each sample will be placed in an airtight "Ziploc" plastic bag The samples will be <br /> allowed to sit for a minimum of five minutes, and then the headspace in the bags will be <br /> analyzed using the PID The results of this field-testing will be recorded on the boring logs <br /> 5 12 Ground Water Monitoring Wells <br /> Each boring will be converted into a four-inch inside diameter flush-threaded Schedule 40 <br /> polyvinyl chloride (PVC) ground water monitoring well All well casing materials will be <br /> steam cleaned prior to installation The shallow wells will terminate at 50 feet bgs, and will be <br /> slotted between 30 and 50 feet bgs The deep wells will terminate at 70 feet bgs, and will be <br /> slotted between 50 and 70 feet bgs The annular space between the borehole wall and well <br /> casing will be backfilled using grade #3 Monterey sand to approximately one foot above the <br /> slotted section A surge block will be used to settle the sand pack and partially develop the <br /> well An approximate three-foot bentonite seal will be placed on the sand pack and the boring <br /> will be grouted to the surface using and cement/bentonite grout, and a flush mounted traffic <br /> grate will be placed over the well <br /> Development <br /> The wells will be allowed to set from construction activities for at least 48 hours, prior to <br /> development The wells will be developed until the water is relatively free of settleable solids <br /> Surveying <br /> To establish an elevation for each well, all well casing elevations will be surveyed to a <br /> benchmark or other point of fixed elevation under the supervision of a registered civil engineer <br /> or registered surveyor <br /> Sampling <br /> Ground water samples will be collected from all wells for analytical testing Prior to <br /> completing any purging or sampling activities, depth measurements to fluid levels in each well <br /> will be obtained using an interface probe accurate to 0 01 foot <br /> Prior to collecting ground water samples from the wells for analytical testing, the wells will be <br /> purged of three to four well casing volumes of water using a down-hole pump Temperature, <br /> conductivity, turbidity and pH readings will be recorded to evaluate the effectiveness of <br /> purging activities The samples will be collected from lust below the water surface using <br /> disposable bottom bailers equipped with volatile organic compound (VOC) sampling tips Use <br /> of these bailers precludes the potential for cross-contamination <br /> HS 11321 ERW_WP -14- <br /> FNVIRONMENTi4t AUDIT', INC., <br />