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' calibrated prior to commencement of the field activities To establish the OVL, soil <br /> from each sample interval will be placed into a sealed container with headspace to allow <br /> for volatilization Prior to obtaining the measurement, the sort will be allowed to stand <br /> at ambient air temperatures for approximately 15 minutes At the end of this time the <br /> probe of the PID/FID will be inserted into the container and the sample OVL will be <br />' measured and recorded on the boring logs <br /> During drilling operations, a modified split-spoon sampler (sampler) will be used to <br />' retrieve soil samples Pre-cleaned brass sleeves are placed inside the sampler and the <br /> sampler is then driven to the desired sampling depth The sampler is then recovered <br /> from inside the boring and the brass sleeves retrieved The brass sleeves will be used to <br /> evaluate soil type and to measure OVLs present in the sample interval Soil type and <br /> OVLs will be recorded on the boring logs Procedures for PID calibration and OVL <br /> monitoring will be followed as described in the previous section Soil cuttings, if any, <br /> will be placed in properly labeled 55-gallon drums and stored on site pending disposal <br /> A 4 Groundwater Sampling <br />' Groundwater samples will be collected using a Hydropunch— or similar sampling <br /> device The Hydropunch— will be pushed into the water-bearing zone by the drill ng and <br /> the water sample will be collected from the Hydropunch— using a clean, Teflon bailer and <br /> will be transferred to pre-cleaned bottles provided by the laboratory All samples will be <br /> stored in a cooler containing ice for transport under proper cham-of-custody protocol to the <br /> laboratory A maximum of 45 minutes will be allowed for a sufficient volume of <br />' groundwater to collect in the Hydropunch-prior to advancing to the next depth <br /> All groundwater sampling equipment will be thoroughly cleaned prior to and following <br /> use All decontamination water will be placed in 55-gallon drums, which will be properly <br />' labeled and left on site pending disposal <br /> A 5 Piezometer Installation <br />' The nested piezometers will each consist of 1-arch diameter schedule 40 PVC <br /> casing with a 5-foot screen interval of 0 020-inch slotted casing The exact depth of the <br />' screen mtervals will be determmed by the field geologist based on site-specific lithology <br /> and constituent distribution information Lonestar 93 sand, or equivalent, will be used as <br /> the filter pack adjacent to each screened interval and will extend a minimum of 2 feet <br />' above and b inches below the screened interval If possible, a minimum of 10 feet of a <br /> cement/bentonite grout mixture will be tremaed into the borehole to separate the shallow <br /> and deep screened zones A bentonite seal comprised of a minimum thickness of 3 feet <br />' will be tremaed into the borehole above the upper filter pack, followed by a <br /> cement/bentonite grout mixture tremied into the remaining portion of the annular space <br /> The borehole will be completed at the surface with a traffic-rated well monument <br /> 1 <br /> ARCADIS GERAGHTY&MILLER <br />