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screened interval below the water table. Caution will be exercised not to drill through <br /> any aquitard below the'water table. If groundwater is not encountered before a depth of <br /> 40 feet below ground surface, or hard rock is encountered before 40 feet, then the boring <br /> will be completely filled from bottom to top with a grout mixture of 95% cement/5% <br /> bentonite, applied by tremie pipe under pressure: <br /> During soil-boring operations, soil samples will be collected at least every 5 feet with <br /> a split-spoon sampler. This will involve 3 1/2 feet of boring followed by 1 1/2 feet of <br /> sampler drive. In addition, soil samples will be collected at any significantly discernable <br /> change in lithology, and just above the water table, if possible. Samples below the water <br /> table will not be collected. <br /> During soil-boring operations, geological descriptions of the soil will be made by an <br /> on-site geologist, and an appropriate soil-boring log will be constructed and submitted <br /> ' with the final report. <br /> Soil samples will be collected in brass tubes by the split-spoon sampler. The ends of <br /> each tube will be covered with Teflon tape and then capped with plastic caps. The caps <br /> w • will be sealed with electrical tape. (�glneae t] <br /> The most contaminated soil sample and/or the deepest sample above the water table <br /> from each boring will be submitted for laboratory analysis. The most contaminated <br /> sample will be determined by field OVA. For each sampling point, soil will be preserved <br /> in glass jars filled approximately 1/2 full, and the jar mouth covered with aluminum foil <br /> and then capped. The jars will be allowed to sit for a minimum-of 20 minutes before <br /> insertion of an OVAp robe through the aluminum foil into the headspace of the soil <br /> sample. The sample depth with the highest OVA readings.'will be chosen as the depth for <br /> -�; sample analysis using the corresponding brass-tube sample. If all OVA readings in a <br /> well are zero, then the sample nearest to and above the water table will be analyzed. <br /> All soil samples submitted to the laboratory will be analyzed for BTX&E per EPA <br /> Method'8020, and for TPH per DHS/LUFT Method. Analytical results will be submitted <br /> in the final written report. <br /> Hollow-stem augers used in boring operations will be.decontaminated by steam- <br /> cleaning methods between each boring. Also, the split-spoon sampler will be <br /> decontaminated between each sampling point. <br /> I <br /> 3.4 Well Construction <br /> If groundwater is encountered, the soil boring(s) will be. converted to a monitoring <br /> well. Wells will be constructed (see Figure 4) using 4-inch diameter PVC casing <br /> designed with screw-type,flush joints. No solvent,cement, glue, screws, nor mechanical <br /> adaptors will be used at the casing joints. <br /> Each monitoring well will have a single screened interval of 15 feet, with 5 feet of <br /> screen above and 10 feet of screen below the water table. The screen slot size will be <br /> either 0.010-in. or 0.020-in depending on the size distribution of matrix materials. A <br /> PVC cap will be affixed to the bottom of the screened interval. <br /> -8- <br /> 172-32.R] 318191 <br />