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AUG 17 '99 15: 11 FR LFR ROSEVILLE 916 79G 0366 TO 9-12094683433 R.06/oe <br /> LFR Levine-Fricke • • DRAFT <br /> Each SVE well and the groundwater monitoring well will be constructed using 2-inch <br /> inside-diameter polyvinyl chloride (PVC) casing. The perforated interval of each well <br /> will consist of 0.02-inch factory-cut slots. After installing the casings in the hollow-stem <br /> auger, number 3 size sand pack will be placed in the annular space from the bottom of <br /> the boring to approximately 1 foot above the top of the slots. Bentonite pellets will then <br /> be placed above the sand pack and hydrated to prevent the entrance of grout into the <br /> sand pack. A cement bentonite grout will be placed from the top of the bentonite pellets <br /> to the ground surface. A traffic rated well vault will then be cemented in place at each <br /> SVE well to allow for future piping to the well heads. A tamper resistant steel stovepipe <br /> will be installed at the monitoring well location extending approximately two feet above <br /> grade. After completion, the monitoring well will be developed using a surge block and <br /> a bailer until the turbidity of the water appears relatively clear. <br /> Soil cuttings generated during drilling activities will be temporarily stored on-site in <br /> DOT approved 55-gallon drums pending waste characterization. Decontamination and <br /> well development water generated during drill activities will be placed in the GWET <br /> system for treatment. <br /> Task 3:Testing of the Soil Vapor Extraction Well Network <br /> Testing will be conducted of the newly installed SVE system to help select the size and <br /> type of soil-vapor treatment equipment. Testing will include applying a vacuum to each <br /> SVE well through a common manifold and measuring the vacuum with respect to time <br /> at each well head_ The pressure (vacuum) and the extracted vapor flow rate will be <br /> recorded for subsequent interpretation. <br /> One soil-vapor sample will be collected from the manifold area and each well head at <br /> startup, after the pressure in soil in the vicinity of the wells has reached equilibrium, <br /> and at the end of the test. The vapor samples will be collected into one-liter summa <br /> canister pending chemical analyses. These samples will be analyzed for fixed gases <br /> using ASTM D 1946 and TPHg, BTEX, and MtBE using EPA Method TO-3. Analyses <br /> of the soil-vapor samples will be performed by Air Toxics of Folsom, California, a <br /> state-certified laboratory. <br /> KMEP will obtain authorization from the SJCAPCD prior to conducting SVE pilot and <br /> inform the SJCAPCD of pollution control measures implemented during testing <br /> activities. <br /> Task 4: Surface-Water Sample Collection <br /> Surface-water monitoring data from stations S-1 and S-2 on Trapper Slough (Figure 2) <br /> have occasionally indicated the presence of very low concentrations of BTEX <br /> compounds (highest concentration of 1.3 parts per billion(ppbl xylenes, August 1996) <br /> and MtBE (highest concentration of 2.6 ppb, March 1997). As requested by the <br /> 12WQCB, surface-water samples from Trapper Slough will be collected at and in the <br /> vicinity of the site to evaluate whether these detections of BTEX compounds and MtBE <br /> page 12 holc.ger.wp:EBF <br />