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L, .s <br /> I.H. KLEINFELDER & ASSOCIATES <br /> File: 24-2038-1/28:725 <br /> December 10, 1986 <br /> Page 4 <br /> San Joaquin Local Health District. A copy of the permit is included in <br /> Appendix B of this report. The wells were completed using two—inch inside <br /> diameter, flush—threaded joint, schedule 40 PVC pipe. Well screen <br /> sections were performed with 0.020—inch factory—cut slots. The screened <br /> section was set at a depth 20 feet below and 5 feet above the depth where <br /> ground water was first encountered. The PVC pipe was steam—cleaned prior <br /> to installation. The annular space between the pipe and the wall of the <br /> boring was backfilled with clean Lone Star Industries #2/12 Monterey sand <br /> to approximately two feet above the top of the perforated section. A <br /> three—foot bentonite plug was placed above the sand pack to provide a seal <br /> against surface water infiltration. The remaining annular space was <br /> filled with sand/cement grout to the surface. Each well was secured with <br /> a locking well cover. Construction diagrams of each well are shown on <br /> Plate Nos. 4 and 5. While installing monitoring well MW-1, construction <br /> material bridged inside the hollow stem auger and the PVC casing was <br /> pulled up eleven feet above the intended depth. Although the screen <br /> section in MW-1 was set higher than originally intended, the well was <br /> completed as a useful ground water monitoring well. <br /> 5.5 Monitoring Well Development and Sampling Procedures <br /> .. Monitoring wells MW-1 and MW-2 were developed on November 5, 1986. <br /> Each well was first sampled with a clear acrylic bailer to visually <br /> inspect the sample for a product layer or sheen. No product layer or <br /> sheen was observed on the water samples bailed from the monitoring wells. <br /> The wells were developed with a surge block/air lift tool. Surging with <br /> the tool along the screened interval of the well was performed to draw the <br /> silts and very fine sands from the formation into the well. The sediment <br /> laden water was airlifted from the well at a rate of approximately 0.75 <br /> gallons per minute (gpm) . Each well was developed until the discharge <br /> water ran relatively clear of fines. Approximately 6.25 well volumes were <br /> removed from monitoring well MW-1 and 10.75 well volumes were removed from <br /> monitoring well MW-2. <br /> Monitoring wells MW-1 and MW-2 were purged and sampled on November <br /> 14, 1986. After the depth to static water was measured, each well was <br /> purged and sampled with a submersible ISCO bladder pump. Five well <br /> volumes were removed from each well before a water sample was collected. <br /> — Water samples MW-1 and MW-2 were collected in one 1—liter bottle and three <br /> 40—mil VOA bottles. The sample bottles were immediately sealed and placed <br /> in an iced cooler. At the end of the field day, the two water samples <br /> were delivered to California Analytical Laboratories/ENSECO in West <br /> Sacramento, California. The analytical results and a completed copy of <br /> the chain—of—custody form are included in Appendix B of this report. <br /> To prevent cross—contamination, all developing and sampling equipment <br /> was steam cleaned prior to use in each monitoring well. Additionally, a <br /> warm trisodium phosphate solution and clean water were pumped through the <br /> sampling equipment prior to the collection of subsequent samples. <br />