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.� Mr. Stephen S. Chen Ooposal 8807-03 <br /> August 29 1988 <br /> Page 2 <br /> Monitoring Well MW-2 is located to be representative of ground-water <br /> quality in a northeasterly direction from the landfill . Monitoring <br /> Well MW-3 is located to be representative of ground-water quality in <br /> an easterly direction from the landfill . <br /> A review of the data collected from a soils investigation at the site <br /> (Soils InvestJation French Camp Sanitary Landfill Site, J.H. <br /> Kleinfelder & Associates; 1974) indicated that the depth to ground <br /> water in 1974 was approximately 30 feet. EMCON proposes that the <br /> monitoring wells be installed to final depths of approximately 20 feet <br /> below first-encountered ground water. Our drilling depth estimate <br /> considers that the ground-water level may have dropped since 1974 <br /> because of pumping in the Stockton area and that the ground surface at <br /> the site may have been built up by soil filling operations. To <br /> estimate a drilling depth EMCON has assumed a total of 210 feet <br /> (3 wells, 70 feet deep each) . <br /> A well drilling permit will be obtained from the San Joaquin Local <br /> Health District, before commencing any drilling. The drill holes will <br /> be advanced using hollow-stem auger drilling equipment. The wells <br /> will be constructed of 2-inch diameter polyvinyl chloride (PVC) casing <br /> and screen. The annular space between the drill hole and the well <br /> screen will be filter packed with a graded sand. A bentonite seal <br /> will be placed above the filter pack. The remaining annular space <br /> will be pressure grouted with a cement-bentonite mixture from the top <br /> of the bentonite seal to the ground surface using a tremie pipe. A <br /> locking steel well cover will be placed over the well casing and <br /> secured with concrete. <br /> An EMCON geologist will log soil samples from the drill hole according <br /> to the Unified Soil Classification System and standard geologic <br /> techniques. Soil samples for logging will be obtained from auger- <br /> return materials and by advancing a modified California split-spoon <br /> sampler equipped with stainless steel liners into the undisturbed soil <br /> beyond the tip of the auger. An exploratory boring log and a con- <br /> struction details data sheet will be prepared for each monitoring <br /> well . <br /> Two soil samples will be collected for vadose zone chemical character- <br /> ization. One soil sample will be collected from MW-1; the second <br /> sample will be collected from either MW-2 or MW-3. The soil samples <br /> for chemical analysis will be collected in stainless steel liners and <br /> sealed with Teflon tape and plastic caps. The liners will be placed <br /> in glass jars, packed on ice, and delivered to EMCON's laboratory with <br /> appropriate chain-of-custody documentation. EMCON proposes to analyze <br /> the soil samples for the following man-made compounds: <br /> • Volatile organic compounds by EPA Method 8240 <br /> • Semivolatile organic compounds by EPA Method 8270 <br />