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page 2 <br /> Drilling and sampling procedures <br /> and olfactory examination. Soil is described using the Unified Soil Classification System. <br /> A portion of this soil may be temporarily placed in a plastic bag and used for examination <br /> with a portable organic vapor analyzer. All field descriptions and measurements are <br /> documented on borehole logs. <br /> Ground-Water Monitoring Well Construction <br /> Ground-water monitoring wells are constructed according to the general specifications <br /> shown on the attached Well Construction Diagram. The wells shall extend a minimum of <br /> 10 feet into the upper aquifer, unless a clay layer greater than five feet in thickness is <br /> found. The wells shall not extend through a laterally extensive clay layer below the upper <br /> aquifer unless circumstances warrent the investigation of deeper aquifers. In the event an <br /> extensive clay layer must be penetrated care shall be taken to assure that mixing of water <br /> or contaminated soil does not occur. <br /> For single-cased wells, the monitoring well casing, with an end cap, shall extend to the base <br /> of the borehole or into a bentonite plug. The casings shall be factory perforated to the <br /> specifications delineated in the site work plan and compatible with the lithology of the <br /> aquifer found in the field. The perforated casing will extend five feet above the top of the <br /> aquifer or known high water level. Properly graded, clean filter sand will be used in the <br /> annulus of the well and prevent the migration of fine particles into the well. The filter sand <br /> will extend at three to five feet above the perforated interval in the well. A seal of at <br /> least three to five feet of bentonite shall be placed above the filter. Sack or neat cement <br /> will be used to seal the annulus from the bentonite pellets to the ground surface where a <br /> well box will be installed. All sand, bentonite, and cement will be placed with a tremie <br /> pipe. <br />