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SOIL SAMPLE HANDLING <br /> Soil sample handling follows the same basic protocol for both drilling and excavation activities. <br /> Upon retrieval, soil samples are immediately removed from the sampler, sealed with Teflon <br /> sheeting and polyurethane caps, and wrapped with tape. Each sample is labeled with the project <br /> ' number, boring/well number, sample depth, geologist's initials, and date of collection. After the <br /> samples have been labeled and documented in the chain of custody record, they are placed in a <br /> cooler with ice at approximately 4 degrees Celsius (`C) prior to and during transport to a state- <br /> certified laboratory for analysis. Samples not selected for immediate analysis may be transported <br /> in a cooler with ice and archived in a frostless refrigerator at approximately 4°C for possible <br /> future testing. <br /> ' MONITORING WELL INSTALLATION <br /> Monitoring wells are constructed of 4-inch-diameter, flush-threaded Schedule 40 PVC blank and <br /> screened (0.020-inch slot size) casing. Where possible, the screened interval will extend at least <br /> 10 feet above, and 10 to 20 feet below, the top of the groundwater table. The annular space <br /> ' surrounding the screened casing is backfilled with No. 3 Monterey sand (filter pack) to <br /> approximately 2 feet above the top of the screened section. <br /> ' During well construction, the filter pack is completed by surging with a rig-mounted surge block. <br /> A 3-foot-thick bentonite annular seal is placed above the filter pack. The remaining annular <br /> space is grouted with Portland cement and/or bentonite grout to the surface. Utility access boxes <br /> are installed slightly above grade. Locking, watertight caps are installed to prevent unauthorized <br /> access to the well, and limit infiltration of surface fluids. <br /> ' FLUID LEVEL MONITORING <br /> ' Fluid levels are monitored in the wells using an electronic interface probe with conductance <br /> sensors. The presence of liquid-phase hydrocarbons is verified using a hydrocarbon-reactive <br /> paste. The depth to liquid-phase hydrocarbons and water is measured relative to the well box <br /> ' top or top of casing. Well box or casing elevations are surveyed to within 0.02 foot relative to <br /> a county or city bench mark. <br /> ' GROUNDWATER PURGING AND SAMPLING <br /> Groundwater monitoring wells are purged and sampled in accordance with standard regulatory <br /> ' protocol. Typically, monitoring wells that contain no liquid-phase hydrocarbons are purged of <br /> groundwater prior to sampling so that fluids sampled are representative of fluids within the <br /> formation. Temperature, pH, and specific conductance are typically measured after each well <br /> ' casing volume has been removed. Purging is considered complete when these parameters vary <br /> less than 10% from the previous readings, or when four casing volumes of fluid have been <br /> removed. Samples are collected without further purging if the well does not recharge within <br /> 2 hours to 80% of its volume before purging. <br /> 0FNFM.1:41D/93 A-2 <br /> 1 <br />