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Project Number 1804BK01 September 17.2003 <br /> remaining annular space. The wellhead will be equipped with a locking cap and a traffic- <br /> rated steel box set in cement slightly above grade to complete the installation. <br /> Well Development <br /> Approximately forty-eight (48) hours after installation of the monitoring and aquifer test wells, <br /> they will be developed to remove fines and settle the filter pack. This will be accomplished <br /> using the 'surge blocking and bailing' method and/or pumping using a submersible pump. It <br /> is anticipated that at least ten (10) well casing volumes will be removed from each well <br /> during development. <br /> Groundwater Monitoring and Sampling <br /> Groundwater at the newly installed monitoring wells will be monitored and sampled at least <br /> 24 hours after development of the wells. Depths to groundwater will be measured from the <br /> top of casing (TOC) to the nearest 0.01-foot using a Solinst water level meter. Depths to <br /> water will be used to calculate the groundwater elevation at each well for generation of <br /> shallow and deep zone groundwater gradient plots. <br /> The monitoring wells will be sampled using low-flow purging and sampling techniques. A <br /> low-flow bladder pump will be slowly lowered to a depth approximately five feet below the <br /> water table to minimize mixing of water stored within the casing. The pump will be operated <br /> at a low-flow rate of approximately 0.1 gallon per minute (gpm) to purge the well minimizing <br /> drawdown. The water level will be monitored during purging to limit drawdown to 4 inches. <br /> Periodically during purging the pH, temperature, and electrical conductivity parameters will <br /> be measured. Groundwater will be considered stabilized and representative of the aquifer <br /> when three consecutive measurements are within ± 0.1 for pH, ± 3% for electrical <br /> conductivity, and ± 10% for temperature. <br /> After purging, a groundwater sample will be collected directly from the pump discharge into <br /> two 40-milliliter VOA vials. Care will be to verify that headspace or bubbles do not exist and <br /> each VOA vial will be sealed using a Teflon®-lined lid. The samples will be labeled and <br /> placed in an iced cooler maintained at 4° Centigrade, and accompanied with a chain- of- <br /> custody document for transport to the analytical laboratory. <br /> All downhole equipment will be cleaned prior to use and between wells by washing using an <br /> Alconox solution and rinsing with clean potable water. <br /> Soil Gas Sample Analysis <br /> The soil gas samples will be transported via overnight carrier to Columbia Analytical <br /> Services, Inc. of Simi Valley, California, a State of California Certified Analytical Laboratory, <br /> for chemical analysis. The samples will be analyzed for VOCs using EPA Method TO-14A <br /> Modified. The permissible holding time for the analysis is seventy-two (72) hours. The <br /> detection limit will be 0.005 microgram per liter (,ug/L) for each volatile organic compound. <br /> Soil Sample Analysis <br /> Selected soil samples will be transported via overnight carrier to Halcyon Laboratories, Inc. <br /> (California State-Certified analytical laboratory #1920) in accordance with State guidelines <br /> and EPA protocols. The samples will be analyzed for VOCs using EPA Method 5035/8260b <br /> within forty-eight (48) hours of collection as specified by the analytical method. The VOC <br /> detection limit will be 0.1 milligram per kilogram (mg/Kg). <br /> E,C Remediation 5 <br />