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' Aprotek's experience indicates that during the first three to four days of the <br /> process, the rate of biotransformation can reach 350 to 400 parts per million (ppm) <br /> per day As the remediation progresses, this rate has been observed to slow down <br /> to 150 to 200 ppm per day The rate of biotransformation is site-specific and is a <br /> function of temperature and the availability of food sources A plate count <br /> conducted March 10, 1994, by Anlab Analytical Laboratories (Anlab) on a <br /> groundwater sample obtained by Waste Science from MW-08 indicated the presence <br /> of 930 coliform forming units per gram (CFU/g) of bacteria at the site The <br /> ' presence of bacteria in the groundwater at the Stockton site supports the supposition <br /> that natural biodegradation is occurring at the site The addition of the enzymes will <br /> make the food source more accessible to the bacteria and will increase the rate of <br /> ' bloremediation <br /> The existing microbial population is sufficient to biodegrade the hydrocarbons <br /> ' present at the site The rate of bioremediation may be enhanced through the <br /> injection of live bacteria However, because of regulatory constraints concerning the <br /> introduction of constituents into groundwater aquifers, this option will not be <br /> considered Based on the available information, it is estimated that the plume size <br /> is approximately 50 feet by 20 feet by 10 feet, or approximately 74,800 gallons of <br /> water With the levels of constituents reported in the groundwater for the Stockton <br /> site, it is anticipated that cleanup of the plume to non-detect levels will take <br /> approximately two to four weeks <br /> ' 2.2 Remedial Design and Well Placement <br /> Waste Science proposes that the remediation be implemented through the <br /> circulation of the ETEC"' multi-enzyme complex using one extraction well and three <br /> perforated injection wells (Figure 2) <br /> Based on historical data, Waste Science proposes to convert MW-08 into an <br /> extraction well. This well is constructed of 4-inch diameter, Schedule 40 flush- <br /> threaded polyvinyl chloride (PVC) casing, with 20 feet of 0 002-inch factory slotted <br /> screen The well is screened from 5 feet to 25 feet bgs Because groundwater was <br /> encountered at 15 feet bgs in MW-08, this well is adequate for the purposes of <br /> extraction The capture radius for this well is conservatively estimated to be 30 feet <br /> The rationale for the placement of the infection wells is based on historical data <br /> and the anticipated radius of influence of each well (30 feet) It should be noted <br /> that,with the exception of the slug test, no further aquifer tests have been conducted <br /> 9488 Fast Bay Municipal Utility District <br /> 40429601 rap 7 Remedial Action Plan <br />