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Nestle USA, Inc.—Ripon, CA January 28, 2011 <br /> 2011 Revised Feasibility Study <br /> treatment process may vary from a simple carbon adsorber to complicated air <br /> stripper and oxidizer. The use of an air stripper and oxidizer, as is currently in <br /> use at the 519 South Stockton Avenue system, significantly increases costs, and <br /> utilizes an energy source like natural gas. It should also be noted that operation <br /> of complex treatment systems are often energy intensive and result in offsetting <br /> environmental impacts including the use of fossil fuels, electricity and associated <br /> air emissions. <br /> Also, high TDS concentrations in the Upper Aquifer (between 900 and 1500 parts <br /> per million) limit the utility of the effluent water in the NP system. High TDS also <br /> causes scale to form on well screens, significantly restricting groundwater flow <br /> and reducing yield. <br /> Though this technology is effective in limiting migration, it will require a long <br /> operation time unless combined with other more aggressive in-situ treatment <br /> technologies. Therefore, long-term maintenance of equipment, infrastructure, <br /> and wells, needs to be considered for pump-and-treat. Further, the relatively <br /> small amount of COC recovery achieved by this process should be weighed <br /> against the burden that pump-and-treat places on groundwater resources. <br /> 9.2.1.3 Relative Cost <br /> The cost to operate this technology in the long-term exceeds that of many other <br /> technologies, particularly due to O&M requirements. <br /> Capital costs may include construction or upgrade of treatment systems, and <br /> installation of extraction wells, pumps, and conveyance piping and utility <br /> conduits. <br /> On-going O&M costs may include electricity and natural gas to operate systems, <br /> GAC management and disposal, water disposal, compliance sampling and <br /> reporting, and replacement parts. O&M costs may increase with time as <br /> equipment ages, requiring replacement, and as energy becomes more <br /> expensive. <br /> Based on current system operation at the Site, the O&M costs for 30 years of <br /> operation is on the order of $6,800,000 for a system extracting and treating <br /> approximately 32 million gallons per year (approximately 60 gpm; see <br /> Attachment D). <br /> 9.2.1.4 Conclusion <br /> Pump-and-treat is suitable as an interim remedy, but must be carefully evaluated <br /> for long-term use. Downsides to long-term implementation of pump-and-treat <br /> technology include limitations on the disposal of treated effluent, high TDS <br /> concentrations, energy use, air emissions, and waste filter generation disposal, <br /> and diminishing effectiveness. These factors must be taken into account and <br /> weighed against the benefits that pump-and-treat can achieve. <br /> Pump-and-treat is a viable option for meeting the RAOs across the Study Area; <br /> however, the length of time required to meet all RAOs may be more than 30 <br /> 26 <br />