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Mr. Robert Garcia • • 29 January 2004 <br /> Leprino Foods, Inc. 2 <br /> In Phase 2, LFC would continue hydraulic control of groundwater by pumping, install additional <br /> injection points along the fenceline, and install injection points within the source area to enhance the rate <br /> that SPH dissolves into the groundwater, thereby accelerating the removal rate of the SPH. <br /> Path to Closure <br /> LFC states that it will attempt to meet the numerical diesel cleanup standard of 10 mg1I(emphasis <br /> added) set by the Regional Board, but if this is not attainable within a reasonable active remediation <br /> period, it proposes using non-numerical cleanup criteria. These criteria include ensuring that polluted <br /> groundwater will not reach potential receptors, human health is protected, natural attenuation <br /> mechanisms will continue to reduce remaining hydrocarbons in the groundwater, and a good-faith effort <br /> is made to reduce hydrocarbon mass while minimizing the potential for long term treatment if the benefit <br /> to water quality is diminishing. LFC then proposes specific criteria under which active remediation and <br /> monitoring would terminate. <br /> Changes to Monitoring and Reporting Program <br /> LFC proposes to change the MRP to require semi-annual monitoring, eliminate wells MW-7, RW-4A, <br /> MW-5 and MW-14A from the program, terminate pumping from recovery well RW-4A, and abandon <br /> well RW-4A. <br /> Comments <br /> 1. Figure 1 of the Proposal shows the cone of depression created by EW-2 is continuing to increase, and <br /> Figure 2 of the Proposal shows proposed injection point O-1 lies within the cone of depression <br /> created by EW-2. Therefore, the oxygenated water will flow towards the extraction well, not <br /> towards the monitoring points. Proposed injection point 0-2, upgradient of RW-1, appears to lie in <br /> the stagnation point between the local groundwater flow to the northwest and the EW-2 cone of <br /> depression in which the flow would be southeast. Therefore, it is not clear which direction the <br /> oxygenated groundwater will flow from 0-2. The oxygen injection points need to be located further <br /> downgradient and outside of the EW-2 cone of depression to treat the offsite plume. <br /> 2. Phase 1 of the Proposal is essentially a pilot study for oxygen injection, because only two injection <br /> points would be installed. Injection point 0-1, upgradient of RW-2, would be monitored by three <br /> monitoring points spaced 8, 16 and 24 feet downgradient, to provide information on effectiveness of <br /> treatment in the downgradient direction. However, there is a lack of monitoring points side-gradient <br /> to the injection point. Assuming that the injection points will be moved further downgradient to treat <br /> the offsite plume, side-gradient monitoring points are needed to confirm the theoretical dispersion <br /> lateral to the groundwater flow. <br /> 3. Regarding site cleanup levels, State Board Resolution No. 68-16 ("Antidegradation Policy")requires <br /> the Board in regulating discharges to maintain high quality waters of the state until it is demonstrated <br /> that any change in quality will be consistent with maximum benefit to the people of the State, will <br /> not unreasonably affect beneficial uses, and will not result in water quality less than that described in <br /> plans and policies (e.g., quality that exceeds water quality objectives). The water quality limit for <br /> TPHd, based on taste and odor, is 0.1 mg/l, not 10 mg/l as stated in the Proposal. <br />