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Geosyntec <br /> consultants <br /> consistently increasing trend), another round of SVE will be implemented. Alternatively, if the <br /> first two performance monitoring events show low or decreasing concentrations near or below the <br /> CHHSL, suggesting a low rebound rate, the third monitoring event will be deferred. If the soil <br /> vapor concentrations continue to be low and stable(below or near the CHHSL)after the first three <br /> performance monitoring events, additional confirmation samples may be collected on an extended <br /> schedule to confirm the trend. With continued mass removal, it is expected that the durations <br /> between subsequent SVE efforts may be increasingly longer and limited by the rate of back- <br /> diffusion. <br /> Because the duration between individual performance monitoring events and subsequent SVE <br /> events is subject to change and may need to be adapted based on the results of the preceding <br /> sampling event(s). The Trust will routinely confer with the CVRWQCB to discuss any proposed <br /> changes in the approach, sample collection or further SVE events. Geosyntec believes that this <br /> approach of intermittent SVE operation is the most effective way to remediate soil vapor, achieve <br /> back-diffusion limited mass removal, and potentially determine the point at which SVE may be <br /> technically infeasible for further cleanup of VOCs at the Site. ISCO Approach <br /> 3.4 ISCO APPROACH <br /> The conceptual site model and groundwater monitoring data suggests the potential presence of <br /> residual PCE mass sorbed to the historic capillary fringe near MW-007A that may be presenting <br /> an ongoing source to groundwater as demonstrated by stable PCE concentrations at MW-007A <br /> and MW-009A (Geosyntec, 2021a; Geosyntec, 2021c). Therefore, in addition to the <br /> implementation of SVE for shallow soil vapor,Geosyntec proposes to conduct ISCO in the vicinity <br /> of MW-007A to address residual PCE impacts in groundwater. It is anticipated that three or four <br /> direct-push injection points will be installed near MW-007A and injected with 5 to 10 percent of <br /> KMn04 solution. The injections will target depths ranging from approximately 40 feet bgs <br /> (capillary fringe) to 70 feet bgs (within the saturated zone). Each location will receive between <br /> 2,500 and 7,500 gallons of the KMn04 solution. With groundwater flow to the east, residual <br /> KMn04 and an influx of cleaner water from upgradient is expected to address the residual <br /> concentrations at MW-009A. <br /> The scope of the ISCO activities is not certain at this point and will need to be refined based on <br /> the results of SVE performance monitoring and groundwater monitoring data. Implementation of <br /> SVE in the deeper well (10-20 feet bgs) may contribute to a consistent reduction in groundwater <br /> concentrations at MW-007A. In this case,the ISCO scope of work may be modified or eliminated. <br /> Alternatively, if SVE and groundwater data suggests no effect of SVE on the capillary fringe or <br /> groundwater concentrations, ISCO will be conducted to target the capillary fringe and groundwater <br /> to reduce PCE concentrations to the extent practicable. <br /> Northern Parking Lot Remedial Plan 5 August 6,2021 <br />