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Mr. Nathan Crum - 2 - 16 December 2009 <br /> Valley Pacific Petroleum Sen <br /> Valley Pacific selected air sparge/soil vapor extraction (AS/SVE) to remediate the <br /> COCs in the groundwater and vadose zone based on the rationale that AS/SVE would <br /> likely enhance the biodegradation potential at the Site by increasing the dissolved <br /> oxygen (DO) levels in groundwater. Valley Pacific estimates that DO levels of greater <br /> than 1-2 mg/L can sustain aerobic degradation of compounds such as BTEX. <br /> Starting in the fourth quarter of 2008, biodegradation indicator parameter monitoring <br /> was conducted in five wells for a year-long assessment of the baseline bioremediation <br /> potential to support the implementation of an AS/SVE pilot study. MW-12 is upgradient, <br /> MW-6R is in the heart of the plume, MW-2 and MW-3 are cross gradient, and MW-10 is <br /> downgradient. Quarterly monitoring was conducted in October 2008, and January, April, <br /> and July 2009. The results are documented in the 1 December 2009 Biodegradation <br /> Parameters Baseline Study (Study). <br /> SPH was present in MW-6R in April 2009, so this well was not sampled during April <br /> 2009. Previous laboratory analytical results showed that the SPH is high sulfur diesel <br /> similar to the type used in California prior to 1993. During the other three quarters, MW- <br /> 6R had the highest concentrations of organic carbon, respiration by-products, anaerobic <br /> terminal electron acceptors, and oxygen demand, as well as the lowest concentrations <br /> of DO. The oxygen-reduction potential (ORP) was generally lowest in MW-10. <br /> Conversely, this well also had the highest DO concentrations. The highest <br /> concentrations of nutrients were present in upgradient well MW-12. Heterotrophic plate <br /> counts varied from 40 to 600 colony forming units per milliliter of water (cfu/mL). <br /> Our comments are presented below. <br /> 1. We concur that AS has the potential to enhance biodegradation by increasing the <br /> DO concentration. However, before the remedy can be implemented we will need <br /> Valley Pacific to submit an Implementation Work Plan detailing schematics of the <br /> proposed system design. The Implementation Work Plan must also contain <br /> calculations and results for initial estimates of (1) the combined mass of the vapor, <br /> separate, and dissolved phases of hydrocarbon mass underlying the Site, (2) the <br /> mass of oxygen required to sustain microbial activity and achieve water quality <br /> objectives (WQOs), (3) any nutrient amendments that may be needed based on the <br /> four quarters of MNA data, and (4) the time required to achieve WQOs. <br /> 2. The MNA data indicate that the biodegradation parameters at the Site are typical of <br /> most established contaminant plumes. However, MW-3 and MW-4 are the only two <br /> wells in which dissolved plume concentrations have decreased since monitoring <br /> began. There is potential for biodegradation, but the nutrients required to sustain <br /> biodegradation have been depleted, and bacterial counts are uncharacteristically <br /> low. In addition, SPH has been present at the Site since 1997 despite continuous <br /> removal. These indicators show that biodegradation has stalled and/or there is an <br /> active ongoing source of petroleum hydrocarbons, as discussed in Comment No.3 <br /> of our 3 July 2008 letter. Implementation of a remedial action will be necessary to <br /> meet WQOs. However, Valley Pacific must also modify operations to prevent fuel <br /> discharges to the ground surface during fuel transfers to eliminate any ongoing <br /> sources. <br />