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Geweke, FRP 3 - 20 September 1993 <br /> smear zone. The wells that are proposed for introducing bacteria into the vadose zone and ground <br /> water may not affect the full extent of soil contamination in the smear zone. <br /> At the Ukiah site, GeoAudit has inferred that soil bioremediation has contributed to the decline in <br /> ground water contamination. However, similar drops in contamination have been noted at sites <br /> where the contaminated soil has merely been removed. It appears that the Apple Valley site was an <br /> in-situ soil cleanup and that ground water was not involved. Neither case study was an in-situ <br /> ground water case. <br /> The case studies for the two sites in Ukiah and Apple valley were very sketchy. Neither case study <br /> contained information about soil characteristics, depth to water, estimates of volumes of <br /> contaminants lost, number of borings used to introduce bacteria to the subsurface, volume of <br /> bacterial consortia and media used, contents of the medium, species of bacteria in the consortia, <br /> number of bacterial inoculations required, size of the contaminated area and the locations of borings <br /> and wells within the area. <br /> The results of any laboratory experiments, bench scale tests, and/or feasibility tests conducted for <br /> Geweke were not provided. The contents of the bacterial medium, the number of bacteria used, <br /> species of bacteria in the consortia, volume of the medium and consortia introduced to the <br /> subsurface, and the number of inoculations required, were not provided. The soil characteristics <br /> were not provided, including pH, EC, moisture content/water-bearing capacity/moisture retention <br /> curves, adsorption/desorption rates, metals toxicity, oxygen demand, nitrogen content, phosphorus <br /> content, trace mineral content, porosity, and soil particle size distribution. All of these parameters <br /> have an impact on soil and ground water in-situ bioremediation. <br /> The number and location of wells to be used to introduce bacteria into the ground water were not <br /> provided. There was no mention of whether oxygen must be added to ground water and how this <br /> may be accomplished. Introduction and maintenance of adequate oxygen in the contaminated ground <br /> water zone may be one of the most difficult aspects of in-situ bio. There was no mention of how <br /> putting the liquid medium into wells will affect ground water flow or contamination. <br /> There was no mention of ground water monitoring for introduction of medium plus consortia during <br /> the soil remediation phase. Without monitoring it will be difficult to determine whether ground <br /> water is being affected positively or adversely. Other than monitoring contamination levels <br /> biannually, there is no mention of how they propose to determine that the soil treatment system is <br /> actually working, if more bacterial inoculations are needed, if more oxygen is needed, if additional <br /> nutrients are needed, or if the soil has become desiccated. Maintaining adequate oxygen without <br /> causing desiccation may be the most difficult aspect of in-situ bio of soil in the vadose zone. <br /> Without additional monitoring, it seems that this is effectively, aeration of the soil. <br /> The following information is needed to complete the FRP: <br /> 1. Locations and descriptions of GL-3, GL-4, and VW-1 through VW-4; <br /> 2. A signed copy of the letter in Appendix C; <br /> 3. A proposal to remediate the "smear zone"; <br />