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18 July 2002 <br /> AGE-NC Project No 96-0254 <br /> Page 9 of 17 <br /> Free oxygen Increases the metabolic rates of reaction in the bacteria A small blower delivering <br />' atmospheric air to the subsurface at a rate of two to five scfm per well can be used to enhance air <br /> flow and oxygen concentrations during the process This may result In unwanted dehydration of the <br /> soil, but dehydration can be ameliorated by monthly infection of distilled water to each well <br />' The hydrocarbon-degrading bacteria are also tolerant to a wide range of soil conditions For instance, <br /> g <br />' pH can range from 4 to 9 5 and electrical conductivity has little or no effect unless sodium <br /> concentrations exceed 5% on a weight basis <br />' 5 2 3 Inoculation Wells <br />' The effective radius of influence in soil of inoculation wells is typically 15 feet Existing monitoring <br /> wells can be used for inoculation of the smear zone as well as ground water, but the Inoculum will <br /> tend to go to the bottom of a monitoring well and pass into the saturated ground water zone from the <br />' annular space near the bottom Although a greater radius of influence is usually obtained for ground <br /> water inoculation, since ground water movement can assist the bacterial migration, additional <br /> inoculation points would be needed for in-situ soil treatment of the vadose zone,utilizing temporary <br /> I. inoculation points or soil borings <br /> I5 2 4 Monitoring Activities <br /> After inoculation,the inoculation wells and groundwater monitoring wells should be monitored over <br />' a period of several months through periodic field measurements of organic vapor, carbon dioxide, <br /> and oxygen concentrations Quarterly or semi-annual monitoring activities should also include the <br />' installation of soil borings to collect soil samples to monitor bacterial populations, nutrient <br /> availability and soil remediation progress If monitoring indicates areas of slow remediation, <br /> additional inoculation or addition of nutrients may be required <br /> I <br /> 5 2 5 Duration _ <br /> Duration (and cost) is dependent on the volume of soil and water to be remediated, the number of <br /> inoculation and monitoring wells,the average concentrations of contaminants and nutrients,and the <br />' temperature and permeability of the soil Theoretically,the radius of influence of the inoculation well <br /> should Increase rapidly at first, then gradually decline as the affected volume Increases and the <br /> bacteria encounter decreasing hydrocarbon concentrations toward the margins of the hydrocarbon <br /> Iplume Shorter-chain hydrocarbons are typically consumed first and longer-chain hydrocarbons later <br /> • Remediation at sites with similar soil composition typically takes between 12 and 48 months <br /> Advanced GeoEnvironmental,Inc <br />