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reports to the PHS/EHD and RWQCB Groundwater samples would be analyzed for TPH/D <br /> and BTEX All monitoring activities would be discontinued five years after the system is <br /> decommissioned This is assumed to occur in 17 years <br /> 5 3 5 In-Situ Bioremediation - Option 5 <br /> Option 5 also consists of in-situ biological treatment to reduce the concentration of <br /> hydrocarbons in soil However, this option would add moisture and nutrients to improve <br /> naturally-occurring microbial growth A groundwater monitoring program identical to that <br /> developed for Option 2 would also be undertaken until the biological treatment is completed <br /> A percolation field consisting of perforated pipes or soaker hoses placed in gravel Iined <br /> trenches beneath the existing pavement would be used to deliver an aqueous solution of nutrients <br /> (probably calcium nitrate) to areas of remaining soil impacts The water and nutrient delivery <br /> rate would depend on the soil type, thickness of the impacted soil column, and areal extent of <br /> impacts With the addition of water to the impacted soil system, increased infiltration and <br /> consequent migration of hydrocarbon constituents and/or nitrate to the groundwater table is likely <br /> at some time during the treatment process This option therefore also includes groundwater <br /> plume capture and reinfection through the percolation field to contain and treat groundwater <br /> impacts resulting from the in-situ bioremediation process <br /> Although Option 5 can be expected to perform better than Option 4 in terms of <br /> hydrocarbon degradation and speed of remediation, there are still practical limits on the degree <br /> of contaminant mass reduction that could realistically be achieved with this technology It is <br /> estimated that in-situ bioremediation could ultimately achieve a cleanup level of about 500 to <br /> 1,000 mg/kg, beyond which little further reduction in hydrocarbon concentrations would be <br /> expected O&M of the system could be expected to continue for a minimum of approximately <br /> eight years As with Option 4, monitoring of system effectiveness would consist of collection <br /> and analytical testing of representative soil samples from both of the primary areas of soil <br /> impact Because of the relatively slow response expected, soil sampling and testing would be <br /> performed every two years <br /> Option 5 also includes quarterly monitoring of groundwater elevations in on-site <br /> monitoring wells (Dames & Moore, 1994b), annual groundwater sampling and analysis of the <br /> five wells, and preparation and submittal of annual monitoring reports to the PHS/EHD and <br /> sAc127 io 16 <br /> DAMES & MOORE <br />