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N <br /> • A solid oxidant demand (SOD, g w) test in the composite soil sample will be <br /> j performed using permanganate as the oxidant. The SODp..gw is <br /> I representative of the solid oxygen demand (SOD) of the soil. The SODpe.g�w <br /> is a test designed by Carus Chemical Company and is performed in their <br /> laboratory. For the aqueous portion of oxygen demand, the chemical oxygen <br /> demand (COD) and the 5-day biological oxygen demand (BODS) of the <br /> groundwater will be analyzed using EPA Methods SM5220D and SM5210B, <br /> respectively. <br /> • Total Dissolved Solids (TDS) by EPA Method 160. 1 <br /> • Selected metals in the groundwater will be analyzed before and after the bench <br /> test, including arsenic, bromide, cadmium, chromium, lead, and mercury. <br /> PROPOSED BENCH TESTING METHODS, <br /> Modified Fenton's treatment of the composite soil sample will consist of four process <br /> conditions: 1) A range of hydrogen peroxide concentrations with no pH adjustment; 2) A <br /> range of hydrogen peroxide concentrations with pH adjustment to 3 (with catalysis of the <br /> hydrogen peroxide by the naturally-occurring transition metals) such as iron, 3) A range of <br /> hydrogen peroxide concentrations with an addition of 200 mg/L of iron(flM) . This test will <br /> be performed at pH 3 ; and 4) A range of hydrogen peroxide concentrations with no pH <br /> adjustment but the addition of a proprietary iron-nitriloacefic acid (NTA) chelate or other <br /> proprietary chelating agent. ) <br /> All treatability studies will use approximately 10 g of the soil cuttings, 2 mL of <br /> groundwater, and 2 mL of reagents. Control samples using deionized water will be used. <br /> Upon addition of hydrogen peroxide and any other reagents (e.g., acid, iron[Il] sulfate, or <br /> iron-chelate), tbe-slurries-wilLhe-mixed-using_a vortex-to-ensure homogeneity of-the <br /> reagents. The reactions will be allowed to proceed until the hydrogen peroxide is consumed <br /> (24 hours) . The entire vial contents will then be extracted with methylene chloride and <br /> analyzed for residual hydrocarbons by gas chromatography/flame ionization detection. <br /> EQUIPMENT <br /> Total petroleum hydrocarbon concentrations will be quantified using an EPA <br /> Modified 8015 methodology on a Hewlett Packard 5890A gas chromatograph with a <br /> flame ionization detector (FID) and a 15-m D13-1 capillary column. Estimated <br /> chromatographic conditions will include an initial oven temperature of approximately 40 <br /> °C, program rate of 10 °C/min, final temperature of 140 °C, injector temperature of 200 <br /> °C, and detector temperature of 220 °C. <br /> DECOMPOSITION OF TREATMENT CHEMICALS <br /> The decomposition of hydrogen peroxide will be monitored in the samples to determine <br /> the length of time in hours that it takes for most of the hydrogen peroxide to decompose . <br /> This information will be useful in planning where the injection ports or injection wells <br /> should be placed so that groundwater travel time between injection locations is no greater <br /> i, <br /> 4 <br />