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TABLE 4 <br /> PARAMETERS FOR PILOT TEST PERFORMANCE MONITORING <br /> Nutrien Ag Solutions, Inc. <br /> 12325 North Dos Palos Road <br /> Firebaugh, California <br /> Parameter Method Rationale/Notes <br /> Laboratory Analysis <br /> Nitrate as Nitrogen (-N) EPA 353.2 Generally, when nitrate-N concentrations are less than 1 mg/L, manganese will become the preferred electron acceptor(AFCEE, 2004). However, <br /> manganese can begin being utilized as an electron acceptor at nitrate concentrations greater than 10 mg/L. <br /> When manganese (Mn4+) is used as the electron acceptor during anaerobic microbial metabolism it is reduced to manganese (Mn2+). The Mn2+ <br /> Dissolved Manganese EPA 200.7 concentrations can be used to indicate that the system is becoming more anaerobic. During or after Mn4+ is depleted, ferric iron (Fe3+) can be utilized for <br /> microbial metabolism. <br /> When Fe3+ is utilized as the electron acceptor, it is reduced to ferrous iron (Fe2+). Elevated levels of Fe2+ can be used to indicate if the ORP and DO in the <br /> Dissolved Iron EPA 200.7 groundwater are low enough to support anaerobic dechlorination. Fe2+ concentrations greater than 1.0 mg/L are indicative of favorable reducing conditions <br /> for dechlorination (AFCEE, 2004). <br /> Sulfate EPA 300.0 Decreasing sulfate concentrations (<20 mg/L) may indicate an environment suitable for reductive dechlorination, although there cases in the literature where <br /> dechlorination occurred at elevated dissolved sulfate levels (2,600 to 5,400 mg/L). (AFCEE, 2004) <br /> Total Organic Carbon (TOC) EPA 415.1 TOC is an indicator that sufficient carbon is available in the groundwater to support biological activity(biodegradation). TOC concentrations greater than 20 <br /> mg/L are indicative of favorable reducing conditions (AFCEE, 2004). <br /> Volatile Organic Compounds (VOCs) EPA 8260 Full VOC scan, including Site chemicals of concern (1,2-DCP)and (1,2,3-TCP). <br /> 1,2,3-Trichloropropane (1,2,3-TCP) SRL 524 Low level analysis for Site chemical of concern. <br /> Chloride EPA 300.0 During reductive dechlorination, chloride is released into the groundwater. Because of the neutral chemical behavior of chloride, it can be used as a <br /> conservative tracer to estimate biodegradation rates. <br /> Field Measurements <br /> Dissolved Oxygen (DO) Field Probe Denitrification will typically begin as DO decreases to less than 1 mg/L. <br /> Oxidation Reduction The ORP is a measure of electron activity and an indicator of the relative tendency of a solution to accept or transfer electrons. Reducing conditions are <br /> Potential (ORP) Field Probe required for anaerobic dechlorination to occur, and the ORP should remain less than -100 millivolts (mV)within the treatment zone for anaerobic <br /> dechlorination to occur(AFCEE, 2014) <br /> Conductivity is a measure of the capability of solution to conduct electricity. The conductivity of groundwater is directly related to the concentration of ions in <br /> Conductivity Field Probe solution. Specifically, conductivity will increase as hydrogen ion concentrations increase during the controlled release of 3DME and then will decrease as <br /> anaerobic degradation of available carbon proceeds towards and during reductive dechlorination. <br /> pH Field Probe The pH of groundwater influences the presence and activity of microbial populations in the groundwater. Microbes capable of conducting reductive <br /> dechlorination prefer pH values varying from 5 to 9 standard units (AFCEE, 2004). <br /> Notes: <br /> mg/L = milligrams per liter <br /> References: <br /> Air Force Center for Environmental Excellence (AFCEE). August 2004. Principles and Practices of Enhanced Anaerobic Bioremediation of Chlorinated Solvents. <br /> Page 17 of 17 <br />