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STATE WATER RESOURCES CONTROL BOARD _ 10 - <br /> ORDER <br /> 10 - <br /> ORDER WQ 2014-0153-DWQ <br /> GENERAL WASTE DISCHARGE REQUIREMENTS <br /> FOR SMALL DOMESTIC WASTEWATER TREATMENT SYSTEMS <br /> conditions, which are not favorable biological treatment conditions. This General <br /> Order includes effluent limits for nitrogen and BOD, and a process to determine how to <br /> apply the limits. Implementation of the process to determine the effluent limit that <br /> applies will result in the BPTC for the wastewater constituents. In addition, this <br /> General Order provides guidance on preparing a monitoring program that ensures the <br /> treatment is effective. Each of the wastewater constituents of concern are discussed <br /> below: <br /> a. Salinity is a measure of dissolved solids in water. Excessive salinity can reduce <br /> the beneficial uses of water. Salinity can be affected by the discharge of <br /> wastewater with elevated concentrations of TDS. TDS consists of both volatile <br /> (organic) and fixed (inorganic) fractions. In a well-operated land application <br /> system, volatile dissolved solids in percolate will be reduced to negligible <br /> concentrations. The best approach for addressing salinity is through source <br /> control activities. This General Order allows an Executive Officer to require <br /> participation in salt and nutrient management planning processes. <br /> b. Nitrogen is a nutrient normally present in domestic wastewater at a <br /> concentration that can degrade groundwater quality. The potential for <br /> degradation depends upon the wastewater treatment method and the <br /> environment into which the wastewater effluent is discharged. Nitrogen <br /> concentration reduction is not required in every situation, such as when <br /> wastewater treatment and application is performed in a way that is protective of <br /> the beneficial uses of water. <br /> When needed, nitrogen concentrations can be reduced in a number of ways, <br /> such as nitrification, denitrification, and/or crop uptake and removal. However, <br /> the General Order requires that the effluent limit for nitrogen be determined <br /> based on procedures in Attachment 1, which provides additional criteria to <br /> determine when and how much nitrogen control is required. Effluent limits are <br /> determined based on the threat to groundwater quality. If nitrogen control is <br /> needed, a minimum of 50-percent reduction is required. In cases where a <br /> higher threat to groundwater exists, a total nitrogen concentration limit of 10 <br /> mg/L is required. By imposing the total nitrogen limit of 10 mg/L, the <br /> wastewater derived nitrogen cannot exceed the maximum contaminant level <br /> (MCL) for groundwater. Because natural systems are rarely 100-percent <br /> efficient, the nitrogen concentration limit will be protective of the existing and/or <br /> potential beneficial use of groundwater. Effluent limitations for nitrogen are <br /> contained in this General Order. To ensure the nitrogen control is effective, the <br /> model Monitoring and Reporting Program (MRP) provided as Information Sheet <br /> Attachment C includes monitoring that can be implemented to verify compliance <br /> with effluent limits. <br /> c. Pathogens and other microorganisms are present in domestic wastewater. <br /> Wastewater treatment processes will reduce the concentration of pathogens but <br /> disinfection is required to significantly reduce their presence. Coliform bacteria <br /> are used as a surrogate (indicator) because they are excreted by warm-blooded <br /> animals, are present in high numbers, survive in the environment similar to <br /> September 23, 2014 <br />