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INFORMATION SHEET -2- <br /> STOCKTON COGENERATION COMPANY <br /> SAN JOAQUIN COUNTY <br /> Effluent/Receiving Water Limitations <br /> The following is a discussion of the significant changes from the previous permit: <br /> Total Dissolved Solids - The TDS secondary drinking water MCL is the basis for the effluent <br /> limitations of 500 mg/l as a monthly average and 1000 mg/l as a daily maximum in Order No. 95-148. <br /> These limitations will be unchanged in this version of the permit. For protection of the agricultural <br /> supply beneficial use based on crop tolerance, the TDS water quality criteria is 450 mg/l as an annual <br /> average. It is unknown if the Discharger is currently capable of meeting this effluent limitation. This <br /> Order provides for a time schedule for meeting the effluent limitation. The Board considers the <br /> application of a water quality objective that has never been applied to North Littlejohns Creek as a new <br /> interpretation of the Basin Plan. <br /> Chlorine Residual—The chlorine residual effluent limitations have been modified from the previous <br /> permit. A chlorine residual monthly average limit of 0.01 mg/l and a daily maximum effluent limit of <br /> 0.02 mg/l have been added to the permit in order to protect freshwater aquatic life. It is unknown if the <br /> Discharger is currently capable of meeting this effluent limitations. This Order provides for a time <br /> schedule for meeting the effluent limitations. The Board considers the application of a water quality <br /> objective that has never been applied to North Littlejohns Creek as a new interpretation of the Basin <br /> Plan. <br /> Copper- Based on a worst-case effluent hardness of 95 mg/l as CaCO3, the CTR hardness dependent <br /> copper water quality criteria for protection of aquatic life is 8.6 µg/l as a four day average and 13 µg/l as <br /> a 1 hour average. Of seven samples collected biannually between January 1997 and January 2000 the <br /> two samples collected in 1998 were both above detection limits at 30 and 50 pg/l. These higher copper <br /> concentrations were attributed to process changes in the Discharger's cooling tower disinfection system <br /> implemented that year. Once the impact of these process changes on effluent copper concentrations was <br /> discovered, the disinfection system was adjusted to reduce copper concentrations below detection limits <br /> again. Because of the process changes made to prevent these increased copper concentrations, the <br /> Board does not find these to be indicative of reasonable potential. However, the other five samples were <br /> below detection limits with four of the five having detection limits ranging between 10 and 30 µg/l. <br /> These levels are above the most stringent copper water quality criteria. The fifth of the non-detect <br /> samples was at a 4 pg/l detection level. Based on the fact that all but one of the samples had detection <br /> limits higher than the most stringent CTR criteria, more data with appropriate detection limits will be <br /> required per SIP section 2.2.2.A. The Discharger is required to develop a workplan and conduct <br /> sampling with detection limits low enough to allow for evaluation with the CTR criteria. <br /> Arsenic -Arsenic is an inorganic priority pollutant that produces human health effects. The Basin Plan <br /> water quality objective for arsenic is a maximum concentration of 10 µg/l dissolved, the U.S. EPA <br /> Primary MCL for arsenic is 10 µg/l total, and the California Proposition 65 Regulatory Drinking Water <br /> Level (10-6 cancer risk) is 5 µg/l total. There are no CTR human health criteria for arsenic. The U.S. <br /> EPA recommended translator for converting total arsenic concentrations to equivalent dissolved <br />