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WASTE DISCHARGE REAEMENTS ORDER NO. 5-01-119 (AISED) -5- <br /> STOCKTON COGEN COMPANY <br /> SAN JOAQUIN COUNTY <br /> included in this permit, as explained below,based on the application of the Basin Plan water <br /> quality objectives within North Littlejohns Creek. It is unknown if the Discharger is currently <br /> capable of complying with these limitations. <br /> This Order provides for a time schedule for meeting the receiving water limitations for temperature <br /> and dissolved oxygen and the effluent limitations for chlorine residual. The time schedule is <br /> authorized to be included in this Order based on 40 CFR §122.47. The Board considers the <br /> elimination of the mixing zone in North Littlejohns Creek for compliance with the Basin Plan <br /> water quality objectives as anew interpretation of the Basin Plan. <br /> 19. Based on a worst-case effluent hardness of 95 mg/1 as CaC031 the CTR hardness dependent copper <br /> water quality criteria for protection of aquatic life is 8.6 9g/1 as a four day average and 13 µg/l as a <br /> 1 hour average. Of seven samples collected biannually between January 1997 and January 2000 <br /> the two samples collected in 1998 were both above detection limits at 30 and 50 gg/l. These <br /> higher copper concentrations were attributed to process changes in the Discharger's cooling tower <br /> disinfection system implemented that year. Once the impact of these process changes on effluent <br /> copper concentrations was discovered, the disinfection system was adjusted to reduce copper <br /> concentrations below detection limits again. Because of the process changes made to prevent these <br /> increased copper concentrations, the Board does not find these to be indicative of reasonable <br /> potential. However, the other five samples were below detection limits with four of the five <br /> having detection limits ranging between 10 and 30 µg/l. These levels are above the most stringent <br /> copper water quality criteria. The fifth of the non-detect samples was at a 4 gg/1 detection level. <br /> Based on the fact that all but one of the samples had detection limits higher than the most stringent <br /> CTR criteria, more data with appropriate detection limits will be required per SIP section 2.2.2.A. <br /> See Provision F.2 for the terms and compliance schedule of the required study. <br /> 20. Arsenic is an inorganic priority pollutant that produces human health effects. Of seven samples <br /> collected and analyzed for arsenic biannually between January 1997 and January 2000, all were <br /> above the State of California Proposition 65 Level of 5 µg/l for arsenic. Effluent concentrations <br /> ranged between 20 and 26 gg/l. Data indicate that the source of the arsenic is the groundwater that <br /> is the supply for the majority of the cooling tower feedwater. There is no arsenic added in any part <br /> of the SCC operation. The Basin Plan requires the Board to consider information submitted by the <br /> discharger and others and numerical criteria and guidelines for toxic substances developed by other <br /> agencies in determining what numeric effluent limitation will properly implement the narrative <br /> toxicity objective. Numerical criteria include, for example, USEPA's 106 incremental cancer risk <br /> estimate for drinking water of 0.02 µg/l, the California Office of Environmental Health Hazard <br /> Assessment's 10`risk level of 0.023 µg/l, USEPA's recommended ambient water quality criterion <br /> for protection of human health in waters considered to be potential sources of drinking water of <br /> 0.018 gg/L at the 10`risk level, the Proposition 65 limit of 5 µg/l, and the California MCL of 50 <br /> µg/l. The Board finds that it is more appropriate to use the MCL of 50 µg/1 in this situation than <br /> the cancer risk levels. Therefore, there is no reasonable potential for the effluent to exceed 50 <br /> µg/1, and an effluent limit for arsenic is not included in this Order. <br /> 21. The water quality goal for the protection of agricultural use for molybdenum is 10 gg/1 as an <br /> annual average. Of seven samples collected and analyzed for molybdenum biannually between <br /> January 1997 and January 2000, four samples were at or below 5.0 µg/1, one was 9.0 µg/l, one was <br /> 15 µg/1, and one was non-detect with a detection limit of 20 µg/l. The data indicate that there is a <br />