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RESPONSE TO WRITTEN COMMENTS -30- <br /> City Of Stockton-Regional Wastewater Control Facility <br /> NPDES No. CA0079138 <br /> 26 April 2002 Board Meeting <br /> RWQCB Response: The permit does not represent a taking of listed species. Effluent limitations are <br /> applied without dilution credit for constituents with acute and/or chronic toxicity criteria. New <br /> treatment processes are required, as well as source control for several pollutants, and a toxicity <br /> reduction evaluation. In addition it requires the City to assess the thermal impacts of its discharge and - <br /> includes a reopener to incorporate new requirements as appropriate. The federal Endangered Species <br /> Act does not apply to the action of the Regional Board. It applies only to federal actions. <br /> DeltaKeeper Comment No. 4: A"Worst Case"Hardness Value Must Be Used. <br /> RWQCB Response: DeltaKeeper states, "Ambient constituent concentrations maybe high during <br /> high Tows. For example, in July 1995, the ambient concentration of copper was 7,u g/1 at a hardness <br /> of 38 mg/1. The river exceeded both the CCC and CMC. Consequently, there was no remaining <br /> assimilative capacity." The ambient concentration of dissolved copper was non-detect (<1.0 µg/1) in <br /> July 1995. The total copper concentration was 7 µg/1. Since the CCC and CMC are dissolved <br /> standards, the receiving water did not exceed the CCC or the CMC. DeltaKeeper states further, "On 8 <br /> September 1998, hardness was 69 while flow was measured at 2,200 cfs. We see little justification for <br /> using a hardness value of 107 mg/l." If a hardness of 69 mg/1 was used, then you must consider the <br /> higher river flows, the dilution would exceed 25:1. Section 11.3.1 of the Fact Sheet adequately <br /> explains the rationale for determining the design hardness and why the design hardness of 107 mg/l is <br /> protective of receiving water beneficial uses. <br /> DeltaKeeper Comment No. 5: The Proposed Permit "Backslides"From Previous Permits. The <br /> CBOD limit represents a"backsliding" from previous permits. Staff is aware of the change from <br /> BOD to CBOD in the last Permit that failed to account for organic nitrogen. <br /> RWQCB Response: The proposed permit doesn't contain an effluent limitation for organic nitrogen. <br /> However, the amount of total oxygen demanding substances allowed to be discharged has been <br /> significantly reduced. During the fall and winter months, the RWCF discharges ammonia in excess of <br /> 20 mg/1. The proposed permit limits the effluent ammonia to 2 mg/l, as a monthly average, and 5 <br /> mg/j, as a daily maximum. Additionally, the requirement to construct tertiary filtration will likely <br /> reduce effluent CBOD and total suspended solids. Thus, the proposed permit contains effluent <br /> limitations for oxygen demanding substances that are more stringent than has previously been adopted, <br /> and is in compliance with the federal regulations, 40 CFR 122.44(1)(2)(ii). However, in order to <br /> further address your comment, the proposed Monitoring and Reporting Program has been updated to <br /> include effluent monitoring of organic nitrogen to determine if additional limitations are needed. <br /> DeltaKeeper Comment No. 6A: Diazinon: The Reasonable Potential Analysis found reasonable <br /> potential to exceed criteria. The calculated effluent limit in the Fact Sheet is an Average Monthly <br /> Effluent Limit of 0.047 µg/l and a Maximum Daily Limits of 0.061 µg/1. Inexplicably, a daily <br /> maximum concentration limit for diazinon of 0.1 µg/1 is included in the Permit. <br /> RWQCB Response: The interim effluent limitation for diazinon was calculated in accordance with <br /> Section 2.1 of the SIP. As the criteria for diazinon were released in March 2000 after the Basin Plan <br /> narrative toxicity criteria were issued, the Basin Plan allows for a compliance schedule of up to ten <br />