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RESPONSE TO WRITTEN COMMENTS -34- <br /> City Of Stockton-Regional Wastewater Control Facility <br /> NPDES No. CA0079138 <br /> 26 April 2002 Board Meeting <br /> remaining assimilative capacity for toxicity. Therefore, the Permit fails to comply with Clean Water <br /> Act mandates to implement a water quality standard protective of aquatic life for toxicity. <br /> RWQCB Response: The permit includes effluent limitations for ammonia that do not allow toxicity. <br /> The permit recognizes that the Discharger cannot meet the limitations, and therefore a Cease and <br /> Desist Order is proposed. The allowance to modify the acute bioassay to remove ammonia from <br /> consideration is not to allow ammonia toxicity in the receiving water, but to allow more reliable <br /> determination of any other constituents in the discharge that might cause acute toxicity. In addition, <br /> the permit requires the Discharger to conduct a toxicity identification/toxicity reduction evaluation to <br /> reduce constituents causing chronic toxicity. <br /> DeltaKeener Comment No. 8: Available dilution for priority pollutant human carcinogen <br /> criteria was improperly calculated. The period of UVM data represents the wettest cycle in California <br /> over the last 200 years. It ignores frequent drought cycles. It ignores average water years. It is <br /> entirely improper to use such a truncated data set (November 95 through September 2000) to compute <br /> a short-term harmonic mean for purposes of establishing human health carcinogen criteria. <br /> Please explain why it is proper to allow a 10:1 dilution ratio based totally on wet year flows? Why <br /> were dry year flows and the drier early decades of the century ignored? A reasonable, prudent and <br /> conservative dilution credit for human carcinogens, based on long-term flows, would be in the area of <br /> 4 or 5:1. <br /> RWQCB Response: Two data sets were available to calculate harmonic dilution: 1) 70+years of <br /> flow estimates at Stockton modeled from Vemalis flow data which included wet and drought cycles; <br /> and 2) 5 years of actual flow data measured at Stockton which included no dry year data. River flows <br /> predicted at Stockton from Vemalis flow data frequently do not agree with flows actually measured at <br /> Stockton. Harmonic mean flows based on actual measured data was judged more reliable, and so was <br /> used for development of effluent limits for human carcinogens. This may over estimate available <br /> dilution, however it is very unlikely that a human health risk would exist because: 1) statistically <br /> estimated effluent concentrations are well above measured effluent concentrations; 2) there are no <br /> drinking water intakes within many miles of the discharge point; and 3) the receiving water standards <br /> assume 70 years of water consumption. These effluent limitations will be recalculated in future <br /> permits as better flow data sets are developed through time. <br /> DeltaKeener Comment No. 9: The permit violates the state and federal anti-degradation policy <br /> by allowing mercury and lindane mass loadings to increase pending the uncertain establishment of a <br /> pollutant trading system, and allows diazinon and chlorpyriphos mass loadings to increase without <br /> restriction. <br /> RWQCB Response: The permit contains performance-based mass limitations for mercury, lindane <br /> and diazinon, intended to prevent further degradation pending compliance with final effluent <br /> limitations. The lindane final effluent limitation, based on the Basin Plan non-detect limitation, is <br /> effective within the permit term and is not tied to a pollutant trading system. Chlorpyrifos has not <br />