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Response to Written Comments -7- 24 April 2007 <br /> City of Tracy WWTP <br /> San Joaquin County <br /> between aluminum toxicity, pH and hardness is not well quantified and <br /> recommends that a Water-Effects Ratio (WER) be used to adjust the criteria <br /> where necessary. The City has not submitted information supporting a WER for <br /> aluminum discharge to Old River. Without this information, the Regional Water <br /> Board must use the default assumption of a WER of 1.0, as was done in <br /> performing the reasonable potential analysis. As explained in the Fact Sheet, the <br /> acid soluble analysis method is allowed to be used to determine compliance with <br /> the effluent limits, which should eliminate from consideration aluminum <br /> associated with clay particles. The upstream receiving water data for aluminum <br /> exceeds both the acute and chronic NRWQC, based on total recoverable <br /> analyses. The City is welcome to provide additional upstream data using the <br /> acid soluble method. If those data are below the NRWQC, then the reasonable <br /> potential analysis could be revised and the need for effluent limits reassessed at <br /> that time. <br /> CITY OF TRACY - NPDES COMMENT #12: Section IV.A.1.a., Table 4, and Section <br /> IV.S.e., Table 9. Copper Limits. The Regional Water Board inappropriately utilizes the <br /> copper objective from Sacramento-San Joaquin Basin Plan, Table III-1, in the derivation <br /> of proposed effluent limitations instead of the CMC included in the California Toxics <br /> Rule. <br /> Request: The City requests that the proposed effluent limits for copper be recalculated <br /> using only the CTR standards as adjusted by the new Biotic Ligand Model <br /> (BLM), and the interim limit be set as a monthly average value. If not enough <br /> data exist, the City should be given adequate time under a compliance <br /> schedule to perform WER or BLM adjustment to reflect local water quality <br /> conditions along with a modification to the reopener at Provision VI.C.1.g. to <br /> amend the final limits based on the WER or BLM adjustment. <br /> RESPONSE: The Policy for Implementation of Toxics Standards for Inland <br /> Surface Waters, Enclosed Bays and Estuaries of California (a.k.a., State <br /> Implementation Policy or SIP) in the fourth footnote on Page 1 states, "if a water <br /> quality objective and a CTR criterion are in effect for the same priority pollutant, <br /> the more stringent of the two applies." This is consistent with guidance supplied <br /> by Kathleen Goforth, Water Quality Standards Coordinator for USEPA, Region 9. <br /> In an email reply to an inquiry from Regional Water Board basin planning staff, <br /> dated 24 August 2004, Ms. Goforth states, "Where there are both State and <br /> federally promulgated criteria, if the State criteria are more stringent than the <br /> federal criteria, the State's more stringent criteria apply. This is explicitly stated in <br /> both the NTR [40 CFR 131.36(c)(1)] and CTR [40 CFR 131.38(c)(1)]. <br /> Conversely, if the federal criteria are more stringent than the State criteria, then <br /> the federal criteria apply." Federal regulations in 40 CFR 131.38(c)(1) state, "The <br /> criteria in paragraph (b) of this section apply to the State's designated uses cited <br /> in paragraph (d) of this section and apply concurrently with any criteria adopted <br /> Regional Water Quality Control Board, Central Valley Region <br /> Board Meeting— 3/4 May 2007 <br /> Item#17 <br />