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REGIONAL WATER BOARD RESPONSE (SWRCB/OCC File A-1846(a) and " 1846(b)) -13- <br /> PETITIONS FOR REVIEW OF V� E DISCHARGE REQUIREMENTS IftO <br /> ORDER NO. R5-2007-0036 (NPDES NO. CA0079154) AND <br /> TIME SCHEDULE ORDER NO. R5-2007-0037 <br /> CITY OF TRACY, WASTEWATER TREATMENT PLANT <br /> not acceptable WVVI-P design parameters. Consequently, the flow limitations contained in the <br /> Order are not based on acceptable WWTP design parameters and therefore fail to comply <br /> with federal regulations. <br /> -CSPA s contention is based on the March 2006 tentative Order, not the adopted Order. The <br /> effluent flow limitations were changed based on CSPA's comments on the tentative Order. <br /> Therefore, this contention is not applicable to the adopted Order. <br /> CSPA - CONTENTION D: The limit for acute toxicity is inconsistent with Basin Plan and <br /> federal requirements. The Order acknowledges in detail that there is no assimilative capacity <br /> in the receiving stream for individual toxic pollutants. It further acknowledges that ambient <br /> waters are impaired for unknown toxicity. Allowing 30% mortality in acute toxicity tests allows <br /> that same level of mortality in the receiving stream, in violation of federal regulations. and <br /> contributes to exceedance of the Basin Plan's narrative water quality objective for toxicity. <br /> Accordingly, the Order should be revised to prohibit acute toxicity. <br /> Order R5-2007-0036 contains several mechanisms to ensure that the effluent discharge does <br /> not cause acute or chronic toxiciton the-receiving water. Receiving water limits proscribe the <br /> discharge from causing toxicity in the receiving water. For effluent limitations included for the <br /> protection of the aquatic life beneficial use, the Order includes end-of-pipe effluent limits that <br /> were developed based on aquatic life toxicity criteria. Furthermore, the Order requires whole <br /> effluent chronic toxicity testing, which identifies both acute and chronic effluent toxicity. If this <br /> testing shows that the discharge causes, has the reasonable potential to cause, or contributes <br /> to an in stream excursion of the water quality objective for toxicity, the Order requires the <br /> Discharger to investigate the causes of, and identify corrective actions to eliminate the toxicity. <br /> The acute whole effluent toxicity limits establish additional thresholds to control acute toxicity <br /> in the effluent: survival in one test no less than 70% and a median of no less than 90% <br /> survival in three consecutive tests. Some in-test mortality can occur by chance. To account <br /> for this, in the EPA acute toxicity test method, the test acceptability criteria allow ten percent <br /> mortality (requires 90% survival) in the control. Thus, the acute toxicity limits allow for some <br /> test variability, but impose ceilings for exceptional events (i.e., 30% mortality or more), and for <br /> repeat events (i.e., median of three events exceeding mortality of 10%). These effluent <br /> limitations are consistent with U.S. EPA guidance. In its document titled "Guidance for <br /> NPDES Permit Issuance", dated February 1994, it states the following beginning on page 14: <br /> "In the absence of specific numeric water quality objectives for acute and chronic toxicity, the <br /> narrative criterion 'no toxics in toxic amounts'applies. Achievement of the narrative criterion, <br /> as applied herein, means that ambient waters shall not demonstrate for acute toxicity: 1) less <br /> than 90% survival, 50% of the time, based on the monthly median, or 2) less than 70% <br /> survival, 10% of the time, based on any monthly median. For chronic toxicity, ambient waters <br /> shall not demonstrate a test result of greater than 1 TUc." <br />