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CALIFORNIA REGIONAL WATER QUALITY CONTROL BOARD AMENDMENT OF WASTE DISCHARGE REQUIREMENTS -2- <br /> CENTRAL <br /> 2- <br /> CENTRAL VALLEY REGION RESOLUTION NO.R5-2005-0110 <br /> CITY OF MANTECA <br /> RESOLUTION NO.RS-2005-0110 WASTEWATER QUALITY CONTROL FACILITY <br /> SAN JOAQUIN COUNTY <br /> AMENDING WASTE DISCHARGE REQUIREMENTS <br /> ORDER NO.R5-2004-0028 5. The effluent limitations for bromodichloromethane and dibromochloromethane included in <br /> NPDES NO.CA0081558 <br /> Order No.R5-2004-0028 were based on treatment plant performance prior to converting to full <br /> CITY OF MANTECA nitrification. With the significant increase in the formation of disinfection byproducts after <br /> WASTEWATER QUALITY CONTROL FACILITY upgrading the WQCF to operate in full nitrification mode,the Discharger is unable to comply <br /> SAN JOAQUIN COUNTY with the effluent limitations. <br /> 6. Due to the significant change in wastewater treatment,and based upon new water quality <br /> information,the Discharger,in a letter dated 20 April 2005,requested that the effluent <br /> The California Regional Water Quality Control Board,Central Valley Region,(hereafter Regional <br /> limitations for bromodichloromethane and dibromochloromethane be modified based upon <br /> Board)finds: current treatment plant performance. <br /> 1. On 19 March 2004,the Regional Board adopted Waste Discharge Requirements(WDR)Order 7. This Resolution amends WDR Order No.R5-2004-0028 by increasing the effluent limitations <br /> No.R5-2004-0028,NPDES No.CA0081558,prescribing waste discharge requirements for the for bromodichloromethane and dibromochloromethane based on re-calculated dilution credits <br /> City of Manteca,City of Lathrop,and Dutra Farms at the Wastewater Quality Control Facility using new effluent data collected while the WQCF was operating in full nitrification mode(see <br /> (WQCF)in San Joaquin County. For the purposes of this Resolution,the City of Manteca is Table 16). The re-calculated dilution credits for bromodichloromethane and <br /> hereafter referred to as"Discharger." dibromochloromethane(see Table 15)are 63:1 and 82:1,respectively,which are less than the <br /> maximum allowable human health dilution of 222:1 for the San Joaquin River. Therefore,the <br /> 2. The Discharger owns and operates a wastewater collection,treatment,and disposal system,and <br /> increased effluent limitations do not allocate the full assimilative capacity of the receiving <br /> provides sewerage service to the City of Manteca and the City of Lathrop. Land disposal of water and are more stringent than water quality-based effluent limitations. Based on the <br /> effluent is maximized by discharging effluent at agronomic rates seasonally to existing sample results in the effluent,it appears the Discharger can meet these new limitations. In <br /> City-owned property. Excess flow of treated municipal wastewater receives chlorine addition,the Discharger is installing ultraviolet(UV)disinfection by April 2007. Once <br /> disinfection and dechlorination prior to discharge to the San Joaquin River. operational,the use of chlorine for final effluent disinfection will be eliminated and the <br /> 3. Finding 31 of WDR Order No.R5-2004-0028 specifies the allowable dilution for human formation of disinfection byproducts will be reduced significantly. Consequently,the effluent <br /> health-based criteria,including bromodichloromethane and dibromochloromethane. Finding 31 concentrations of bromodichloromethane and dibromochloromethane will decrease. <br /> states,"A steady state analysis utilizing the harmonic mean flow at Vernalis provides a dilution 8. Sections 402(o)(2)(33 U.S.C.section 1342(o)(2))and 303(d)(4)(33 U.S.C.section 1313(d)(4)) <br /> of 222:1. The Regional Board is not required to grant a mixing zone or allocate the full of the Clean Water Act(CWA)and federal regulations at40 CFR section 122.44(l)prohibit <br /> assimilative capacity of the receiving water. For limitations based on these human health backsliding in NPDES permits. These anti-backsliding provisions require effluent limitations <br /> criteria,dilution is limited to the amount required to maintain compliance." In WDR Order No. in a reissued or amended permit to be as stringent as those in the previous permit,with some <br /> R5-2004-0028,the dilution credits granted for bromodichloromethane and exceptions where limitations may be relaxed. As discussed in Finding 7,the increased effluent <br /> dibromochloromethane were 11.5:1 and 8.9:1,respectively,and were based on treatment plant limitations for bromodichloromethane and dibromochloromethane are based on new <br /> performance,resulting in effluent limitations more stringent than water quality-based effluent information and are more stringent than water quality-based effluent limitations. Therefore,the <br /> limitations. Since the effluent limitations were based on treatment plant performance,the relaxation of the effluent limitations for bromodichloromethane and dibromochloromethane is <br /> Regional Board found the Discharger was able meet the effluent limitations. consistent with the anti-backsliding requirements of the CWA and federal regulations and is <br /> 4. The WQCF has historically operated in a non-nitrifying or partial nitrifying mode,which also consistent with the antidegradation provisions of 40 CFR section 131.12 and State Water <br /> typically produced an effluent with elevated levels of ammonia. Chlorine,when combined Resources Control Board Resolution No.68-16. Any impact on existing water quality will be <br /> with ammonia,creates chloramines,which are effective and stable disinfectants. In November insignificant. Furthermore,this Resolution adds a provision to allow Order No.R5-2004-0028 <br /> 2003,the treatment process was converted to full nitrification mode to reduce ammonia. to be reopened to modify the effluent limitations for bromodichloromethane and <br /> Without ammonia in the effluent,organochloramines are formed,which are less effective dibromochloromethane after installation of UV disinfection facilities. <br /> disinfectants than chloramines. Consequently,more chlorine is required for disinfection, 9. The Discharger historically utilized drying beds to dewater biosolids with final disposal on land <br /> increasing disinfection byproducts,including bromodichloromethane and adjacent to the WQCF. Monitoring and Reporting Program(MRP)Order No.R5-2004-0028 <br /> dibromochloromethane. requires biosolids monitoring pursuant to 40 Code of Federal Regulations(CFR)Part 503 for <br />