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WASTE DISCHARGE REQUIREMENTS ORDER NO.R5-2004-0028 -21- WASTE DISCHARGE REQUIREMENTS ORDER NO.R5-2004-0028 -22- <br /> CITY OF MANTECA,CITY OF LATHROP AND DUTRA FARMS CITY OF MANTECA,CITY OF LATHROP AND DUTRA FARMS <br /> WASTEWATER QUALITY CONTROL FACILITY WASTEWATER QUALITY CONTROL FACILITY <br /> SAN JOAQUIN COUNTY SAN JOAQUIN COUNTY <br /> Therefore,this Order includes an effluent limitation for aluminum of 71ug/1 as a monthly 1800 ug/l. The maximum observed upstream receiving water MBAS concentration is less than <br /> average and 143 ug/1 as the daily maximum. 20 ug/l. An Effluent Limitation for MBAS is included in this Order based on of the Basin Plan <br /> water quality objectives for chemical constituents,floating material,and tastes and odors. <br /> 47. Iron: Iron concentrations in the effluent ranged from 170 ug/1 to 730 ug/1 while background <br /> concentrations in the San Joaquin River ranged from 780 ug/1 to 2800 ug/1 based on results from 51. Molybdenum: The recommended agricultural water quality goal for molybdenum,that would <br /> 12 samples collected between January 2002 and December 2002. The Basin Plan chemical implement the narrative"Chemical Constituent"objective,is 10 ug/1 based on Water Quality for <br /> constituent objective includes a receiving water objective in Table III-1 for iron of 300 ug/1 in Agriculture,Food and Agriculture Organization of the United Nations—Irrigation and Drainage <br /> the Delta,and the secondary MCL for iron of 300 ug/l. Both the receiving water and the effluent Paper No.29,Rev.1(R.S.Ayers and D.W.Westcot,Rome,1985). Molybdenum was not <br /> exceed the Basin Plan numeric objective and the secondary MCL. Therefore,effluent monitored in the effluent or in the receiving waters. Because of the uncertainty associated with <br /> limitations are included in this Order based on the Basin Plan chemical constituents objective. the lack of monitoring,additional studies of this constituent are warranted to more thoroughly <br /> evaluate reasonable potential for this constituent to exceed criteria. MRP No.R5-2004-0028 <br /> 48. Manganese: Manganese concentrations in the effluent ranged from 13 ug/1 to 120 ug/1 while specifies monitoring for this pollutant. If the monitoring shows a reasonable potential to cause <br /> background concentrations in the San Joaquin River ranged from 82 ug/1 to 220 ug/1 based on or contribute to an exceedance of a water quality objective,this Order may be reopened to <br /> results from 11 samples collected between January 2002 and December 2002. The Basin Plan consider incorporation of appropriate effluent limitations. <br /> chemical constituent objective includes a receiving water objective in Table III-I for manganese <br /> of 50 ug/1 in the Delta,and the secondary MCL for manganese of 50 ug/1. Both the receiving 52. Carbofuran: Carbofuran was detected in the effluent and receiving water at concentrations <br /> water and the effluent exceed the Basin Plan numeric objective and the secondary MCL. greater than the OEHHA criterion of 1.7 ug/1. Because the data was greater than the method <br /> Therefore,effluent limitations are included in this Order based on the Basin Plan chemical detection limit but less than the laboratory's reporting limit,the data was flagged as"detected <br /> constituents objective. but not quantified". Additional monitoring is required. If the monitoring shows a reasonable <br /> potential to cause or contribute to an exceedance of a water quality objective,this Order may be <br /> 49. Chlorine: The Discharger currently uses chlorine for disinfection and has reported that it uses reopened to consider incorporation of appropriate effluent limitations. <br /> sodium hypochlorite for maintenance. Chlorine is extremely toxic to aquatic organisms. The <br /> Discharger uses a sulfur dioxide process to dechlorinate the effluent,but will discontinue this 53. Acute Bioassay: The new USEPA test procedure for acute bioassays(EPA-821-R-02-012,Fifth <br /> with the installation of the UV disinfection system. Because of the existing chlorine use and the Edition,October 2002)constitutes a more stringent acute toxicity limitation. The finding for <br /> future use of hypochlorite solutions without effluent dechlorination,there is reasonable potential ammonia indicated that there is a reasonable potential for the RWCF effluent to cause or <br /> for chlorine to be discharged at toxic concentrations. The Basin Plan contains a narrative contribute to an in-stream excursion above acute and chronic water quality standards for <br /> toxicity objective.Consistent with 40 CFR 122.44(d),it is appropriate to use the USEPA ammonia. To comply with the acute toxicity requirement of this Order and to comply with the <br /> ambient water quality criteria for chlorine for protection of freshwater aquatic life of 11 ug/1 as a Basin Plan narrative toxicity objective,the Discharger must reduce effluent ammonia <br /> 4-day average(chronic)concentration,and 19 ug/1 as a 1-hour average(acute)concentration to concentrations to comply with the new effluent limitations by 31 March 2004. Monitoring <br /> implement the narrative toxicity objective. Therefore,this Order includes water quality based Reporting Program No.R5-2004-0028 allows the bioassay to be modified to eliminate ammonia- <br /> effluent limitations for chlorine based on the USEPA ambient criteria to protect freshwater related toxicity until 31 March 2004,at which time the Discharger shall be required to <br /> aquatic life. implement the test without modifications to eliminate ammonia toxicity. The time schedule is <br /> authorized to be included in the Monitoring and Reporting Program based on 40 CFR§122.47. <br /> 50. Methylene blue active substances(MBAS): The effluent contains MBAS at levels that may <br /> cause or contribute to exceedances in the receiving waters of water quality objectives in the 54. Chronic Bioassay: The Discharger shall conduct the chronic toxicity testing specified in the <br /> Basin Plan. The Basin Plan includes the"Chemical Constituents"objective that incorporates Monitoring and Reporting Program. If the testing indicates that the discharge causes,has the <br /> state MCLS applicable to waters designated MUN. MUN is a designated beneficial use of the reasonable potential to cause,or contributes to an in-stream excursion above the water quality <br /> San Joaquin River. The Secondary MCL Consumer Acceptance Limit is 500 ug/1 for foaming objective for toxicity,the Discharger shall initiate a Toxicity Identification Evaluation(TIE)to <br /> agents(MBAS). The Basin Plan also includes water quality objectives that water not contain identify the causes of toxicity. Upon completion of the TIE,the Discharger shall submit a <br /> floating material or taste-or odor-producing substances in concentrations that causes nuisance or workplan to conduct a Toxicity Reduction Evaluation(TRE)and,after Regional Board <br /> adversely affect beneficial uses. The Basin Plan identifies non-contact water recreation,which evaluation,conduct the TRE. This Order will be reopened and a chronic toxicity limitation <br /> includes aesthetic enjoyment,as a beneficial use of the San Joaquin River. MBAS included and/or a limitation for the specific toxicant identified in the TRE included. <br /> concentrations in excess of the Secondary MCL-Consumer Acceptance Limit produce Additionally,if the State Board adopts a chronic toxicity water quality objective,this Order may <br /> aesthetically undesirable froth,taste,and odor. Foam has been observed on the surface of the be reopened and a limitation based on that objective included. <br /> discharge plume from the WQCF. The maximum observed effluent MBAS concentration is <br />