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SITE INFORMATION AND CORRESPONDENCE
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Last modified
4/3/2020 2:10:20 PM
Creation date
4/3/2020 1:50:02 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0524190
PE
2965
FACILITY_ID
FA0016241
FACILITY_NAME
STOCKTON REGIONAL WATER CONTROL FAC
STREET_NUMBER
2500
STREET_NAME
NAVY
STREET_TYPE
DR
City
STOCKTON
Zip
95206
APN
16333003
CURRENT_STATUS
01
SITE_LOCATION
2500 NAVY DR
P_LOCATION
01
P_DISTRICT
001
QC Status
Approved
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REGIONAL BOARD RESPONSE (SYI7ZCB/0CC FILE A-1483) 1 S- <br /> PETITION FOR REVIEW OF WASTE DISCHARGE REQUIREMENTS <br /> ORDER NOS. R5-2002-0083 AND R5-2002-0084 <br /> CITY OF STOCKTON REGIONAL WASTEWATER CONTROL FACILITY <br /> "79. The RWQCB further acted arbitrarily and unreasonable in applying the Basin Plan's <br /> narrative water quality objective for lindane rather than the more specific numeric objective found in <br /> the CTA." <br /> When setting effluent limitations, it is necessary to evaluate all water quality objectives and use the most <br /> stringent to protect the beneficial uses. The Basin Plan pesticide objective is more stringent than the <br /> CTR numeric criterion for lindane. The CTR and the SIP specify that the Regional Board should apply <br /> the Basin Plan water quality objective if it is more stringent than the CTR. Therefore, the Basin Plan <br /> objective must be applied. <br /> "80. The permit contains inappropriate effluent limitations for chlorine, based on EPA guidance. <br /> The RWQCB failed to consider the impact of chlorine decay/complexing, ignored pertinent technical <br /> information, and imposed a chlorine limit that is not necessary for the protection of beneficial uses. <br /> The chlorine limitation is inconsistent with the Basin Plan and adopted without compliance with <br /> Porter-Cologne, CEQA, and the APA." <br /> Chlorine is used as a disinfectant at the RWCF and is known to cause toxicity to aquatic organisms. <br /> Based on the effectiveness of dechlorination, chlorine may, at times, be present in the effluent. Thus, <br /> there is a reasonable potential that the discharge will cause or contribute to an excursion above the <br /> narrative toxicity objective. The previous NPDES permit, WDR Order No. 94-324, included a daily <br /> average limitation of 0.018 mg/l and a monthly average limitation of 0.011 mg/l, which were intended to <br /> address short-duration chlorine discharges. Stockton believes these effluent limitations are protective. <br /> However, the chorine residual limitations in Order No. 94-324 were based on receiving water studies <br /> performed by the Sacramento Regional County Sanitation District for its discharge into the Sacramento <br /> River, because Stockton had not yet performed similar studies. The USGS SJR flow gauge at Stockton <br /> has since been installed and much more information is now available regarding the Stockton discharge <br /> conditions. The tidal conditions in the SJR at Stockton are vastly different than in the Sacramento River <br /> in the vicinity of the Sacramento Regional discharge. <br /> The federal regulations at 40 CFR section 122.44(d)(1)(vi)(B), requires the state to establish effluent <br /> limitations to implement narrative objectives using one or more of several options, including using <br /> USEPA's water quality criteria. Order R5-2002-0083 establishes effluent limitations of residual <br /> chlorine consistent with the USEPA Ambient Water Quality Criteria for the Protection of Fresh Water <br /> Aquatic Life, 1984 (EPA 44015-84-030), 0.02 mg/1 as a one-hour average and 0.01 mg/1 as a 4-day <br /> average. This strict application of the water quality criteria is necessary because of periods of little or no <br /> dilution in the receiving.water. Continuous residual chlorine monitoring is currently in place at the <br /> RWCF and the facility is capable of meeting the new limitations. Additionally,based on State Board <br /> Resolution 68-16 ("Statement of Policy with Respect to Maintaining High Quality of Waters in <br /> California") and the federal antidegradation policy, 40 CFR 131.12, the City must, among other <br /> requirements,use best practicable treatment and control technology. In this case, implementation of best <br /> practicable treatment or control, which is already in place, achieves compliance with the effluent <br /> limitations. <br /> "81. The Permit includes effluent limitations for pH based on short-term flow conditions. The pH <br /> effluent limitation is inconsistent with the Basin Plan's use of thirty-day average flow conditions and <br />
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