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SITE INFORMATION AND CORRESPONDENCE_1985-2004
Environmental Health - Public
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SITE INFORMATION AND CORRESPONDENCE_1985-2004
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Last modified
7/23/2020 5:02:50 PM
Creation date
7/23/2020 4:28:31 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
1985-2004
RECORD_ID
PR0506303
PE
2965
FACILITY_ID
FA0001086
FACILITY_NAME
MANTECA PUBLIC WORKS
STREET_NUMBER
2450
Direction
W
STREET_NAME
YOSEMITE
STREET_TYPE
AVE
City
MANTECA
Zip
95336
APN
24130050
CURRENT_STATUS
01
SITE_LOCATION
2450 W YOSEMITE AVE
P_LOCATION
04
P_DISTRICT
005
QC Status
Approved
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• <br /> REVISED WASTE DISCHARGE REQUIREMENTS ORDER NO. 97-115 6 <br /> CITY OF MANTECA AND CITY OF LATHROP <br /> WASTEWATER QUALITY CONTROL FACILITY <br /> SAN JOAQUIN COUNTY <br /> 34. The permitted discharge is consistent with the antidegradation provisions of 40 CFR 131.12 and <br /> State Water Resources Control Board Resolution 68-16. This Revised Order provides for an <br /> increase in the volume and mass of pollutants discharged. This permit will allow ammonia <br /> concentrations to be significantly increased in the discharge, an increase above the concentrations <br /> necessary to meet the toxicity limits of Order No. 97-115. However, because of the small size of <br /> the chronic mixing zone (51 feet long), the increase will not cause significant impacts on aquatic <br /> life,which is the beneficial use most likely affected by the pollutant(ammonia) discharged. <br /> This Order specifically allows toxicity within the mixing zone and the initial zone of dilution. <br /> The increase may also cause a violation of water quality objectives and the narrative toxicity <br /> objective for ammonia within the mixing zone. The mixing zone modeling results submitted by <br /> the Discharger describes the acute and chronic toxicity portion of the plume, in general, as <br /> described in Finding 20 above. The mixing zone modeling study was a conservative model based <br /> on effluent discharged through a diffuser, and restricted to times when the river flow is greater <br /> than 0.56 mg N/1 June to September and 0.69 mg N/1 October to May. The increase in <br /> discharged pollutants will not cause a violation of water quality objectives beyond 51 feet from <br /> the discharge, of either the chronic or acute toxicity objective. To the extent an increase in <br /> discharged pollutants results from this order(by an increase up to the permitted flow volume and <br /> effluent concentration limitations) the impact on water quality will either be localized or <br /> insignificant. Allowing no change to Order no 97-117 would require the discharger to implement <br /> the only alternative to control the ammonia problem by re-designing the entire treatment plant to <br /> provide full nitrification at a capital improvement cost of approximately 10 million dollars (based <br /> on discharger cost analysis). Resolution 68-16 requires that any activity which increases a <br /> volume of a waste must meet waste discharge requirements which will result in the best <br /> practicable treatment or control of a discharge to assure that pollution will not occur and the <br /> highest water quality consistent with maximum benefit to the people of the state will be <br /> maintained. To the extent that any increase is regarded as occurring as a result of this order, it <br /> will allow wastewater utility service necessary to accommodate housing and economic expansion <br /> in the Manteca area, and is considered to be a benefit to the people of the State. <br /> 35. The SWRCB, on 16 May 1974, adopted Resolution No. 74-43 titled "Water Quality Control <br /> Policy for Bays and Estuaries of California". This Policy is applicable to this discharge to the <br /> San Joaquin River, an estuarine water of the state. <br /> 36. Effluent limitations, and toxic and pretreatment effluent standards established pursuant to <br /> Sections 208(b), 301, 302, 304, and 307 of the Clean Water Act (CWA) and amendments thereto <br /> are applicable to the discharge. <br /> 37. The discharge is presently governed by Waste Discharge Requirements Order No. 97-115 <br /> adopted by the Board on 20 June 1997. <br /> 38. The Discharger is required to establish a Pretreatment Program to enforce the requirements <br /> promulgated under Sections 307(b), (c), (d), and 402 (b) of the Clean Water Act. The discharger <br /> does not have an approved and implemented Pretreatment Program yet. The City submitted the <br /> Pretreatment Program to this office,but as of yet has not been approved. This permit contains a <br /> time schedule for implementation of a Pretreatment Program. <br />
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