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SITE INFORMATION AND CORRESPONDENCE
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PR0524190
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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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INFORMATION SHEET -4- <br /> CITY OF STOCKTON <br /> REGIONAL WATER QUALITY CONTROL PLANT <br /> SAN JOAQUIN COUNTY <br /> meet the limitation for ammonia without proceeding with plant improvements. Until such time <br /> as other sources of oxygen demand impacting the San Joaquin River in the vicinity of Stockton <br /> have been identified and addressed, the Board does not believe that it is reasonable to require <br /> reductions in effluent CBOD and ammonia beyond the levels required by the new final effluent <br /> limitations. <br /> Based on the City's model, three different CBOD and ammonia limitations are prescribed for <br /> different times of the year. <br /> - For the months when water temperatures are cool (1 December through 31 March) a <br /> monthly average of 20 mg/l CBOD is prescribed. The model found that ammonia did <br /> not exert a measureable oxygen demand when water temperatures are low because of <br /> significantly reduced metabolic rates in nitrifying organisms at these lower temperatures. <br /> Therefore no ammonia limitation is prescribed for these months. A CBOD limitation was <br /> prescribed rather than a BOD limitation, because the BOD test is conducted at a <br /> standardized warm temperature at which the oxygen demand of the ammonia would be <br /> exerted, showing an apparent oxygen demand in the laboratory test which does not <br /> properly predict the oxygen demand on the receiving water, which is cooler. <br /> - For the months when water temperatures are warm ( 1 April through 31 October), a <br /> monthly average of 10 mg/l CBOD and a monthly average of 2 mg/l ammonia are <br /> prescribed. Due to the warmer water temperatures, the metabolic rates of organisms <br /> oxidizing carbonaceous and nitrogenous compounds are increased, increasing the impact <br /> of the effluent on the receiving water. Also, during these months, there are frequent, <br /> sustained periods with low net flow or reversals of the flow in the River due to pumping <br /> of water from the South Delta. The low net flow and flow reversals result in very little <br /> dilution of the effluent in the receiving water. Tides move a mixture of wastewater and <br /> receiving water back and forth past the discharge point, so that the "receiving water" for <br /> the discharge already contains significant portions of wastewater. <br /> - For November, intermediate effluent limits of 15 mg/l CBOD and 10 mg/l ammonia are <br /> prescribed. The proposed nitrifying treatment facility to be built by Stockton will use <br /> nitrifying bacteria to reduce the ammonia concentrations in the effluent. The nitrifying <br /> bacteria in the plant can not be instantaneously turned on and off, but will slowly change <br /> the effluent quality as process modifications are made and the temperature of the <br /> wastewater changes seasonally. The City's model has demonstrated that an intermediate <br /> level of treatment during this transition period in the wastewater treatment plant will not <br /> increase the impact of the wastewater discharge during November. <br /> Daily maximum effluent limitations for BOD and TSS are established in this permit as <br /> allowed under state regulations. The daily maximums for BOD and TSS are based on <br /> professional judgement, having been found to be technically achievable at a properly operating <br />
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