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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
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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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RESPONSE TO WRITTEN COMMENTS <br /> City Of Stockton-Regional Wastewater Control Facility 6 <br /> NPDES No. CA0079138 <br /> 26 April 2002 Board Meeting <br /> The chronic dilution report calculated "actual dilution"using the effluent and receiving water data, in <br /> a manner similar to the calculations provided by staff in Table 8-1. During this critically dry period, <br /> the maximum instream ammonia concentration observed was about 6.2 mg/1, with a maximum 30-day <br /> average ammonia concentration of 5.55 mg/I(see Fact Sheet @ 25).4 Over this period,the effluent <br /> ammonia concentration averaged 19 mg/l. Together these data demonstrate available dilution on the <br /> order of 3.4:1. <br /> RWQCB Response: The data referred to in the above comment are from receiving water monitoring <br /> stations R-2 and R-3, which are significant distances from the discharge. In addition, the monitoring <br /> is sporadic with only monthly monitoring during the winter months when the RWCF has the <br /> propensity to discharge high levels of ammonia. Frequent monitoring closer to the outfall is needed to <br /> determine the actual dilution. <br /> Stockton Comment No. I.D (1)• UVM data are reliable for predicting critical low flow. <br /> RWQCB Response: The Regional Board does not agree with the findings of the Jones & Stokes flow <br /> model. Detailed comments are provided in Attachment A. <br /> Stockton Comment No. I.D (2)• Box Model accurately predicts dilution. <br /> RWQCB Response: The report describing the Box Model is void of information regarding the <br /> calibration and validation of the model. Therefore, it is premature to state that the Box Model <br /> accurately predicts dilution. The Regional Board has many concerns regarding the Jones & Stokes <br /> Box Model. Detailed comments are provided in Attachment B. <br /> Stockton Comment No. LD (3) and (4)• Acute and chronic dilution are available. Also, the UVM <br /> gauge cannot be used on a day-to-day basis to estimate actual dilution flow. <br /> RWQCB Response: During above average wet years the chronic dilution was estimated to be as low <br /> as 5:1 (Fact Sheet @ 13). This is based on net SJR flows and the actual RWCF flow. Using the wet <br /> year 7-day average SJR flow (102 cfs) and the maximum consecutive 4-day average flow from the <br /> RWCF (95.5 cfs), as called for by the SIP, the estimated dilution credit is only 1.07:1. This suggests <br /> that during a wet year there could be minimal dilution. As discussed above in greater detail in the <br /> response to Stockton Comment No. LC (1), the 7-day average SJR flow at Stockton could be much <br /> less during a critically dry year. Therefore, it is reasonable to assume that during a critically dry year, <br /> there would be minimal to no dilution. The City proposes that there is chronic dilution based on the <br /> Hall &Associates chronic dilution model and the Jones & Stokes Box Model. Detailed comments <br /> regarding the models are contained in Attachments B and C. With regards to the acute dilution, we <br /> agree that the UVM data cannot be used on a day-to-day basis to estimate dilution. Dilution credits <br /> for acute dilution have not been granted, in part, because there is little or no chronic dilution based on <br /> minimal weekly and monthly average flows,. Since the acute averaging period is much shorter than <br /> the chronic averaging period, there cannot be any acute dilution either. <br />
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