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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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Attachment B - 3- <br /> Comments <br /> 3_Comments on Tidal Dilution of the Stockton Regional Wastewater <br /> Control Facility Discharge Into the San Joaquin River <br /> April 2001 <br /> 5. The Report uses September 1999 data from the ultrasonic velocity meter located near <br /> the RWCF discharge to simulate the tidal fluctuations. The September 1999 monthly <br /> ave .tie net flow was 916 cfs. The Report adju-rs the monthly average net flow to <br /> 100 cfs. It is not clear where the 100 cfs river flow originates. Jones & Stokes states <br /> in the Flow Report that the minimum monthly average flow at Stockton is 150 cfs. <br /> However, in this Report they use the flow passing Stockton as 100 cfs river flow plus <br /> 50 cfs RWCF effluent. This is not explained in the Report. <br /> 6. The method used in the Report to convert the flow to dry conditions is questionable. <br /> None of the daily net flows are negative, due to the unsupported assumption that daily <br /> net flow reversals do not exist in the river. Department of Water Resources models <br /> suggest that net flow reversals occur during low flow conditions at Vernalis. <br /> 7. The evaluation did not use data from other months of record to determine the affect <br /> on model results. It is possible that after converting the flow to dry conditions, other <br /> months may have extended periods of low flow. The Report makes the assumption <br /> that all months will be the same. The Report also does not evaluate overlap between <br /> months. The critical 30-day period may not occur in a single month. <br /> 8. The box model is composed of water segments with a constant volume of 150,000 <br /> cubic feet. At an average monthly flow of 150 cfs, 43 segments are filled per day. <br /> The Report states that downstream segments are dropped from the model at the end of <br /> each day to avoid having to track so many segments. The Report states, "These <br /> downstream segments do not influence the model results because they have been <br /> placed far downstream from the discharge and lateral mixing is complete by this <br /> time." The Report then contradicts itself in the next paragraph by stating, "During <br /> periods of low net river flows, tidal flows generally move the water past the RWCF <br /> effluent for about 5-7 days. During this time, the water may have effluent added more <br /> than 20 discrete times (i.e., during ebb and flood periods of more than 10 tidal <br /> cycles)." During low net river flows or reverse flows, it would be inaccurate to drop <br /> water segments at the end of each day. <br /> 9. The Report does not define the initial conditions of the box model. The river should <br /> have some concentration of RWCF effluent to begin with. The initial conditions and <br /> the specific steps used to formulate them should be described in the Report. <br /> 10. The study estimates the initial jet dilution as 7:1. However, the study does not <br /> consider the affect of recirculation of the effluent. Due to the tidal influences, the <br /> river is dosed multiple times. The study states, "...the water may have effluent added <br /> more than 20 discrete times..." There may be a 7:1 initial jet dilution with river <br /> r iowever, a substantia' portion of the river water maybe previously discharged <br /> ;, it low, or no flow ca:iditions. <br />
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