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SITE INFORMATION AND CORRESPONDENCE_CASE 2
Environmental Health - Public
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SITE INFORMATION AND CORRESPONDENCE_CASE 2
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Last modified
11/15/2019 1:40:39 PM
Creation date
11/15/2019 1:28:05 PM
Metadata
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Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
FileName_PostFix
CASE 2
RECORD_ID
PR0505422
PE
2965
FACILITY_ID
FA0006902
FACILITY_NAME
TRACY WASTEWATER TX PLNT
STREET_NUMBER
3900
STREET_NAME
HOLLY
STREET_TYPE
DR
City
TRACY
Zip
95376
CURRENT_STATUS
01
SITE_LOCATION
3900 HOLLY DR
P_LOCATION
03
P_DISTRICT
005
QC Status
Approved
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REGIONAL WATER BOARD RESPONSE (SWRCB/OCC File A-1846(a) and A-1846(b)) -9- <br /> PETITIONS FOR REVIEW OF Vim,E DISCHARGE REQUIREMENTS `j <br /> ORDER NO. R5-2007-0036 (NPOES NO. CA0079154) AND <br /> TIME SCHEDULE ORDER NO. R5-2007-0037 <br /> CITY OF TRACY, WASTEWATER TREATMENT PLANT <br /> would require the implementation of reverse osmosis, while these actions and TMDLs are <br /> pending, is inconsistent with the Manteca order. <br /> Considering the actions by the Regional Water Board to develop a new salinity policy for the <br /> Central Valley and based on the fact that the Discharger could not reasonably b6 expected fo <br /> achieve compliance with final salinity WQBELs within the five year life of the Order, on <br /> 4 August 2006, Regional Water Board staff recommended for adoption a proposed Order that <br /> did not include final WQBELs for salinity. Instead, the proposed Order included an interim <br /> performance-based effluent limitation for EC and required the Discharger to implement <br /> measures to reduce the salinity in its discharge to Old River. The proposed Order required the <br /> Discharger develop and implement a pollution prevention plan for salinity, required an <br /> submittal of annual reports demonstrating its efforts to reduce salinity, and established an <br /> intermediate salinity goal of 1350 pmhos/cm as EC to be achieved during the permit term. In <br /> addition, the proposed Order included a requirement to study the affects of the saline <br /> discharge in the South Delta and a reopener provision to allow modification of the permit <br /> requirements, if necessary. <br /> The Regional Water Board held a lengthy hearing on the proposed Order at the August 2006 <br /> Regional Water Board meeting, with salinity issues being the major topic of testimony and <br /> Board discussion. The hearing was continued pending a better assessment of the impacts of <br /> the discharge on Delta salinity and development of alternative means of regulating salinity for <br /> Regional Water Board consideration. The Regional Water Board was concerned with the <br /> possible impacts of the discharge without requiring final WQBELs, especially considering the <br /> impaired nature of the southern Delta, and directed staff to work with the Discharger, the <br /> Department of Water Resources (DWR), and other stakeholders to model the affects of the <br /> discharge in the southern Delta. It was suggested that DWR's Delta Simulation Model II <br /> (DSM2), which has been used extensively for the South Delta Improvements Project (SDIP), <br /> could be used for this purpose. A stakeholder group that included staff from the City of Tracy, <br /> Mountain House Community Services District, South Delta Water Agency, CSPA, DWR, and <br /> the Regional Water Board was formed to develop appropriate scenarios for running the DSM2 <br /> model. The model was run under reasonable worst-case conditions, with temporary barrier <br /> operations to evaluate current conditions and with permanent operable gates to evaluate <br /> future conditions. Attachment H of the Order R5-2007-0036 provides a detailed description of <br /> the modeling scenarios. <br /> The DSM2 modeling demonstrated that even under reasonable worst-case conditions the <br /> Tracy discharge has limited impacts on the salinity problem in the southern Delta (see <br /> Figure 1, below). Furthermore, the Order includes an interim performance-based effluent <br /> limitation for total dissolved solids (TDS) that limits the annual mass loading of TDS to current <br /> levels. This mass loading limitation will require the EC concentration to decrease as the . <br /> discharge flow rate increases, which is expected to occur as the Discharger increases it use of <br /> a new, less saline water supply. The DSM2 modeling output predicts reduced EC impacts in <br /> the southern Delta as the City of Tracy discharge increases, due to the reduction in the <br /> concentration of EC (see Table 2). <br />
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