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SITE INFORMATION AND CORRESPONDENCE
Environmental Health - Public
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2900 - Site Mitigation Program
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PR0516772
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SITE INFORMATION AND CORRESPONDENCE
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Last modified
6/1/2020 12:44:39 PM
Creation date
6/1/2020 12:23:17 PM
Metadata
Fields
Template:
EHD - Public
ProgramCode
2900 - Site Mitigation Program
File Section
SITE INFORMATION AND CORRESPONDENCE
RECORD_ID
PR0516772
PE
2965
FACILITY_ID
FA0012793
FACILITY_NAME
MUSCO OLIVE LAND APP/TITLE 27
STREET_NUMBER
17950
Direction
W
STREET_NAME
VIA NICOLO
STREET_TYPE
RD
City
TRACY
Zip
95377
APN
20911032
CURRENT_STATUS
01
SITE_LOCATION
17950 W VIA NICOLO RD
P_LOCATION
99
P_DISTRICT
005
QC Status
Approved
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ORDER NO.R5-2002-0148 - 4 - <br /> INFORMATION <br /> 4 -INFORMATION SHEET <br /> MUSCO FAMILY OLIVE COMPANY AND THE STUDLEY COMPANY <br /> WASTEWATER TREATMENT AND LAND DISPOSAL FACILITY <br /> SAN JOAQUIN COUNTY <br /> The tentative WDRs contain the Discharger's proposed flow limit of 800,000 gpd (as a monthly <br /> average), subject to a number of additional restrictions. <br /> Application of wastewater on the land application areas and then bypassing the wastewater/stormwater <br /> mix may result in discharge of wastewater off site, a situation that is expressly prohibited by the WDRs. <br /> Therefore, the tentative WDRs included a prohibition against applying wastewater during the three <br /> months (December-February) when stormwater bypass is proposed and when the water balance <br /> indicates that wastewater will not be applied to land. In response to the tentative WDRs, the Discharger <br /> asked that this prohibition be removed. Staff are uncertain how the Discharger will be able to irrigate <br /> the LTUs during the winter and still be able to bypass stormwater. However, this proposed prohibition <br /> has been deleted with the Discharger's understanding that, as described in the last paragraph of this <br /> section, there is a higher likelihood that it may need to cease production at its facility if it has to collect <br /> more stormwater than anticipated. <br /> Because of the uncertainties of tailwater generation and the importance to preparation of any future <br /> water balances, it is reasonable to require monitoring of the amount of tailwater generated. The <br /> Discharger has verbally described a plan (but has yet submitted a written description)to collect tailwater <br /> from the application areas in collection ditches and return the water to the storage pond in a <br /> sump/pump/piping arrangement. Monitoring of the tailwater will allow a better evaluation of the flow <br /> rate for fixture preparation of water balances. The monitoring might consist of totalizing meters or pump <br /> run time meters. If pump run time meters are used, annual calibration of the meters should be required <br /> because the Discharger has reported inaccurate metered flow rates in the wastewater discharge self- <br /> monitoring data. The Discharger also needs to either directly measure, or accurately estimate, the <br /> amount of stormwater which runs off the land application area and is collected in the storage pond. <br /> Finally, because the water balance contains optimistic assumptions, it is reasonable to include a <br /> requirement to cease the discharge to the either the 1-Mgal settling pond or the 84-Mgal storage pond if <br /> the freeboard in either is less than two feet at any time. This will minimize the possibility of spilling <br /> wastewater into the natural surface water drainage. The Discharger is also required to inform Regional <br /> Board staff of the freeboard violation immediately. <br /> REGULATORY CRITERIA <br /> Based on the available information regarding groundwater quality, the wastewater contains higher <br /> concentration of DIS, sodium, and chloride than the groundwater. It may also contain other analytes in <br /> concentrations higher than the underlying groundwater. The discharge is nonhazardous, but exhibits <br /> characteristics of"designated waste," as defined by CWC Section 13173(b), as the concentrations of <br /> some waste constituents when applied to land have potential for causing exceedances of water quality <br /> objectives or affecting beneficial uses. The discharge contains decomposable waste constituents (e.g., <br /> organic carbon and nutrient compounds) and inorganic dissolved solids in concentrations orders of <br /> magnitude greater than water quality objectives. <br />
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