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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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WASTE DISCHARGE REQUIREMENTS ORDER NO.R5-2002-0148 - 16- <br /> MUSCO FAMILY OLIVE COMPANY AND THE STUDLEY COMPANY <br /> WASTEWATER TREATMENT AND LAND DISPOSAL FACILITY <br /> SAN JOAQUIN COUNTY <br /> c. The wastewater is nonhazardous waste and need not be managed according to Title 22, CCR, <br /> Division 4.5, Chapter 11, as a hazardous waste. <br /> ANTI-DEGRADATION ANALYSIS <br /> 76. State Water Resources Control Board (State Board)Resolution No. 68-16 (hereafter Resolution <br /> No. 68-16)requires that waste be discharged in a manner that maintains the high quality waters of <br /> the state. Any change in quality can occur only after full application of best practicable treatment <br /> and control (BPTC) of the waste, and must be consistent with maximum benefit to the people of <br /> the State, not unreasonably affect a beneficial use, and not result in water that exceeds a water <br /> quality objective. Where the water quality objective is exceeded in background water quality but <br /> nonetheless beneficially used or designated for beneficial use, the background water quality cannot <br /> be degraded. <br /> 77. Antidegradation factors have been considered pursuant to Resolution No. 68-16. The project as <br /> proposed does not threaten to degrade groundwater with nitrogen, assuming that the proposed <br /> intensive cropping can be maintained. The project as proposed may degrade or cause degradation <br /> of groundwater and possibly create nuisance from organics while waste is ponded and in the <br /> manner applied to land. As described in Finding No. 26, the project as proposed will certainly <br /> cause pollution with constituents of salt. Degradation of the groundwater with organics and salt is <br /> not consistent with maximum benefit to the people of the State. If it were, the Discharger would <br /> have to demonstrate its treatment as being best practicable treatment and control (BPTC). The <br /> Discharger has made no BPTC demonstration. In short, the project as proposed by the Discharger <br /> is not consistent with Resolution 68-16. <br /> 78. In considering potential salt degradation of groundwater from the discharge, the salt already within <br /> the LTU and underlying soil profile must be considered, and elevated salt is already within the <br /> LTU and likely in the soil profile below it given past practices of the Discharger. Given the <br /> unacceptability of the salt proposed for discharge, it is not necessary to quantify this factor. <br /> 79. Following adoption of WDRs Order No. 97- 037, the Discharger has been provided ample <br /> opportunity to justify a discharge and comply with Order No. 97-037. It has not complied. It has <br /> been granted interim conditional flow increases while under a series of enforcement actions while <br /> developing justification for discharge, and violated those conditions including repeated failure g g p e to <br /> monitor waste and submit reports as required, and failure to restrain production in accord with <br /> enforcement conditions, resulting in administrative civil liability. The RWD is inadequate to <br /> support the requested discharge. Therefore, this Order limits the Discharger to that which will not <br /> degrade the underlying groundwater. <br /> GROUNDWATER DISCHARGE ANALYSIS —LAWS, RULES,AND REGULATIONS <br /> 80. For the waste constituents present in the discharge in significant concentrations, the water quality <br /> objectives determined by the translator process from narrative objectives are all less than observed <br /> background water quality, except for nitrate. Because all forms of nitrogen can convert to nitrate <br />
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