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Regional Water Quality Control Board (RWQCB) on April 15, 1966). This caused <br /> elevated TDS levels (high salinity) in the shallow groundwater aquifer underlying <br /> the facility. <br /> In July of 1986 the RWQCB conducted a water quality survey of domestic wells <br /> near the Victor plant after receiving a complaint from a nearby homeowner. On <br /> September 28, 1987, GMI was ordered by RWQCB (Cleanup and Abatement Order <br /> No. 87-733) to develop an alternative method of disposal for process waste water, to <br /> assess the impact on groundwater, and to develop a remediation plan. <br /> As of this date, the company continues to dispose of process waste water to the sur- <br /> face ponds. Contaminated groundwater from the shallow aquifer beneath the ponds <br /> is extracted and mixed with fresh water to achieve a level of total dissolved solids <br /> less than 1200 ppm. This diluted groundwater is then discharged to the Mokulumne <br /> River. Under the current RWQCB order (88-191), this interim disposal of <br /> groundwater to the river and waste water to the ponds was to have ceased by March <br /> 1, 1990. <br /> In order to achieve compliance with this order, Victor Fine Foods elected to dispose <br /> of its process waste waters and the extracted ground water by deep well injection. <br /> EPA's Underground Injection Control (UIC) program received an application from <br /> Golden Gate Fresh Foods, Inc. for one Class I non-hazardous waste injection well. <br /> Following preparation of the draft permit and public comment period, UIC permit <br /> CAS8900000001 was issued on February 9, 1990 and became final on March 12, 1990 <br /> at the end of a 30-day appeal period. <br /> Based on professional judgement, the applicant had identified a suitable zone for <br /> Class I injection at a depth of 2700 feet in the Domengine Formation, just below the <br /> Nortonville Formation. According to the terms of the Class I permit and the re- <br /> quirements set forth in 40 CFR 144.4, the formation waters of the injection zone <br /> must have total dissolved solids (TDS) level greater than 10,000 ppm. Upon reaching <br /> the target zone, chemical analysis indicated that the formation waters had a TDS <br /> level of approximately 7500 ppm, well below that required for Class I injection. <br /> After examination of the character of the fluids to be injected, the applicant deter- <br /> mined that their waste disposal requirements could be met with a Class V injection <br /> well operating in the same borehole at the intended target zone. The applicant then <br /> requested termination of the original Class I permit and made application for a new <br /> Class V permit. <br /> e. Saecial Conditions <br /> The Code of Federal Regulations (CFR) requires that a permit for a Class V well <br /> shall be effective for a fixed term, not to exceed ten years from the effective date. <br /> This permit will be effective for a 10 year period should the permit be issued as <br /> drafted (40 CFR 144.36). The permittee will be authorized to inject for a 10 year <br /> period beginning on the effective date of this permit. <br /> The draft permit contains a condition which states that EPA may, for cause, <br /> modify, revoke and reissue, or terminate the permit in accordance with any ap- <br /> plicable amendments to the Safe Drinking Water Act (SDWA). <br /> 2 <br />