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CA ARNG Field Quality Assurance Project Plan <br />• Casing sections adjacent to saturated, relatively low -permeability clayey zones, as inferred from the <br />natural gamma logs and available well construction data, including the Corcoran Clay. <br />8.5.2 An average of four perforations per line foot (LF) of casing will be made. The perforations will be <br />cut at 90 degree intervals around the casing circumference and will be at least one -quarter -inch wide and <br />2 inches long. The wells will then be abandoned by backfilling the casing with grout in lifts. The <br />remainder of the casing will then be perforated and grouted in stages, as appropriate. <br />8.5.3 As previously noted, decommissioning techniques for wells with extensive filter packs and cable <br />tool wells directed toward sealing aquitards should be the focus of the effort. As with filter packed wells, <br />perforating cable tool wells adjacent to a permeable zone may severely limit efforts to achieve an <br />adequate seal adjacent to aquitards because permeable geologic materials will more readily accept grout <br />during the sealing operation. <br />8.5.4 The perforations will facilitate the flow of sealing material from the well casing into the annual <br />space/gravel pack and aquitard. The grout should effectively seal the well casing and prevent it from <br />serving as a pathway for contaminant migration from shallow to deeper zones. <br />8.6 Final Abandonment Procedures <br />After the casing has been backfilled with grout, the protective casing will be removed and the well casing <br />cut off at least 2 feet below grade and removed. Additional grout will continue to be added to the casing <br />if any settlement occurs. Approximately 24 hours after the backfilling is completed, the grout will be <br />topped off and any surface depression filled with soil material and slightly mounded to allow for <br />settlement. All downhole equipment should be steam -cleaned between wells (see Section 9.3). <br />-8.7 Regulatory Issues and Permits <br />8.7.1 Wells to be abandoned will be destroyed according to minimum requirements set forth in Bulletin <br />74-90, California Well Standards, prepared by the State of California Department of Water Resources <br />(DWR). The DWR has responsibility for developing these standards under California Water Code <br />Section 231. According to these standards, abandoned wells must be destroyed to ensure the quality of <br />groundwater is protected and eliminate a possible physical hazard to humans and animals. <br />8.7.2 Each well must be investigated before it is destroyed to determine its condition and details of its <br />construction prior to abandonment. All undesirable materials and obstructions that would interfere with <br />well destruction must be removed (DWR, 1991). <br />8.7.3 If the presence of contaminants is known or suspected in a well to be destroyed, all applicable <br />agencies overseeing the individual facilities shall be notified as soon as possible. The enforcing agency at <br />CA ARNG facilities will vary at the different agencies. <br />8.7.4 Minimum well abandonment guidelines require that the well casing will be completely filled with <br />sealing materials. If the hole is deeper than 30 feet, sealing materials must be placed under pressure and <br />tremied to prevent separation of the grout components. Sealing materials must be placed continuously <br />from bottom to top unless conditions in the well dictate that sealing operations be conducted in a staged <br />manner. It must be verified that the volume of sealant equals or exceeds the volume of the casing to be <br />filled and sealed. Suitable sealing materials include neat cement, sand cement, and bentonite (DWR, <br />1991). <br />field QAPP.DOC 8-5 May 2000 <br />