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43.90(g) • <br />• <br />(g) Corrective Action Program. If the groundwater protection standards <br />established under paragraph 43.90(f) are exceeded at a licensed site, <br />• a corrective action program must be put into operation as soon as is <br />practicable, and in no event later than 18 months after the Agency <br />finds that the standards have been exceeded. The licensee shall <br />submit the proposed corrective action program and supporting rationale <br />for Agency approval prior to putting the program into operation, <br />unless otherwise directed by the Agency. The licensee's proposed <br />program must address removing or treating in place any hazardous <br />constituents that exceed concentration limits in groundwater between <br />the point of compliance and downgradient licensed site boundary. The <br />licensee shall continue corrective action measures to the extent <br />necessary to achieve and maintain compliance with the groundwater <br />protection standard. The Agency will determine when the licensee may <br />terminate corrective action measures based on data from the ground- <br />water monitoring program and other information that provides <br />reasonable assurance that the groundwater protection standard will not <br />be exceeded. <br />(h) In developing and conducting groundwater protection programs, appli- <br />cants and licensees shall also consider the following: <br />(1) Installation of bottom liners. Where synthetic liners are used, <br />a leakage-detection system shall be installed immediately below <br />the liner to ensure detection of any major failures. This is in <br />addition to the groundwater monitoring program conducted as <br />provided in 43.90(m)(2). Where clay liners are proposed or rela- <br />• lively thin, in situ clay soils are to be relied upon for seepage <br />control, tests shall be conducted with representative tailings <br />solutions and clay materials to confirm that no significant <br />deterioration of permeability or stability properties will occur <br />with continuous exposure of clay to tailing solutions. Tests <br />shall be run for a sufficient period of time to reveal any <br />effects that may occur. <br />(2) Mill process designs which provide the maximum practicable <br />recycle of solutions and conservation of water to reduce the net <br />input of liquid to the tailings impoundment. <br />(3) Dewatering of tailings by process devices and/or in situ drainage <br />systems. At new sites, tailings shall be dewatered by a drainage <br />system installed at the bottom of the impoundment to lower the <br />phreatic surface and reduce the driving head of seepage, unless <br />tests show tailings are not amenable to such a system. Where in <br />situ dewatering is to be conducted, the impoundment bottom shall <br />be graded to assure that the drains are at a low point. The <br />drains shall be protected by suitable filter materials to assure <br />that drains remain free-running. The drainage system shall also <br />be adequately sized to assure good drainage. <br />(4) Neutralization to promote immobilization of hazardous constit- <br />uents. <br />• <br />43 - 21 (April 1990) <br />