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III IIIIIIIIIIIII III ~ ~ <br /> STATE OF <br />DIVISION OF MINERALS AND GEOLOGY <br />Department of Natural Resources <br />1 313 Sherman Si.. Roam 215 <br />Denver, Colorado 80203 <br />Phone. {3031 866-3567 <br />FAX: (3071 832-8106 <br />February 12, 1999 <br />Mr. Scott Hoover <br />B & B Excavating, Inc. <br />Drawer 249 <br />COLORADO <br />J <br />DEPARTMENT <br />NATURA~a <br />RESOURCE <br />Roy Romer <br />Governor <br />tames 5. Lochhead <br />Fzecutive Director <br />Michael B. Long <br />Vall, C~ 81658 Division Duector <br />RE: Amendment to Sampling and Analysis Plan, Montgomery Pit, Permit No. M-86-104 <br />Dear Mr. Hoover: <br />The Division of Minerals and Geology (DMG) has completed a review of the "Amendment to <br />Sampling and Analysis Plan" (SAP amendment) for the Montgomery Pit herbicide release. The SAP <br />amendment was prepared by Greg Lewicki and Associates and submitted to DMG on February 2, <br />1999. The following issues remain to be addressed to the satisfaction of DMG prior to implementation <br />of the SAP amendment. <br />Please provide a statement that those portions of the Draft Sampling and Analysis Plan <br />prepared by Dames and Moore and submitted to DMG on December 18, 1999 [hat are no[ <br />modified by the SAP amendment will remain as components of the sampling and analysis plan. <br />Specifically, sections 4.4, 4.5, 4.6, 4.7, 5.0, and Appendix D from the Dames and Moore <br />sampling and analysis plan must be adhered to during implementation of the SAP amendment. <br />In addition, pertinent portions of section 4.3 must be adhered to relative to the procedure for <br />conducting ambient temperature headspace testing with the photo-ionization detector. <br />Under the terms of the SAP amendment, an on-site hazardous waste repository and treatment <br />cell may or may not be needed depending on whether or not contamination in excess of ]0 <br />mg/kg 2,4-D is found at the site. The DMG suggests that the treatment cell be constructed with <br />a composite liner rather than with the clay liner that is proposed, for the following reasons: <br />a) It is not known how long it will take for the 2, 4-D [o decompose to below the ]0 mg/kg <br />limit in the treatment cell. During the period [hat the hazardous material is present in <br />the cell a clay liner would be susceptible to damage by desiccation cracking and <br />freeze/thaw effects. <br />b) 2,4-D, bromacil, or diesel fuel may permeate through the clay and be released to [he <br />environment during the period of storage in the treatment cell. The likelihood of this <br />occurring would be increased if any precipitation were to accumulate in the cell. <br />Assuming a hydraulic conductivity for the clay of 4.7 x 10' m/s and an areal extent for <br />the cell of 1,800 square feet, permeation of contaminants through the proposed 6 inch <br />