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GENERAL43353
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Last modified
8/24/2016 8:12:08 PM
Creation date
11/23/2007 12:20:11 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1988112
IBM Index Class Name
General Documents
Doc Date
10/1/1992
Doc Name
MEMO TAILINGS DAM DESIGN BATTLE MOUNTAIN GOLD CROWN JEWEL PROJECT WASHINGTON STATE FILE WITH BMG SAN
From
DMG
To
B HUMPHRIES L OEHLER J PENDLETON & A SORENSON
Media Type
D
Archive
No
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<br />Ctown Jewel Project <br />June 25, 1992 <br />Page 3 <br />current suppositions as to the nature of the emplaced slimes is indexed <br />representative of actual field conditions. <br />Closure - After filling of the impoundment, the area will be capped and graded <br />as necessary to facilitate runoff. Ideally, this will prevent rewet:ting of <br />the slimes thereby minimizing their future liquefaction susceptibility and the <br />volume of leachate that must be treated. Normally, the operator monitors the <br />facility for several years following closure. Thereafter, responsit~ility for <br />maintenance and operation of the facility normally reverts to the State and <br />Federal governments. <br />DSS RATIONALE FOR REJECTING THE PROPOSED UPSTREAM CONSTRUCTION EMBANKMENT <br />SCHEME OVER A MORE CONVENTIONAL EMBANKMENT APPROACH <br />From the DSS's perspective there are three questions that need to ba assessed <br />in determining the appropriateness of a particular embankment construction <br />scheme. What aze the consequences of a failure? Does the proposed design <br />scheme provide a level of reliability that makes a failure appropriately <br />remote given the damage potential? During construction can it be <br />satisfactorily demonstrated by field testing that key parameters related to <br />the stability of the structure equal or exceed design assumptions? <br />f~hat are the consequences of failure? - This project poses a number of <br />difficult issues in estimating the character of the breach, the volume of <br />slime released and the likely extent of slime spreading. A primary issue in <br />this assessment is the motility of the slimes. This will be a function of the <br />degree of saturation of the slimes and the potential for any free water to <br />flow towards the breach in the embankment and entrain slimes. <br />As a minimum, a failure would likely spread slimes several hundreds of feet <br />downstream of the embankment. This would pose an environmental hazard in the <br />form of muddying nearby water courses and concerns of freeing the small <br />residual of cyanide to the environment. The mine operation likely would be <br />halted for a protracted period as it would be a major undertaking to <br />reconstruct the impounding barrier. As a practical matter it woul~. probably <br />be necessary to construct a new dam immediately downstream of the failed <br />section. This would involve an extensive cleanup of the slimes within the <br />footprint of the new dam to properly found it. This cleanup and <br />reconstruction effort would likely be plagued by continuing movements of the <br />slimes from the breached section of the original dam. Furthermore, the <br />likelihood of such a failure is greatest as the impoundment approaches its <br />capacity as the depth of slimes reaches a maximum. In the event of a failure <br />at this time the mine operator would face large costs to restore ttte integrity <br />of the impoundment bu[ with only a minimal prospect for future economic <br />returns. This expenditure would be shortly followed by the costs <essociated <br />with closure of the facility and probably legal fees arising from damage <br />claims. Although a remote possibility, there is the prospect that the <br />operator may not have the resources nor the bonding to cover such costs. <br />State and federal agencies may become, by default, the parties fors:ed to fund <br />large parts of any cleanup and closure activities. <br />
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