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GENERAL45209
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Last modified
8/24/2016 8:14:06 PM
Creation date
11/23/2007 1:38:07 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1980244
IBM Index Class Name
General Documents
Doc Date
1/12/1995
Doc Name
PIT RACKFILL CLOSURE COVER SYSTEM DESCRIPTION RICHMONG HILL MINE LEAD SOUTH DAKOTA
From
GOLDER ASSOCIATES
To
LAC MINERAL USA INC
Media Type
D
Archive
No
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<br />n <br />criteria. <br /> <br />By July I, 1994, LAC Minerals sB~! submit for approval a Performance Monitoring Plan <br />that will be used as a basis for ~ jng performance of the various components of the <br />reclaimed facility, including the ante Impoundment, the South Waste Dump, <br />rnr-taminated groundwater in the pit andS.svaste dump area, the Leach Pads, and ancillary <br />facilities. The performance monitoring plan shall take into account the concepts described <br />in the examples given below. <br />The Department will develop site-specific performance criteria (or standards) for each <br />component of the reclaimed facility after reclamation has been completed, when achievable <br />cleanup limits can be realized. After performance criteria are developed, if any reclaimed <br />component of the facility is generating AMD-related contamination to the point where <br />performance criteria are not being complied with, LAC Minerals shall submit for approval <br />a site-specific mitigation plan as per condition no. 5 under Postclosure. <br />The Department may alter the performance criteria based on the annual assessments and <br />changing conditions at the site. For clarification, it should be understood that compliance <br />with performance criteria will be based on expected trends in environmental monitoring <br />as the r~ecLumed system approaches ambient conditions and/or equilibrium. For example: <br />a. The water quality of contaminated groundwater in Spruce Gulch should be <br />expected to reach ambient conditions in 30 years and approach that level at a <br />predictable rate and according to a calculated curve. Perturbations away from the <br />curve may trigger alternative reclamation work, depending on the degree of <br />perturbation and associated environmental impacts, and <br />b. Temperature and oxygen concentrations in the reclaimed backfill material, the <br />moisture content of the clay layer, and infiltration rates as recorded by the quantity <br />of water collected in lysimeters, should reach equilibrium within approximately <br />two years. These type of physical monitoring measures, taken at the same time <br />each year, will assess the success of the pit/waste impoundment. <br />15 <br />
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