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REV05177
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REV05177
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Entry Properties
Last modified
8/25/2016 1:03:35 AM
Creation date
11/21/2007 9:23:32 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1980244
IBM Index Class Name
Revision
Doc Date
7/26/2000
Doc Name
PN M-1980-244 CRESSON PROJECT AM-08
From
DMG
To
CRIPPLE CREEK&VICTOR GOLD MINING CO
Type & Sequence
AM8
Media Type
D
Archive
No
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Rationale-Reconenzendation forApproual <br />July 26, 2000 <br />Page 6 <br />contaminants that may be released in the long and short term from the VLF during and after the <br />active mining and leaching. Clearly, there is no discussion of costs to treat planned released from the <br />VLF after puncturing, if the dischazge contain pollutants other than WAD CN at 0:? mg/L. <br />(Roger Flynn: CFV, Kirby Hughes) <br />DMG Response: Detoxification and monitoring covering this issue were approved under Amendment <br />No. 7. The previously Board approved detoxification and monitoring practices have been expanded to <br />address the areas covered under Amendment No. 8. The practices sufficiently address concerns regarding <br />compliance with water quality standards. <br />15. Both exceedances [WAD CN and Zn standards] were explained as upset conditions as a result of <br />heavy precipitation. However, the 1999 rain and snowmelt levels were below the 100-year, 24-hour <br />event, suggesting [hat exceedances are likely to happen again. Rule 3.1.36(b) requires compliance <br />with applicable federal water quality laws & regulations. (J. Lockhart) <br />DMG Response: The finding of "upset condition" at issue was determined by CDPHE under the <br />authority of the Colorado Water Quality Control Act. According to the permit amendment application, <br />exceedances of Zn might be encountered during future upset conditions. If exceedances do occur to surface <br />water, CDPHE is the responsible regulatory agency. <br />16. Due to release of pollutants from the Carlton Tunnel, and the high likelihood of future releases from <br />the same, the applicant must provide adequate water treatment at this location. Since the Carlton has <br />been shown to be a source of water pollution, and the applicant's permit covers the majority of the <br />diatreme, the applicant must take full responsibility for the water that comes out of the Tunnel. <br />Without water treatment, the discharge from the tunnel will not meet water quality standards. <br />Therefore, the permit amendment application must be denied. (Mineral Policy Center) <br />DN1G Response: Past discharges from the Carlton Tunnel have not required water treatment to maintain <br />compliance with the Colorado Water Quality Control Act. The Cresson Operation has maintained an <br />NPDES permit and has been in compliance since operations began. Based on this past performance, the <br />notion that [here is a high likelihood of future releases being out of compliance with standards cannot be <br />sustained. <br />17. The hydrogeochetnical model used in the application does not cover the likelihood of current and <br />future preferential flow through the diatreme. (Mineral Policy Center) <br />DMG Response: The hydrogeochemical model actually depends on preferential flow through carbonate lined <br />fractures to bring potentially acidic waters in contact with those cazbonates. Therefore, the Division does not <br />anticipate changes to water quality. <br />l8. Monitoring of the entire suite of chemicals should be required. (J. Minkler; R. Flynn; R. Fay; <br />K. Hughes) <br />DhfG Response: Water quality monitoring parameters are derived from a mineralogical and water <br />quality assessment. Parameters are selected based on their ability to record a pollutant discharge or to <br />indicate changes in chemical behavior of the system in order [o prevent a discharge of pollutants. Because <br />the ores and waste rock contain only a select number of potential pollutants, the Division does not consider it <br />necessazy to monitor for all regulated pollutants. <br />
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