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2017-04-26_REVISION - M1977300
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2017-04-26_REVISION - M1977300
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Entry Properties
Last modified
12/21/2020 3:29:34 PM
Creation date
4/28/2017 5:01:07 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1977300
IBM Index Class Name
Revision
Doc Date
4/26/2017
Doc Name
Request for Technical Revision
From
Cotter
To
DRMS
Type & Sequence
TR25
Email Name
MAC
WHE
Media Type
D
Archive
No
Tags
DRMS Re-OCR
Description:
Signifies Re-OCR Process Performed
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Technical Revision 25 Schwartzwalder Mine <br /> ' chemicals, toxic or acid-forming materials and describe how unauthorized discharge of acid mine <br /> drainage will be prevented. <br /> ' No designated chemicals are currently in use or being stored at the Schwartzwalder Mine site. No acid- <br /> forming materials exist onsite. Native rock at the Schwartzwalder Mine is not acid-generating. Instead, it <br /> ' is classified as having a low potential to generate acidic drainage, and no acidic drainage has occurred <br /> from the mine or waste rock facilities to date. Geochemical characterization of the waste rock piles is <br /> described in Section 14 of the Revised EPP. The water quality of the flooded mine workings is described <br /> ' in Section 9(b)(iv) of the Revised EPP. The pH of groundwater in the flooded mine is near neutral, and <br /> has been stable (no obvious increasing or decreasing trend) since monitoring of mine water began in <br /> ' 2000. The mine pool has shown no potential to generate acid. <br /> The flooded mine workings and the alluvium and fill have been identified as toxic-forming materials on <br /> ' the basis of(1) uranium and radium-226 in groundwater in the underground mine pool and (2) uranium in <br /> groundwater in the alluvium and fill. The hydrogeologic conceptual model is described in Section 8(e) of <br /> the Revised EPP. Water quality in the mine pool is summarized in Table 9-8 and discussed in Section <br /> ' 9(b)(iv) of the Revised EPP. Water quality in the alluvium and fill is summarized in Table 9-3 and <br /> discussed in Section 9(b)(ii) of the Revised EPP. Potential mitigation options for groundwater are <br /> discussed in Section 15 of the Revised EPP along with a proposed schedule for feasibility investigations, <br /> ' engineering design, and implementation. <br /> 3.2.3 Geological and Geochemical Conditions <br /> ' Section 8 of the Revised EPP presents geological conditions, and Section 14 of the Revised EPP presents <br /> geochemical conditions. <br /> ' 3.2.4 Monitoring and Sampling <br /> Water levels will be monitored in the clean water, treated water, and reactor tanks in the following <br /> manner: <br /> ' • Water levels within the two, 20,000-gallon storage (treated water) tanks (which are connected via <br /> a 4"pipeline) are monitored with a pressure transducer connected to the programmable logic <br /> controller(PLC). The PLC maintains the levels within the tanks to a determined height by <br /> ' speeding up or slowing down booster pumps that draw from these storage tanks and provide <br /> pressure for the RO system. <br /> • Water levels within the reactor tank will be monitored by a pressure transducer connected to the <br /> ' PLC. Water level control is accomplished by a throttling valve. <br /> • Water levels within the clean water tank will be monitored by a pressure transducer connected to <br /> the PLC. <br /> The treated water tanks and the reactor tank will not be Y <br /> sampled routinely. However, the clean water tank <br /> will be sampled as required by Cotter's discharge permit CO-0001244. Sampling will occur from a <br /> ' sampling port within the NWTP building immediately upstream of the clean water tank, except for pH. <br /> ' Mine Permit M-1977-300 <br /> Cotter Corporation(N.S.L.) 14 April 2017 <br />
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