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2013-07-29_GENERAL DOCUMENTS - C2009087
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2013-07-29_GENERAL DOCUMENTS - C2009087
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Last modified
8/24/2016 5:22:59 PM
Creation date
7/31/2013 8:54:29 AM
Metadata
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Template:
DRMS Permit Index
Permit No
C2009087
IBM Index Class Name
General Documents
Doc Date
7/29/2013
Doc Name
Modifying Discharge Point of Compliance for Selenium
From
Brownstein Hyatt Farber Scheck
To
DRMS
Permit Index Doc Type
General Correspondence
Email Name
JDM
DIH
Media Type
D
Archive
No
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Case 3:05 -cv -00784 Document 133 -2 Filed 07/14/06 Page 3 of 5 PagelD #: 4500 <br />memo states, in part, that impoundments created by the discharge of fill material and <br />permitted by the Corps under CWA section 404 for purposes of creating a waste <br />treatment system. "would no longer be waters of the United States." The memo goes on <br />to clarify that discharges into such waste treatment systems do not require a CWA permit, <br />although discharges from these systems to waters of the U.S, would require a permit <br />under CWA Section 402 from EPA or an approved State program. <br />In May, 2004, EPA provided additional information clarifying the framework <br />governing the regulation of mine tailings discharged in waters of the U.S. associated with <br />hard rock mining in Alaska. (See May 17. 2004 memorandum from Diane Regas, James <br />Hanlon. and Geoffrey Grubbs to Randy Smith regarding Clean.Water Act Regulation of <br />Mine Tailings.) In that memo. EPA recognized that the agencies' revised definition of <br />the term "fill material" (67 Fed. Reg. 31129. May 9, 2002) makes clear that mine tailings <br />placed into i mpounded, waters, as proposed in the Kensington mine project in Alaska, are <br />regulated as a discharge of fill material under CWA Section 404 because the tailings have <br />the effect of raising the bottom elevation or converting waters'to dry land. Our <br />conclusion in that memo is based on the agencies' analysis of how the May 9, 2002, <br />rulemaking.applies to the regulation of discharges of mine tailings into waters impounded <br />for the purpose of containing and isolating those materials. The memo proceeds to <br />clarify that the rulemaking did not alter our interpretation of the waste treatment <br />exclusion as defined in the agencies' regulations. While the agencies chose not to rely on <br />the use of the wastq treatment system exclusion in the permitting context for the <br />Kensington mine. nothing in the May 2004 memo was intended to preclude us from <br />relying on use of the exclusion in other circumstances that meet the'agencies' definition. <br />The waste treatment system exclusion continues to apply to the creation or use of <br />a waste treatment system in waters below a valley fill permitted by the Corps under CWA <br />Section 404.1 As provided in the agencies' regulations. a waste treatment system is <br />"designed to meet the requirements of the CWA," (40 CFR 232.2 and 33 CFR 328.3(a).) <br />The Corps. EPA and states ensure that the waste treatment systems meet those <br />requirements through the section 404 permitting process for discharges of dredged or fill <br />material, the section 402 permitting process for discharges from the sediment pond, and <br />the section 401 certification process. A11 three programs ensure that the system is <br />constructed and operated in compliance with the CWA. In older to minimize the <br />physical extent of the waste treatment system and to reduce potential adverse <br />environmental effects, to the maximum extent practicable the Corps requires under its <br />Section 404 authorities that the sediment pond be located as close to the toe of the valley <br />fill as possible2. However, it is generally not practicable to locate the sediment pond <br />I <br />'The agencies' designation of a portion of the waters of the U.S. as part of a waste treatment system does <br />not itself alter CWA jurisdiction over any waters remaining upstream of such system. <br />The siting of sediment ponds below the valley till is dependent on a number of site specific engineering <br />and environmental factors. Ponds are designed and located to ensure that they have sufficient volume and <br />reduce the rate of flow to provide for effective settling of suspended sediments. The agencies require that <br />ponds be located as close as is practicable to the toe of the till in order to minimize temporary adverse <br />environmental impacts associated with the construction and operation of the waste treatment system,. <br />
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