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2014-05-13_PERMIT FILE - C1996083A (3)
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2014-05-13_PERMIT FILE - C1996083A (3)
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Last modified
8/24/2016 5:43:58 PM
Creation date
5/21/2014 9:22:10 AM
Metadata
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Template:
DRMS Permit Index
Permit No
C1996083A
IBM Index Class Name
Permit File
Doc Date
5/13/2014
Doc Name
pages 2.05-84 to 2.05-165
Section_Exhibit Name
Volume I 2.05 Operation and Reclamation Plans Part 2
Media Type
D
Archive
Yes
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As explained in Section 2.04.7, the Bowie No. 2 Mine is experiencing an <br />inflow of approximately 700 gpm. Recent mine water quality analysis are <br />shown above in section 2.05.6(3)(a)(iv). For the purposes of this PHC a <br />worst case mine inflow /discharge of 1,000 gpm from Outfall 006 is utilized. <br />Flow from outfall 006 need only travel a short distance to enter a highway <br />culvert and join the North Fork of the Gunnison River. See Map 41, Mine <br />Discharge Pipe Alignment. The heavily vegetated water course from Outfall <br />006 to the highway culvert will eliminate the possibility of sediment entering <br />the North Fork of the Gunnison River, due to erosion. Since the mine <br />discharge will mix with the River water in a relatively short distance, there are <br />no lands, river banks, structures, alluvial valley floors or prime farm land on <br />either side of State Highway 133 that potentially may be adversely affected <br />by the mine water discharge quantity or quality. <br />The average TDS and total recoverable Manganese measurements at the <br />upstream North Fork of the Gunnison River monitoring station for the <br />baseline period (2007 AHR) are 130 and 0.015 mg /I respectively. The <br />average iron measurement at the upstream North Fork of the Gunnison River <br />monitoring station for the baseline period (2007 AHR) is 0.09 mg /I. The <br />• following table presents the estimated affect the average mine water quality <br />(page 2.05 -70i) will have on the quality of water in the North Fork of the <br />Gunnison River at low flow: <br />PHC North Fork of the Gunnison River <br />Based upon the above calculations, the mine discharge into the North Fork of <br />the Gunnison River will not have a measurable impact on total recoverable <br />manganese or total recoverable iron in the river. TDS values in the river <br />would increase under rare low flow conditions. <br />PR -12 2.05-110 02/10 <br />it I16 [/0 <br />Flow <br />Gpm <br />Flow <br />Cfs <br />TDS <br />mg /I <br />Manganes <br />a <br />Trec. mg /I <br />Iron <br />Trec, mg /I <br />North Fork <br />11,220 <br />25 <br />130 <br />0.015 <br />0.09 <br />Mine Discharge <br />j 1,0001 <br />2.2 <br />2,838 <br />0.0371 <br />2.43 <br />Combined Flow <br />1 12,2201 <br />27.2 <br />3521 <br />0.0171 <br />0.28 <br />Based upon the above calculations, the mine discharge into the North Fork of <br />the Gunnison River will not have a measurable impact on total recoverable <br />manganese or total recoverable iron in the river. TDS values in the river <br />would increase under rare low flow conditions. <br />PR -12 2.05-110 02/10 <br />it I16 [/0 <br />
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