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2009-08-10_GENERAL DOCUMENTS - M1977300
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2009-08-10_GENERAL DOCUMENTS - M1977300
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Last modified
8/24/2016 3:49:32 PM
Creation date
8/13/2009 8:38:41 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1977300
IBM Index Class Name
GENERAL DOCUMENTS
Doc Date
8/10/2009
Doc Name
EPP- SECTIONS 1 to Pg. 9-26
From
Whetstone Associates/Cotter Corp.
To
DRMS
Permit Index Doc Type
Gen. Correspondence
Email Name
DB2
Media Type
D
Archive
No
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Environmental Protection Plan, Schwartzwalder Mine 7-2 <br />• (b) Waste Rock Piles <br />Two reclaimed waste rock piles are associated with the mine. The East and West Waste Rock Piles are <br />located adjacent to Ralston Creek, upstream (west) of the mine. Reclamation of the waste rock piles has <br />been successfully completed, and no impacts to water quality in Ralston Creek are detectable from the <br />waste rock piles. <br />The footprint of the east and west piles at the end of mining (2000) are shown in Figure 2-2. In total, the <br />two piles contain have combined footprint of about 6.3 acres (Figure 2-1). The east pile is larger (about 4.0 <br />acres) than the west pile (about 2.3 acres). Material contained in the waste rock piles includes lime-silicate- <br />hornblende gneiss, garnet-biotite gneiss, mica schist, and smaller amounts of quartzite, pegmatite, and vein <br />material derived from the underground mine and ore-sorter reject rock. Reclamation included capping with <br />3 ft of rock cover, then topping with surface soils and revegetation using the seed mix specified by DMG <br />(now DRMS). <br />Evaluations related to the closure of waste rock piles include stability, geochemical characterization of <br />waste rock, and water quality in streams and groundwater adjacent to the piles. The stability of the piles <br />was summarized in the mine closure hydrology report (Whetstone, 2007). The geochemical characteristics <br />of the waste rock piles are discussed in detail in Section 14(a). The water quality in Ralston Creek above, <br />below, and adjacent to the piles is discussed in Section 11. <br />(c) Fill Material <br />Prior to the construction of mine facilities, waste rock from the mine was placed as fill material in the <br />valley adjacent to Ralston Creek. The fill material covers an area of approximately seven (7) acres, and <br />Ralston Creek was diverted toward the north side of the canyon to make room for mine buildings and <br />• facilities. Although those facilities have been removed, the fill remains in place in the valley floor and has <br />been reclaimed. <br />The composition of the fill is similar to the waste rock piles. During reclamation, additional fill was mined <br />from the Black Forest Mine (east of the Schwartzwalder) and used for cover and fill material in the valley. <br />Rock from the Black Forest Mine is a hornblende gneiss (LSHG) unit, assumed to have the same chemical <br />composition as other LSHG samples that have been analyzed from the site. <br />Groundwater quality in the alluvium and fill is discussed in detail in Section 9(b)(ii). The fill material may <br />be acting as a secondary source of uranium loading to Ralston Creek (Section 11(c)). <br />(d) Flooded Underground Workings <br />U <br />As described previously in Section 1, the Schwartzwalder Mine was kept dry during operations by pumping <br />water from the lower levels of the mine. Water was collected in the 19 Level, pumped to the 7 level, and <br />then pumped to the surface where it was sent through the water treatment plant before being discharged to <br />Ralston Creek. Pumping rates from the underground mine were very low (140 to 310 gpm) for a mine of <br />this size and depth, indicating that the bedrock has very low permeability (Whetstone, 2007). <br />Dewatering of the spiral decline ceased in September 1998, when the pumps at the 22 Leve13 were shut off <br />and the lower workings of the mine were allowed to refill to the 19 Level. Mining operations continued <br />until May 2000, when the pumps were shut off on the 19 and 7 Levels, and the mine was allowed to flood. <br />Refilling rates are discussed in Section 8(b)(iii).4. The portals of the Steve and Pierce adits were <br />bulkheaded in December, 2007, followed by contact grouting in January 2008 (MES, 2008). <br />Water in the flooded underground workings is a strongly-buffered calcium-magnesium-sodium-sulfate <br />water with near neutral pH (median value = 7.17), high concentrations of total dissolved solids (about 3,000 <br />3 Approximately 2,200 feet below the Steve Level <br />4109C.090807 Whetstone Associates 6
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