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2009-10-30_PERMIT FILE - C1982056A (5)
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2009-10-30_PERMIT FILE - C1982056A (5)
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Last modified
8/24/2016 3:56:36 PM
Creation date
2/9/2010 10:39:29 AM
Metadata
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Template:
DRMS Permit Index
Permit No
C1982056A
IBM Index Class Name
Permit File
Doc Date
10/30/2009
Doc Name
Pages 2.05-123 to 2.05-197.3
Section_Exhibit Name
2.05.5 Postmining Land Uses
Media Type
D
Archive
Yes
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The mining in the EMD will result in subsiding areas where springs exist. TCC's experience is that there will be <br /> a temporary disruption in flow, and then recovery of the springs. The reader is referred to TCC's 1996 AHR for <br /> a further discussion of the recovery of springs SW1 and SW2. No long -term impacts are anticipated to the <br /> springs in this area. <br /> The present interpretation of the impacts of subsidence on the water - bearing strata in the study area is supported <br /> by numerous studies in various coalfields worldwide. <br /> Subsidence Impacts on Ground Water Quality <br /> The potential impacts of subsidence on ground water quality could develop in the following ways: <br /> • Caved overburden materials replace part of the coal seam unit; and <br /> • Fracturing develops a new hydraulic connection between units with different water quality. <br /> The first potential impact is applicable only in cases where the coal seam acts as a unit, which is not the case in <br /> the study area. The second example is more common in cases where several units with different water quality <br /> are, present. In the Foidel, Middle and Fish Creek alluvium areas, the potential interconnection could be, for <br /> example, between the Twentymile Sandstone and the alluvial unit. One apparent impact to the Twentymile <br /> Sandstone from subsidence is the drop in water level in monitoring well 006- 82 -48A. This drop in water level is <br /> attributed to a possible mechanical failure of the casing and loss of the well seal, or increased porosity resulting <br /> in a lowering of the water level. Monitoring Well 006 -82 -48A was installed in a borehole that had originally <br /> been drilled through the Twentymile Sandstone to the Wadge Seam. Although subsidence may have resulted in <br /> the loss of this well, no impacts on the ground water quality in the Foidel and Middle Creek alluviums are <br /> anticipated. This conclusion is consistent with experience in other coal fields. <br /> S Most of the studies of subsidence effects of surface and ground water quality in the Appalachian coal fields <br /> concluded that no significant long -term effects on water quality were observed, which confirms observations <br /> from the Foidel Creek Mine (Owili -Eger, 1987; Moebs and Barton, 1985; Schultz, 1988). After over 15 years of <br /> monitoring of alluvial and bedrock wells (see Annual Hydrologic Reports), no impacts to the water quality of <br /> the Trout Creek Sandstone, Twentymile Sandstone, or overlying alluvial aquifers has been found. The only <br /> impacts to sub - surface water quality have been an increase in TDS and iron in the water stored in the mine. In <br /> addition, high TDS water from the adjacent surface mine has moved into the underground workings (see in <br /> Effects on Ground Water Quality of Aquifers). <br /> SURFACE WATER SYSTEM <br /> A detailed discussion of surface water hydrology is presented under Rule 2.04.7(2). The proposed life -of -mine <br /> area for the Foidel Creek Mine is located within the Foidel Creek and Fish Creek surface water drainages. <br /> Therefore, any mining impacts on surface water systems will be confined to these drainages and their receiving <br /> streams. <br /> Potential Mining- Related Impacts on Surface Water Quantity and Quality <br /> The planned underground mining and associated activities have the potential of creating changes in the existing <br /> surface water quantity in terms of runoff volumes, flow rates, and direction and location of surface water <br /> drainage. The potential mechanisms of impact are: <br /> 1) Direct disturbance of surface flow channels <br /> 2) Discharge of mine inflow water to surface water drainages via sedimentation ponds or direct discharge <br /> • 3) Detention of surface runoff in sedimentation ponds and related evaporation loss <br /> 4) Diversion of overland flow with ditches <br /> 5) Induced recharge or discharge by underground mine dewatering <br /> PR09 -08 2.05 -149 04/27/09 <br />
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