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APPCOR11775
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Last modified
8/24/2016 6:32:06 PM
Creation date
11/19/2007 2:24:08 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1981026
IBM Index Class Name
Application Correspondence
Doc Date
10/29/1981
Doc Name
Proposed Decision Letter Stipulations & Findings
From
MLRD
To
Wyoming Fuel Company
Media Type
D
Archive
No
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-I 5- <br />At the maximum extent of mining operations of botA Wyoming fuel. Company and Kcir <br />Coal Company during this permit term, approximately 200 oC the drainage area of <br />Bolton Draw will be detained in sediment ponds. This figure is not indicative of <br />the probable diminution of flows of Bolton Draw. Several factors play a role in <br />mitigating the impact of mining operations on the quantity of water in Bolton <br />Draw. They are: <br />1. The areas of both mine sites are generally canopied by short grasses and sage- <br />brush. Snow accumulation in these areas is slight due to blowing conditions in North <br />Park. The forested slopes of Johnny Moore ~~fountain provide much better conditions <br />for Snow accumulation and probably provide a greater water. yield per acre than the <br />mine sites. <br />2. Bolton Draw receives some if its water from transbasin diversion of hfichigan <br />River waters through Spear Ditch. <br />3. The scenario given above assumes that a1Z of the mining occurs at once w7ren, <br />in reality, mining will be done in phases, with portions of mined lands being re- <br />claimed and released from the requirements of sediment control, and other areas, <br />ahead of mining, being undisturbed. <br />Water which does Leave the mine sites will carry a greater salt load than native <br />surface waters due to the pumping of poor quality p.it water into sediment ponds and <br />the evaporation of water from ponds increasing the concentration of dissolved solids. <br />An estimate, which assumes the worst-case of 200 of the water in Bolton Draw coming <br />from disturbed areas, is that 90.5 ky/yea z• of salt will he introduced into Bolton <br />Draw. As Wyoming Fuel Company has never discharged water from their mine site, this <br />estimate is highly speculative. Salt concentrations of the Canadian Strip mine over- <br />burden are higher than overburden at the llarr Strip mine. Due to concern that pit <br />water may eventually reach surface waters by dewateriny of sediment ponds, a stipu- <br />lation has been included in this document Eo monitor the pz~oduction of salt from the <br />ponds (see Bydroloyic Balance: .Surface Waters). <br />After mining and reclamation of the affected areas, a slight increase in water yield <br />may be expected. Infiltration tests done by f/yoming Fuel Company have shown the <br />infiltration rate of replaced topsoil and regraded spoil to be less than the pre- <br />existing soils. This effect should gradually decrease over time as the vegetation <br />becomes established, increasing the depth of the rhizosphere and increasing the <br />organic content of the soil. Both of these processes increase the infiltration <br />rate of soils. <br />Effects: Ground F7ater <br />Both the Wyoming Fuel and Kerr mines are located on the flanks of the McCallum Anti- <br />cline and the Johnny Pfoore Syncline, and thus, are hydrogeologically adjacent. The <br />Bourg mine is outside of the ground water basins of these mines. The Wyoming Fuel <br />mine is mining south and west around the nose of the hcCallum Anticline, whereas <br />the Kerr mine is mining north and east around the nose of the Johnny Moore Syncline. <br />Ground water flow from both the Kerr and Wyoming Fuel mines is down the dip of <br />the McCallum Anticline to the axis of the Johnny hfoore Syncline. <br />
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