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2010-12-17_REVISION - C1981019 (122)
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2010-12-17_REVISION - C1981019 (122)
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Last modified
8/24/2016 4:28:02 PM
Creation date
12/30/2010 2:20:14 PM
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Template:
DRMS Permit Index
Permit No
C1981019
IBM Index Class Name
REVISION
Doc Date
12/17/2010
Doc Name
Exhibit 7 Item 23 Erosion and Sedimentation Control Plan
Type & Sequence
PR3
Email Name
JRS
Media Type
D
Archive
No
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• 1.9 BASE FLOW <br />Base flows were not used in any pond design calculations. Treated discharge of collected water from the <br />Little Collom X in -pit sump will be pumped to the Little Collom X downstream pond after settling has <br />occurred. <br />2.0 SEDIMENTATION CALCULATIONS <br />The sedimentation calculations for each pond on the Colowyo Mine were performed using the SEDCAD4 <br />Computer Modeling Program developed by Civil Software Design. The SEDCAD4 sediment detachment <br />routine is based on the Revised Universal Soil Loss Equation (RUSLE). The input parameters used in the <br />sedimentation analyses are presented in the following sections. <br />2.1 RAINFALL FACTOR. R <br />An annual rainfall erosivity factor of 19 was used for the Little Collom Sump (LCX -IN in -pit sump) <br />sedimentation pond. This factor is consistent with other recent erosion analyses performed for the <br />Colowyo Coal Company. However this R factor was not used in the design of Little Collom (LCX -D /S) <br />Pond due to the short duration of the worst case conditions for this pond. Calculations were made with <br />the initial sediment storage set to equal 1.57 acre -feet, which results in a sediment storage elevation of <br />6629.88 feet, approximately 3 months of storage at the average annual rate. Throughout the initial 6- <br />month condition, Little Collom (LCX -D /S) Pond will be monitored and cleaned out to ensure the <br />sediment storage is maintained at or below this elevation. <br />2.2 SOIL ERODIBILITY FACTOR, K <br />A conservative soil erodibility factor of 0.31 was used for all watersheds. Future analyses will refine this <br />value to be less conservative and more accurate. A comparison to dominant soil types and associated K <br />values is provided in Table 2. <br />TABLE 2 <br />SOIL ERODIBILITY FACTOR <br />DOMINANT SOIL TYPE <br />SOIL TEXTURE <br />SOIL ERODIBILITY <br />FACTOR(K <br />Campspass Series <br />Loam <br />0.24 <br />Burnette Series <br />Loam <br />0.28 <br />Work Series <br />Loam <br />0.31 <br />Average <br />0.28 :J <br />2.3 LENGTH -SLOPE FACTOR. LS <br />Input parameters to determine the LS factor were obtained from scaled maps of the watershed areas. <br />Values measured from the scaled maps are shown in the SEDCAD4 printouts. Within disturbed <br />subwatersheds, the representative length was capped at 250 feet to account for control practices to be <br />utilized, including terrace ditches, slope drains, and benching. No adjustment to slope was made, though <br />benching will reduce some slopes significantly as mining progresses. <br />2.4 CONTROL FACTOR, C <br />The Control factor is used to account for vegetative or mulch cover. The following values presented in <br />Table 3 were utilized in previous pond design evaluations (Schwab and Warner, 1987): <br />Exh. 7 -23 -4 Revision Date: 12/15/10 <br />Revision No.: PR -03 <br />
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