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GENERAL31182
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Last modified
8/24/2016 7:48:32 PM
Creation date
11/23/2007 6:56:52 AM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
M1999002
IBM Index Class Name
General Documents
Doc Date
1/19/1999
Doc Name
DRAFT ENVIRONMENTAL IMPACT STATEMENT CHAPTER 4
From
STEIGERS CORP
To
DMG
Media Type
D
Archive
No
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<br />CNAPTERFOUR Environmental Consequences <br />acres of fragile soils (5 percent of the study azea). Incremental disturbance of the mine panels <br />would affect 470 acres of fzagile soils (12 percent of the study area) over 30 yeazs. Project <br />facilities would disturb 35.2 acres of fragile soils (less than 1 percent of the study area) for the <br />' life of the project. <br />Some soil loss to wind and water erosion is inevitable. However, minimizing the disturbance <br />azea, retaining a vegetative cover over much of the Piceance Site, and effectively using erosion <br />' and sediment control structures (i.e., silt fencing, straw or hay check dams and filters, erosion <br />blankets or mats, water bars etc.) at all disturbed sites would reduce the potential for accelerated <br />' erosion and sedimentation. Studies have shown that most accelerated erosion occurs in the first <br />year following soil disturbance and that measures such a mulching can reduce erosion by as <br />much as 60 to 80 percent in that critical fast year (Ketcheson and Megahan 1996; USFS 1979; <br />' Synthetic Industries 1996). <br />Interim or final revegetation with a protective herbaceous cover could be expected within one to <br />two years for most areas. Upon successful revegetation, erosion rates could be expected to return <br />' to rates similar to existing conditions for the long term. Revegetation may be more difficult in <br />areas with high rock content and for shallow soils on steep slopes, but use of erosion control <br />' measures, and monitoring and retreatment as needed, would likely return such sites to conditions <br />similaz to predisturbance levels of erosion within 5 years. Severe, localized erosion impacts <br />would be expected to occur in any azea of fragile soils where erosion control measures or <br />revegetation efforts were not adequate. <br />Loss of soil fertility and soil structure would occur during soil salvage and stockpiling. Although <br />almost none of the soils within the proposed mine azea are well-suited for use during <br />reclamation, salvage of what little coversoil is available would provide an important source of <br />plant growth material to assist with reclamation. Stockpiled material would be protected from <br />erosion, and a temporary vegetative cover would be established on stockpiles that would be <br />inactive for more than 12 months. Following redistribution of coversoil material, and based on <br />fertility testing, fertilizers or other soil amendments would be applied as needed, which would <br />increase the potential for successful reclamation. Other measures such as erosion control and <br />,application of organic mulches would also aid in re-initiation of the soil development process. <br />Biological activity in soils would gradually increase after reclamation, and plant communities <br />and soil structure would evolve on reclaimed azeas. <br />Natural Gas Piveline Alternative A <br />Construction of this alternative would result in temporary disturbance of 1.2 acres of fragile soils. <br />Impacts, mitigation and reclamation would be as described above. <br />Natural Gas Piveline Alternative B <br />Construction of this alternative would not result in any impacts to soils in addition to those <br />described above. <br />' Soils 4-7 <br />
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