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PERMFILE112893
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PERMFILE112893
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Last modified
8/24/2016 10:09:09 PM
Creation date
11/24/2007 10:01:32 PM
Metadata
Fields
Template:
DRMS Permit Index
Permit No
C1981010
IBM Index Class Name
Permit File
Doc Date
3/18/1991
Doc Name
DRAINAGEWAY RECONSTRUCTION, Improvement and Repairs 1990
Section_Exhibit Name
Appendix W 1990 Report Section 3.0
Media Type
D
Archive
No
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. headwater locations or on relatively gentle grades often within water harvesting diver- <br />sions on reclaim sideslopes. <br />Water harvesting diversions are channels constructed across slopes with a supporting <br />ridge on the lower side that is used to transport excess water from areas that need pro- <br />tection to sites where water can be used or disposed of safely. A diversion's effectiveness <br />as a sediment reducing measure is in diverting the runoff which would otherwise flow <br />across erosion susceptible areas, thus detaching and transporting soil particles. <br />Contour farming and live haul topsoil transport are used on all reclaimed sideslopes and <br />drainage areas when possible. Topsoil replacement, seedbed preparation, and planting <br />are done on the contour. Contouring can reduce erosion by 40 to 50 percent. When <br />contour farming is combined with live material topsoil transport the erosion loss poten- <br />tial can be further reduced. Contouring provides excellent erosion control by reducing <br />transport from moderate rainfall events. Contouring in combination with diversion <br />establishment can be very effective in reducing erosion potential. <br />Rock check structures are used to dissipate the energy of flowing water within the <br />drainageway channel. Debris and sediment tend to be deposited and trapped upstream <br />of structures. This in turn permits establishment of vegetation behind structures which <br />further stabilize the channel. In addition, filter fabric is installed and used to fine rack <br />check structure core trenches, thus providing additional structural support and reduces <br />the potential for advancement of downstream headcutting to move upstream. <br />Cover crops and mulch are used very effectively in drainageways to reduce the detach- <br />ment of soil by rainfall and runoff while providing seasonal protection and soil improve- <br />ment. Cover crops provide protection from wind and water erosion during vegetation <br />establishment periods when permanent vegetation is inadequate to provide adequate <br />cover. <br />Permanent vegetative (grasses, (orbs and shrubs) cover provides the most significant and <br />permanent long term solution to erosion control problems. The selection of species <br />adapted to the climate and soils is one of the most important steps in achieving success. <br />Woody plants are desirable for the long term stability of a particular site. However, <br />woody plants require time to develop sufficient size to control erosion adequately and <br />the quick cover that can be obtained with grasses and (orbs is needed in the interim. The <br />principles for selection of herbaceous vegetation is based on a particular species adapta- <br />tion to the mine site and its erosion control potential. The idea] species have strong root <br />development. A diverse mixture of plant species increases the assurance of a stand as it <br />is difficult to anticipate all of the variables that will affect germination and stand estab- <br />lishment on any given site. <br />Willow wattles and woody seedling transplants are installed in drainageways and serve as <br />energy dissipaters for water and soil moving down the drainageway and provide long <br />term stability. Woody plants filter and trap entrained debris (soil, small rocks, veg litter) <br />• and provide a series of areas with reduced slope angles on which vegetation can be <br />established. Deep rooted woody vegetation prevents gully formation and will become <br />part of the permanent stabilizing cover. <br />
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