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PERMFILE50304
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Last modified
8/24/2016 10:54:54 PM
Creation date
11/20/2007 2:25:49 PM
Metadata
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Template:
DRMS Permit Index
Permit No
M1999002
IBM Index Class Name
Permit File
Doc Date
4/26/1999
Doc Name
PRELIMINARY RESPONSE PLAN
Section_Exhibit Name
APPENDIX A PRELIMINARY STORMWATER MANAGEMENT PLAN
Media Type
D
Archive
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• <br />reducing peak flows and trapping sediments. Care should be taken at the inlet to <br />ensure a gradual or moderate slope into the pool. Creating a steep angled drop into the <br />pool may cause headcutting upstream and sloughing or accelerated erosion, which can <br />significantly decrease the holding capacity of the structure. In locations where or <br />during periods of time when erosion rates and sedimentation are high, sediment traps <br />must be maintained frequently. Use, placement, functional life expectancy, and ability <br />to perform maintenance should be considered when using sediment traps. <br />For small impoundments where human safety and health risks are not of concern, <br />generic designs that are modified to take into account local site conditions may be <br />utilized for non-critical structures. <br />2.1.3.4 Sedimentation Basins <br />A professional engineer familiar with sedimentation ponds will be utilized in site <br />specific designs for sedimentation basins or other large impoundments that present <br />risks to the environment or to public health and safety or that are used for final water <br />treatment purposes. A professional engineer certification is normally required by <br />regulation for sedimentation basin and other large impoundment designs. <br />Sedimentation basins primarily serve to trap sediments. Secondarily they reduce or <br />abate water pollution by providing a collection structure for the storage of chemical <br />contaminants, debris, and other processing wastes. The designs of dams, spillways, and <br />drainage facilities should be in accordance with standard engineering principles <br />appropriate for the class and kind of structure being considered. Dewatering devices <br />should be incorporated where permanent pools are unacceptable, or where adequate <br />containment volumes for runoff must be provided. <br />The ability of an impoundment to accomplish runoff treatment goals is directly related <br />to basin specifications and construction procedures. The efficiency and life of an <br />impoundment are directly related to the scale of up-gradient disturbance activities and <br />to the types of erosion and runoff control measures being employed. Therefore, basin <br />design should be performed on a site-specific basis taking into account local <br />environmental factors. <br />A designed catchment basin or impoundment may be incised, formed by an above- <br />ground embankment, or formed by some combination thereof (Figure D-4). Typical <br />sedimentation basins are 5 to 20 acre-feet in capacity. Sedimentation basins are the <br />preferred treatment method for areas that remain disturbed for extended periods of <br />time. Typically they are used to treat runoff from facilities areas, but they may be used <br />to treat runoff from any type of disturbance area. However, because of their size, <br />construction costs, and the additional disturbance area associated with their <br />construction, sedimentation basins are normally impractical for use in treatment of <br />small areas. <br />Preliminary Response Plan A-l3 <br />Yankee Gulch Sodmm Minerals Project <br />American Soda, L.L.P. <br />
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