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PERMFILE103728
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Last modified
8/24/2016 9:57:11 PM
Creation date
11/24/2007 10:21:25 AM
Metadata
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Template:
DRMS Permit Index
Permit No
M2001022
IBM Index Class Name
Permit File
Doc Date
8/5/1996
Doc Name
IN -STREAM AGGREGATE EXTRACTION AND RECLAMATION GUIDANCE DOCUMENT
Media Type
D
Archive
No
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<br />Aoocndix D - Porrntia! Hvdrola¢ic Srrucrurrt ra Minimise fmaactt and Minin¢ Merhodt <br />Frequently a biorevetement will include willow plantings. These consist of willow stakes or <br />fascines, that are approximately 5 to 8 foot wands of dormant willows cut in the spring before they <br />have leafed out. Store in water with a root promotion solution until planted. Do not allow them <br />to dry out. Fascines are bundles of willows that have been planted horizontally in shallow <br />trenches at benched heights ranging from several inches to 2 to 3 feet above the low flow water <br />surface elevation. Willow plantings are most successful when planted in sites with adequate <br />moisture in well-drained conditions such as silty sand. They should not be planted below the <br />perennial waterline (base flow elevation of stream), or success will be tempered. <br />Gabion Baskets <br />Gabion baskets are sized rock enclosed in a wire mesh basket. It is recommended that a type of <br />galvanized wire be used to promote a longer life of the installation. Size of the basket and rock <br />can vary with the type of installation and the objectives of the control measure. Gabion baskets <br />provide a durable and lon; lasting erosion control measure and rock materials aze usually available <br />a[ the mining site. Figure D-10 shows photographs of two types of gabion baskets. <br />Jetties <br />Jetties consist of dike-type strucmres that may be used for bank protection (Figure D-11). Jetties <br />project from the toe of a graded 4:1(H:V) channel bank to no more than one-third the stream's <br />width, and optimally 15 to 25 feet. Jenies aze installed in a series along a straight reach or outside <br />bank. Their orientation should be either perpendicular to a stream's centerline or at a 4~ degree <br />angle downstream. Jetty spacing should be placed at a ratio of centerline spacing to jetty projection <br />less than or equal to three. Thus, if the jetty extends 25 feet from the toe of the bank, jetty <br />installation should occur every 75 feet or less. Jetties should be toed in at least 5 feet deep, and <br />wing wails should extend at least 25 feet. Jetties should be constructed of Type Hrip-rap. The <br />core of the jetties may be constructed with a mixture of concrete rubble. Banks between jetties <br />should be stabilized with vegetation. Fiawre D-12 contains photographs of jetties installed in river <br />channels. <br />Vegetation Stabilization <br />Vegetation is often used in a variety of methods to stabilize and protect stream banks from erosion. <br />A combination of species are used, including willows and grasses. Vegetation is often used in <br />conjunction with other stabilization methods such as rock armoring, bioreve[emenrs, and vegetated <br />zones between jetties. Fierrre D-13 shows revegetated stream banks following mining operations. <br />GRADE CONTROL STRUCTURES <br />In-stream grade control structures, if used, should be installed on the upstream end of [he in- <br />stream pi[. Examples of these structures are described below. <br />.i me~n~e~n ~. iwa D-5 <br />
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