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Last modified
1/25/2010 7:09:12 PM
Creation date
10/5/2006 2:20:47 AM
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Template:
Floodplain Documents
County
Statewide
Basin
Statewide
Title
Colorado Erosion Control Manual
Date
11/1/1992
Prepared For
CWCB
Prepared By
USGS
Floodplain - Doc Type
Floodplain Report/Masterplan
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<br />Erosion Reduction Methods. <br /> <br />e <br /> <br />dramatic effect upon the morphology of the river. Clearing and snagging reduces stages, <br />changes the velocity distribution at a section, and can increase sediment transport <br />through the reach. Selective clearing of bars and islands can cause realignment of the <br />main channel of the river. Chute closures or channel blocks increase the flow in the main <br />channel and reduce or deplete flows in the chute. The stage of the river will increase <br />upstream of the structure, particularly during high flows. Both velocity and sediment <br />movement may increase slightly in the channel. If flow is eliminated in the chute, <br />sediment deposition will eventually fill it. Vegetation encroachment will occur in the <br />chute, further reducing the flood capacity of the section. <br /> <br />Vanes - Vanes are structures placed within the channel at a slight angle to the normal <br />flow that reduce the secondary currents and thus reduce the erosive capacity of the river. <br />The three most common types of vanes are 1) Iowa Vanes, 2) baftle vanes, and 3) stone <br />vanes. Iowa vanes are small flow-training structures (foils), designed to modify the <br />near-bed flow pattern and redistribute flow and sediment transport within the channel <br />cross-section (Odgaard and Wang). The structures are typically installed at an angle of <br />15-20 degrees to the flow, with a height of 0.2 - 0.4 times loca1 water depth at designed <br />stage. The vanes function by generating secondary circulation in the flow. The <br />circulation alters magnitude and direction of the bed shear stresses and cause a change <br />in the distributions of velocity, depth, and sediment transport in the area affected by the <br />vanes. As a result, the river bed topography may be altered by selective layout of the <br />structures. Baffle.type vanes are structures consisting of boards attached to piles that are <br />placed in series in the stream to disrupt the secondary currents that cause erosion on the <br />outside of meander bends. The number, locations, spacing, orientation, size, and height <br />of the vanes are critical to success and must be determined from careful analysis. Stone <br />vanes are low slone structures angled approximately 15 degrees to normal flow. They <br />are overtopped by all but the lowest flows. <br /> <br />Because vanes stop erosion by modifying secondary circulation, no bank sloping or <br />treatment is necessary. Aquatic benefits are not destroyed, and once vegetation becomes <br />re~tablished on the eroding bank, riparian haJ)itat and aesthetic benefits are improved. <br />During low water the vanes are not very appealing visually, and there may be some <br />hazard to navigation and to recreationists using the stream. <br /> <br />Vanes have not been used extensively. Prototype vane systems have been installed in a <br />couple of midweslem streams, including the East Nishnabotna River in Iowa. However, <br />it is too soon to evaluate the success of the prototype demonstration at this site. These <br />structures are proprietary, therefore, the user must contact the University of Iowa, <br />Institute of Hydraulic Research for specific design guidance and permission. <br /> <br />. <br /> <br />Clearing and Snagging - For flood control on small streams, conventional clearing and <br />snagging has been used to remove all obstructions from the channel and to clear all <br />significant vegetation within a specific width on both sides of the channel. Key aspects <br />of selective clearing and snagging involve: 1) selective removal of vegetation based on <br />size, condition, species, or location; 2) removal of only those snags that are major flow <br />obstructions; 3) use of hand labor and small equipment when feasible, and rigid access <br />controls when heavy equipment must be used; 4) protection of existing vegetation of <br />disturbed areas; and 5) greater reliance on multidisciplinary teams in all phases of <br />project planning and management. Disturbed areas should be restored to natural <br />contours, and preserved trees should be spaced at irregular intervals. Natural sloughs, <br /> <br />Colol'IIdo Erosion Control Manual <br /> <br />45 <br />
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