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Last modified
1/29/2010 10:11:58 AM
Creation date
10/5/2006 2:08:36 AM
Metadata
Fields
Template:
Floodplain Documents
County
Otero
Pueblo
Community
Otero, Pueblo Counties
Stream Name
Arkansas River
Basin
Arkansas
Title
Arkansas River Channel Capacity and Riparian Habitat Planning Study
Date
7/1/1999
Prepared For
CWCB
Prepared By
US Army Corps of Engineers
Floodplain - Doc Type
Project
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<br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I' <br />I <br />I <br />I <br />I <br />I <br /> <br />leaf area. Dense mature trees have large cross-sectional areas and can withstand relatively high <br />flows without breaking, therefore, provide the greatest resistance to flow (\1 ogel 1984). <br />Sparsely distributed trees can actually generate bank scour by accelerating flow around their <br />trunks. <br /> <br />Ftood attenuation. Flood discharge is strongly influenced by floodplain area. A larger <br />floodplain will have a lower peak stage than a smaller one for a given discharge. Additionally, <br />larger channel capacity allows a given flood event to pass more quickly. <br /> <br />Sediment toad. Riparian vegetation affects stream morphology by regulating sediment <br />supply and points of deposition. As stated previously, overbank vegetation influences sediment <br />transport by reducing flow velocities and causing deposition. Since the primary source of <br />sediment in many streams is bank erosion (Dunne and Leopold 1978), sediment load can be <br />significantly limited by bank vegetation. In agricultural watersheds with significant sediment <br />laden runoff, riparian vegetation traps sediments before they reach the stream (Lowrance et at. <br />1984). <br /> <br />Nutrient trapping and removat. Riparian vegetation traps both suspended and dissolved <br />materials and contributes significantly to the high fertility of floodplain soils. Suspended <br />particles in overbank flow and upland runoff are deposited when flow velocities are decreased <br />by vegetation. Most notably, carbon, nitrogen, and phosphorous concentrations in surface <br />water are effectively reduced by floodway vegetation (PeteIjohn and Correll 1984 ). <br />Additionally, riparian root systems uptake dissolved nutrients in subsurface water. <br /> <br />Wildtife habitat. Riparian habitats provide breeding sites, wintering areas, and <br />migratory stop-over areas for nurnerous wildlife species. The provision of food, cover, and <br />shelter has long been an important, widely recognized function of riparian vegetation (Brinson <br />et at. 1981, Minshall et at. 1989). This is especially true in the central and western United <br />States where riparian woodlands provide uncommon and structurally complex habitats relative <br />to the surrounding grassland or shrubland. Lowland riparian forests occupy only 3% of <br />Colorado's land area but contain the highest bird species richness and abundance than any other <br />ecosystem in the state except for marshes (Kingery 1998). The Arkansas River below John <br />Martin Dam harbors a nationally prominent white-tailed deer population (Ed Gorman, Habitat <br />Biologist, Colorado Division of Wildlife, October 1998,pers. comm.). Individual deer are <br />known to range throughout 350 to 400 acres of riparian woodland during the course of the year <br />(Kufeld and Bowden 1995). Riparian plant communities serve as travel corridors for local <br />populations of deer and other mammals, and as major migration routes for migratory birds. <br /> <br />Importance to aquatic systems. Bank vegetation also is an important component of <br />aquatic faunal habitat (Platts 1983). Streamside vegetation provides shade and cover for fishes <br />where it overhangs the water surface. The contribution of carbon to downstream aquatic <br />habitats is one of the most widely recognized functions of riparian vegetation (Brinson et at. <br />1981 ). <br /> <br />29 <br />
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