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The Arkansas River within the study reach historically was an ephemeral, braided river <br />with a varied channel today of about 3,000 cfs. Several small, shifting channels occupied a <br />broad, sandy river bottom and were interspersed with numerous bars and islands. In the late <br />1800s, the bankfull width of the channel was approximately 1,000 feet, and bankfull depth was <br />within the range of 1 to 2 feet. Currently, this reach-has become a perennial, narrow, meandering <br />channel. Bankfull width has decreased to approximately 100 feet. <br />Historic flow data for the Arkansas River above John Martin Dam were evaluated. A <br />Rating Curve for the stream gage at La Junta was developed to determine the-2-year flow. The <br />2 -year flow at La Junta is approximately 7,000 cfs and this flow transports the greatest amount of <br />sediment over the historical record of the Arkansas River. <br />Suspended sediment data were analyzed and upstream reaches of the Purgatoire and <br />Arkansas Rivers show high rates of suspended sediment. Many changes have occurred as a <br />result to this condition such as decreased channel capacities due to sediment deposition, scouring <br />of embankments, high water table and extensive overgrowth of vegetation and encroachment on <br />the floodway. <br />Numerical hydraulic models were developed for each of the problem areas to analyze <br />current conditions with flows of 100, 200, 300, 500, and 1,000 cfs. The combined hydraulic and <br />sediment analyses indicate several problems. First, the channel capacity in some areas is less <br />than 1,000 cfs. Second, the 2 -year flow of 7,000 cfs; would completely flood the overbank areas <br />resulting in local scour or deposition and inhibiting Effective conveyance of water and sediment. <br />Additionally, erratic hydraulic conditions contribute to seepage problems during high river <br />flows. Thirdly, sediment transport potentials are erratic. <br />Overall, the channel appears to be impacted primarily by three phenomena; a reduction <br />in peak flows due to the Pueblo Dam and Reservoir, changes in floodplain vegetation, and <br />encroachment on the channel and floodway. Reduced peak flows have caused the channel to <br />become smaller and this shrinkage is often exhibited as narrowing. Dense vegetation (primarily <br />salt cedar) has become established on the newly formed bank and inhibits the river's widening <br />again during high flows. Likewise, agricultural fields have encroached on the floodway with a <br />similar result. The reduced peak flows have induced: an expectation that the river needs less <br />room. Lands nearer the river have been put into production and this encroachment inhibits <br />rewidening of the channel. Leveeing further restricts the flow path and causes incision and bank <br />instability. As this cycle continues, the effective conveyance capacity becomes less and less. <br />The current floodway is tightly bounded by farmland and attendant berms. Several agricultural <br />fields were identified as currently at risk from surface water inundation at river discharges near <br />1,500 cfs. <br />Historically, riparian vegetation along the Arkansas River in eastern Colorado consisted <br />of a wide band of sparsely distributed plains cottonwood, with scattered stands of sandbar willow <br />along the channel banks and bars. Although relatively dense cottonwood stands occurred <br />between La Junta and Las Animas (the "Big Timbers" area), the majority resembled an open - <br />canopied parkland ranging up to 2 miles wide, Grasslands dominated by salt grass and alkali <br />sacaton occupied areas too saline to support cottonwood and willow. <br />iv <br />