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<br />. <br /> <br />. <br /> <br />. <br /> <br />Extensive efforts to mechanically break up hydrophobic soils and slow water and sediment runoff <br />began very soon after the fire, Most efforts were in basins posing greatest risk to the public: <br />Sand Draw, Spring Gulch, and Shinglemill Creek, A moderate flood on June 12, 1996 (Casey <br />Clapsaddle, USFS, written commun" 1996) and the severe flash flood on July 12,1996 washed <br />out most of the initial rehabilitation efforts, Small amounts of water were applied to burned areas <br />(simple infiltration tests) in 1996 and 1997, Generally, no water infiltrated and small droplets of <br />water formed, indicating hydrophobic soils in 1996, During the wet spring of 1997, applied water <br />infiltrated rapidly, even on very steep hillslopes (>30 'Yo), However, after the soils dried, <br />infiltration was low due to reformed hydrophobic conditions or other factors, Data monitoring in this <br />study complements an instrumented, paired-basin analysis being conducted by Casey <br />Clapsaddle to assess the rehabilitation efforts used in Shinglemill Creek and Morrison Creek <br />basins (burned area was left untreated), <br /> <br />Despite extensive rehabilitation efforts in burned area, smaller rainstorms after July 12 in 1996 <br />and in 1997 produced similar rates of runoff (fig. 10), On August 31, 1997, a 63 mm rainfall in <br />about 30 minutes over the headwaters of Sand Draw, produced a flash flood of about 34 m3/s <br />from about 1,5 km2, which reflect persistent conditions that exacerbate flash-flood potential and <br />minimal watershed recovery, Natural debris (trees and sediment) present in many channels <br />appeared to help slow water and sediment runoff for many events, In addition, small runoff <br />events (as much as -3 m3/s) from burned hillslopes that reached channels having thick (>3 m) <br />pea-gravel sediments such as in Sand Draw often infiltrated in a short distance, Long-time <br />residents indicated that since the fire, streams in the burned area have more flow that usual. <br /> <br />Base flows as small as 0,2 m3/s after the July 12, 1996, flood were competent to incise and <br />erode much of the new alluvial fans, Many fans had several agradation-degradation cycles for <br />small events (peak flows of -1-2 m3/s) since the fire, which reflects channel instability, Lower <br />tributaries reaches that agraded on July 12, 1996, generally had degraded by about a meter by <br />the end of 1997, but hills lope erosion continues to contribute sediment to channels, Sediment <br />from the burned area continued to be transported through the NF and South Platte Rivers to <br />Strontia Springs Reservoir, About 75 percent of Denver's water comes through the reservoir, <br />which has a capacity of about 9,74 hm3. From May 1996 to October 1997, about 0,31 hm3 of <br />sediment washed into the reservoir compared to about 0,14 hm3 in the 13 years since the <br />reservoir was built (Denver Water Department, written commun" 1997), Snowmelt runoff in the <br />NF and South Platte Rivers likely will continue to move large amounts of wildfire-produced <br />sediments towards the reservoir. <br /> <br />Geomorphic investigations of alluvial sediments in the burned and unburned (in 1996) areas <br />indicate at least 10 fires/flood sequences have occurred in the study area prior to 1996 (fig, 12), <br />At least one paleoflood was larger than the July 12, 1996 flood, and runoff after several of the <br />prehistoric fires produced much thicker alluvial deposits than following the 1996 wildfire, <br />Radiocarbon dating of organic material in alluvial sediments in a Buffalo Creek tributary indicated <br />that these sequences span about the last 2,500 years (John Elliott, USGS, written commun" <br />1997), Additional investigations will help determine the long-term fire and flood history in the <br />region, which could help forest managers develop policy for prescribed bums and other <br />management practices, <br /> <br />Study results can be used to develop and verify hydrologic- and sediment-budget models for <br />burned watersheds, In conjunction with the NWS, study results and rainfall-runoff modeling was <br />conducted to help determine threshold-rainfall amounts for flash-flood conditions, These results <br />were used to refine flash-flood warnings, particularly to minimize the number of false alarms that <br />can cause complacency of those at risk, The Colorado Water Conservation Board (1997) <br />prepared an emergency response, hazard-mitigation, and awareness plan for government <br />officials, residents, and visitors in the Buffalo Creek area, <br /> <br />Studying only the Buffalo Creek area can not provide answers to all questions about wildfire <br />hazards in other forest ecosystems, Thus, additional paleoflood studies are needed for burned <br />(wildfire and prescribed bum) watersheds this century in the Rocky Mountain region, These <br />could include, but are not limited to, Storm King Mountain, Colorado (1994), Black Tiger in Boulder, <br /> <br />7 <br />