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Last modified
1/26/2010 12:36:19 PM
Creation date
10/11/2006 11:03:40 PM
Metadata
Fields
Template:
Water Supply Protection
File Number
8102
Description
Arkansas River Basin Basic Hydrology
State
CO
Basin
Arkansas
Water Division
2
Date
5/7/1999
Author
Inter-Fluve Inc
Title
Fluvial Geomorphic Assessment of Upper Arkansas River - Final Report
Water Supply Pro - Doc Type
Report/Study
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<br />May 7, 1999 <br /> <br />Fluvial Geomorphological Assessment <br />Upper Arkansas River <br /> <br />Page 12 <br /> <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br />, <br />I <br />t <br />I <br />I <br />I <br />I <br />I <br />I <br />I <br /> <br />quantified from the comparison. Rather, the comparison is intended to compare flow <br />conditions in the Arkansas River before and after the Mt. Elbert conduit was completed. <br /> <br />Flow duration data represent the percent of time that a given flow is equaled or exceeded <br />at a given data collection point. Between Leadville and Malta, the magnitudes of all but <br />the most frequently occurring flows (>95% duration) increase significantly between <br />Leadville and Malta during the 1976-1983 time frame (Figure 3,8), These curves <br />represent a time period during which both native and augmented flows were conveyed <br />down Lake Fork Creek, In contrast, the 1990-1993 time frame was characterized by <br />diversion of both augmented and native flows past the project reach via the Mt. Elbert <br />conduit (Figure 3.9). The increase in discharge between Leadville and Malta is markedly <br />less during the 1990-1993 time period for all but the lowest flow conditions. <br /> <br />Figure 3.10 shows the ratios of unit discharges (discharge per square mile of drainage <br />area) for incremental flow duration values at each gage, The 1976-1983 time frame was <br />characterized by unit discharges at Malta that were around double that of Leadville for <br />flows that occurred between 40% and 80% of the time, Larger magnitude events (less <br />than 10% duration) were of comparable unit discharges, and low flow unit discharges <br />(greater than 90% duration) at Malta were roughly one half of those at Leadville. In <br />contrast, the 1990-1993 time frame was characterized by unit discharges at Malta that <br />were approximately 1.5 times those of Leadville for relatively common flows (60% to <br />80% duration), and less than those of Leadville for flow durations of less than 25%. <br /> <br />In summary, annual hydro graphs and flow duration curves for the overlapping periods of <br />record (1976-1983 and 1990-1993) upstream and downstream of Lake Fork Creek depict <br />a significant influence of flow augmentations during the 1976-1983 time frame when <br />both native and augmented flows were conveyed down Lake Fork Creek. Annual <br />hydro graphs (Figures 3,2-3.4) depict block release patterns that are characteristic of <br />Turquoise Lake operations (Figures 3.5-3.7). Unit discharges that are equaled or <br />exceeded between 40% and 80% of the time downstream of Lake Fork were <br />approximately double those measured upstream of Lake Fork during the 1976-1983 time <br />frame (Figure 3.10), In contrast, the during the 1990-1993 time period, the effects of <br />Turquoise Lake operations are reduced peak unit discharges (low duration flows), which <br />are also depicted in the spring runoffhydrographs of Figure 3.5-3,7, and a moderate <br />increase in low flow unit discharges (high duration values), <br /> <br />It should be noted that the impact of reservoir releases on project reach hydrology is not <br />only due to the change in flow magnitude, but also stems from the patterns of release, or <br />the shape of the hydro graph generated. Rapid fluctuations in flow rate have the potential <br />to greatly impact river geomorphology, due to the effects of such fluctuations on bank <br />stability and sediment transport conditions. In general, the BOR attempts to keep the <br />fluctuations in diurnal releases to less than 10 to 15% (Studzinski, 1996), however, flow <br />records indicate that that objective has not always been met. Studzinski (1996) reports <br />that between 1970 and 1994, a reduction in daily streamflow in excess of 25% occurred <br />270 times. <br />
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