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Estimating Additional Water Yield from Changes in Management
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Estimating Additional Water Yield from Changes in Management
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Last modified
1/26/2010 4:41:08 PM
Creation date
7/22/2009 12:50:22 PM
Metadata
Fields
Template:
Water Supply Protection
File Number
8461.250
Description
Water Issues
State
CO
Basin
South Platte
Water Division
1
Date
5/12/2000
Author
Charles A. Troendle, James M. Nankervis
Title
Estimating Additional Water Yield from Changes in Management
Water Supply Pro - Doc Type
Report/Study
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watersheds were monitored from 1911 to 1919 and then one of the <br />, watersheds was clear cut. Following harvest, stream flow was increased an <br />average of 1 area inch for the following 7 years. The authors concluded the <br />increased flow was largely a reflection of reduced winter interception loss <br />and that although summer evapotraspiration (ET) by the over story was <br />reduced it was largely offset by increased under story ET. <br />As noted by Leaf (1999), the most classic watershed experiment, in terms of <br />both the length of record and the duration of treatment response, has been <br />the Fool Creek Watershed on the Fraser Experimental Forest, CO (Hoover <br />and Leaf 1967; Troendle and King 1985). Following a 12-year calibration <br />with the control watershed, East St. Louis Creek, approximately 40 percent <br />of the 714 acre Fool Creek drainage was harvested in altemating clear cut <br />and leave strips during 1954-1956. The average hydrograph before and after <br />treatment is depicted in figure l. On average, total seasonal flow increased <br />by 40 percent, average peak flow increased by 20 percent, and most of the <br />detectable change in flow occurred in the month of May (Troendle and King <br />1985; Troendle et al. 1998). The largest peaks were not significantly <br />increased and the largest increases in flow occur in the wettest or largest <br />flow years (figure 2) (Troendle et al. 1998; Troendle and King 1985). In the <br />case of Fool Creek, "bankfull discharge" increased from an average duration <br />of 3.5 days prior to harvest to more than 7.0 days following harvest <br />(Troendle and Olsen 1994). The most frequently occurring, or lowest, flows <br />were not affected by rimber harvest (Troendle and Olsen 1994). The <br />response at Fool Creek, a small experimental watershed was similar to that <br />of Wagon Wheel Gap and depicts the nature of the change that occurs when <br />the forest in the sub alpine environment is disturbed by harvest, fire, or <br />insect mortality. Fool Creek was harvested over 40 years ago and although <br />the initial response to treatment has diminished as the Forest has recovered, <br />full recovery is not expected to occur for yet another 25 to 30 years (figure <br />3). <br />Peak discharges expressed as either maximum instantaneous or maximum <br />mean daily flow; from Fool Creek have always been observed to be <br />snowmelt driveri. This is consistent with Jarrett's (1993) observations that <br />floods occurring from watersheds lying above 7,500 feet in elevation in <br />Colorado axe snowmelt driven. Response to summers rainfall events <br />generally represents only 3 to 4 percent of the event precipitation both <br />before and after either timber harvest (Troendle and Bevenger 1987) or fire <br />(Troendle and Bevenger 1995). <br />4
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