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Estimating Additional Water Yield From Changes in Management of National Forests in the North Platte Basin
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Estimating Additional Water Yield From Changes in Management of National Forests in the North Platte Basin
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3/29/2013 2:57:42 PM
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3/6/2013 10:50:04 AM
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An Independent Report Prepared for the Platte River EIS Office U.S. Department of the Interior Related to Platte River Endangered Species Partnership (aka Platte River Recovery Implementation Program or PRRIP),
State
CO
NE
WY
Basin
North Platte
Water Division
6
Date
5/12/2000
Author
Charles A. Troendle, Matcom Corporation & James M. Nankervis, Blue Mountain Consultants
Title
Estimating Additional Water Yield from Changes in Management of Ntional Forests in the North Platte Bains, Final Report
Water Supply Pro - Doc Type
Report/Study
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t <br />watersheds were monitored from 1911 to 1919 and then one of they <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 alternating clear cut <br />and leave strips during 1954 -1956. The average hydrograph before and after <br />treatment is depicted in figure 1. 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 />�r <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 timber 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 driven. This is consistent with Jarrett's (1993) observations that <br />floods occurring from watersheds lying above 7,500 feet in elevation in <br />Colorado are 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). 1 <br />4 <br />
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