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Forests and Water: A State of the Art Review for Colorado
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Forests and Water: A State of the Art Review for Colorado
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Publications
Year
2003
Title
Forests and Water: A State-of-the-Art Review for Colorado
Author
Colorado State University
Description
Colorado State University 2003
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i <br />6.0 <br />a� <br />5.0 <br />CO <br />t <br />V <br />4.0 <br />c� 3.0 <br />c <br />cc 2.0 <br />2 <br />1.0 <br />8jl <br />1 Apr. 2 May <br />2 June 3 July 3 Aug. 3 Sept. <br />Figure 2.3. Mean annual pre- and post treatment hydrographs for Fool Creek, Fraser Experimental Forest. <br />ET, and this change in ET drives the change in runoff in <br />accordance with equation 1. However, the snow -domi- <br />nated areas of Colorado are unusual in that winter inter- <br />ception is a much larger component of the overall water <br />balance than for most other forested areas. Studies on the <br />FEF have shown that completely removing the tree cano- <br />py increases the amount of snow water equivalent (SWE) <br />on the ground by approximately 20 -45 %, depending on <br />aspect. Clearcuts on the Manitou Experimental Forest <br />increased the SWE by 8 -35% (Gary, 1975). <br />The decrease in winter interception due to forest harvest <br />can be as large or larger than the decrease in summer <br />ET, particularly in wetter years. The exceptionally high <br />winter interception rates at the FEF can be attributed <br />to the low relative humidity, high average wind speed, <br />large surface area of snow in the tree canopy, and the <br />nearly continuous presence of snow in the tree canopy <br />in winter, especially on north- facing slopes. A series of <br />detailed studies have shown that the observed increase <br />in SWE following forest harvest or thinning is due <br />almost entirely to the reduction in winter interception <br />rates rather than the redistribution of snow into open- <br />ings as claimed in some earlier studies (Troendle and <br />King, 1987). For a given vegetation type and aspect the <br />amount of winter interception is nearly a fixed percent- <br />age of winter snowfall, and the increase in peak SWE is <br />directly proportional to the amount of the canopy that is <br />removed. In the subalpine zone the mean percent inter- <br />it) <br />:nt) <br />ception loss in winter and spring is approximately 25% <br />for conifers and II% for aspen (Troendle et al., 2003). <br />In lower elevation areas the increase in SWE after tim- <br />ber harvest is generally smaller, and a 22% reduction in <br />basal area did not significantly increase the SWE at the <br />Manitou Experimental Forest (Gary, 1975). <br />The other factor that governs the change in water yield is <br />the amount of evaporation and transpiration in the grow- <br />ing season. The general principle is that in drier years <br />and areas with shallower soils, summer ET savings are <br />minimized because the combination of soil evaporation <br />and transpiration from the residual vegetation will use <br />nearly all of the available water. Under these conditions <br />the reduction in winter interception will provide nearly <br />all of the increase in water yield from forest harvest. In <br />wetter years and on aspects with less winter interception, <br />proportionally more of the increase in water yield will be <br />derived from the reduction in summer ET (Troendle and <br />King, 1985; Troendle and Reuss, 1997). <br />Plot -scale data for different levels of thinning in lodge - <br />pole pine indicate that the reduction in winter intercep- <br />tion on the FEF is approximately two to three times larger <br />than the reduction in summer soil water depletion (Wilm <br />and Dunford, 1948). For the Fool Creek Experiment it <br />has been estimated that, on average, approximately 50% <br />of the increase in water yield is due to the reduction in <br />snow interception, and 50% is due to lower ET during <br />
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