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the growing season (C. Troendle, Matcom Corp., pers.
<br />comm., 2000).
<br />Plot- and catchment -scale studies on the FEF indicate
<br />that the pattern of forest harvest has a surprisingly small
<br />effect on the magnitude of the resulting water yield
<br />increase. In the Deadhorse North experiment 36% of
<br />the basal area was removed by patch cutting, and the
<br />increase in annual water yield was proportional to the
<br />percent of basal area removed. Removing 40% of the
<br />basal area in the first step of a shelterwood cut resulted
<br />in a 16% increase in peak SWE, and the observed in-
<br />crease in streamflow, while too small to be statistically
<br />significant, was consistent with the observed increase in
<br />SWE (Troendle and King, 1987). These results suggest
<br />that the reductions in winter interception were directly
<br />transformed to streamflow, and the additional water
<br />generated in a spatially - distributed manner across the
<br />hillslopes was able to reach the stream channel.
<br />In drier areas and areas where summer ET is the pri-
<br />mary source of "saved" water, the pattern and location
<br />of forest harvest can have a much greater effect on the
<br />observed change in annual water yields. Baker (1986)
<br />found that watersheds with longer and flatter hillslopes
<br />generated smaller increases in runoff after forest thin-
<br />ning than steeper and narrower watersheds. Other studies
<br />have suggested that harvest- induced increases in runoff
<br />can be reduced because the remaining trees can scavenge
<br />the "saved" water from upslope areas before it is able to
<br />reach the stream channel (e.g., Ziemer, 1968; MacDon-
<br />ald, 1987). In general, the pattern of forest harvest and
<br />the location of the harvest relative to the stream channel
<br />are more likely to affect the magnitude of a water yield
<br />increase in drier, lower - elevation areas and possibly in
<br />drier years in sub - alpine areas. In the higher - elevation,
<br />wetter sub - alpine zone most of the interception savings
<br />will probably be transformed into runoff, regardless of
<br />the pattern of harvest or proximity to a stream channel.
<br />yields on north- facing slopes than south - facing slopes
<br />(Troendle et al., 1994). In contrast, aspect has relatively
<br />little effect on the magnitude of the reduction in summer
<br />ET after forest harvest, as the amount of ET is limited
<br />primarily by the amount of water rather than the amount
<br />of incoming energy (Troendle et al., 1994).
<br />Aspect can affect the magnitude and timing of potential
<br />water yield increases in higher- elevation forests by af-
<br />fecting both the amount of sublimation and the rate of
<br />snowmelt. In the sub - alpine zone, north - facing slopes
<br />typically have denser vegetation than south - facing
<br />slopes. This denser vegetation has higher interception
<br />rates, as the greater leaf area and higher winter branch
<br />turgor capture and hold more snow. Recent modeling
<br />studies assume a winter -spring interception loss rate of
<br />32% for north- facing slopes, 26% for east- and west -fac-
<br />ing slopes, and only 17% on south - facing slopes (Tro-
<br />endle et al., 2003). The difference in winter interception
<br />rates results in a greater potential to increase water
<br />In the case of Deadhorse Creek, openings on south -fac-
<br />ing slopes had a smaller increase in SWE than expected .
<br />from interception studies on other aspects (Troendle and
<br />King, 1987). This suggests that the orientation of for-
<br />est openings relative to the sun can affect the increase
<br />in SWE resulting from forest harvest, and this effect
<br />is probably due to differences in incoming shortwave,
<br />reflected shortwave, and longwave reradiation from the
<br />surrounding leave trees. In general, forest harvest will
<br />increase melt rates by increasing the amount of incom-
<br />ing solar radiation, increasing the turbulent transfer of
<br />sensible heat to the snowpack surface, and increasing the
<br />transfer of latent heat by condensation and freezing. All
<br />of these factors will vary with aspect, slope, prevailing
<br />wind direction, and wind speed. These differences mean
<br />that the increase in SWE, the increase in water yield, and
<br />the timing of an increase in water yield will vary with
<br />aspect (Baker, 1986).
<br />The size of the openings created by forest harvest and
<br />the amount of roughness also can affect the magnitude
<br />of the increase in SWE after forest harvest. Larger open-
<br />ings are more subject to wind scour, but this effect can be
<br />ameliorated if there is sufficient slash or other sources of
<br />roughness to capture and hold the snow within the open-
<br />ing (Troendle and Meiman, 1984). Because the annual
<br />runoff in snow - dominated areas is closely related to the
<br />maximum SWE, the ability of forest openings to retain
<br />snow can directly affect the magnitude of the increase in
<br />water yield after forest harvest.
<br />The water balance equation and the interplay between
<br />evaporation, interception, and transpiration can explain
<br />the observed interannual variability in water yield in-
<br />creases in response to forest harvest. In dry years a great-
<br />er proportion of the precipitation is needed to recharge
<br />soil moisture, and there may also be slightly greater
<br />soil moisture depletion due to the increase in potential
<br />evapotranspiration. In wet years there will be more soil
<br />moisture carryover, and less snowmelt or winter precipi-
<br />tation is needed for soil moisture recharge. Hence more
<br />of the interception and transpiration savings can be con-
<br />verted into runoff. The net result is that the increases in
<br />runoff following forest harvest are substantially greater
<br />in wet years than in dry years (Baker, 1986; Troendle and
<br />Kaufmann, 1987).
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