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In the snow zone of the Central Rockies, forest removal has been shown to <br />reduce canopy interceptior.i losses in the winter months, resulting in greater - <br />snow pack accumulation (Wi:(m and Dunford 1948; Dietrich and Nleiman <br />1974; Gary and Troendle 1982; Troendle and Meiman 1984; Potts, 1984; <br />Gary and Watkins 1985; Troendle and King 1987; Meiman 1987; Schmidt <br />and Troendle 1989; and Tr•oeridle and Reuss 1997). A similar reduc.tion in <br />interception loss (E), as we;ll a.s reduced transpiration (T), occurs during the <br />growing season following, harvest (Wilm and Dunford 1948; Tr-oendle <br />1987a; Troendle and Reuss 1997). The reduction in summer ET results in <br />less soil-water depletion or.isite:, but it is only at the hillslope level that these <br />wetter soils have, heretofo:re, lbeen demonstrated to result in an increase in <br />either late season base flow, or'summer storm response (Troendle and. Reuss <br />1997). This lack of derrnon"trated, late-season stream flow respanse to <br />timber harvest is a reflection of the limited precipitation, causing t:he sub <br />alpine forest to be water-limited in the late summer. The elevated soil- <br />moisture levels in the harve;sted area, although not generally a demonstrated <br />factor in influencing curre,nt season runoff, do play a significant role in <br />response during the next snoAfmelt period. At that time, less melt-water is <br />needed onsite to recharge the :>oil and excess melt-water becomes available <br />for stream flow sooner (Troen.dle and King 1987; Troendle 1987b). As a <br />result, changes in flow res'ulting from forest disturbance in the snow zone -- <br />have always occurred on tlze rzsing side of the hydrograph, or early in the <br />runoff season. In all snoiv zone studies, monthly flow change has been <br />observed to consistently oc;cur only in May and sometimes in June during <br />snowmelt runoff (Troendle et at. 1998) with no detectable change duri.ng the <br />balance of the runoff season. In addition, the lar est increases in seasonal <br />flow, following rimber hai-ves,t, occur during the wettest years while the <br />srr.?allest increases in seasonal flow are usuall associated with the drier <br />_years (Troendle and Leaf 19M; roendle and King 1985, 1987; Troend t <br />al. 1998). T hese two factors r.nan date t hat a dequate storage be avai lab le to <br />make the increases in yield ava.ilable when needed such as during periods of <br />low flow. In contrast, the slow- growth rate of sub alpine vegetation makes <br />hydrologic recovery following timber harvest, or the return to pre-riarvest <br />flow levels, quite slow (Traenclle and King 1985; Shepperd et al. 1991) and <br />makes the efficiency and cos1; effectiveness of water yield augmeritation <br />seem quite attractive. <br />The first "paired" watersheci sriidy that looked at the effect of timber haivest <br />on water yield occurred on the headwaters of the Rio Grande River at <br />Wagon Wheel Gap, CO (Bates and Henry 1928). Stream flow from two -- <br />3