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i <br />? <br /> <br />Zfl <br />15 <br />c <br />U <br />?..i <br />a? 10 <br />>- <br />.? <br />a? <br />a4 <br />? <br />U <br />0 <br />• <br />• <br />• • <br />? . <br />• •? • <br />• <br />• <br />• <br />• ' ?? •• <br />• • • • <br />• <br />. • • <br />0 10 20 30 40 <br />Years Since Treatment <br />Figure 3. Increase in flow from Fool Creek plotted over years after Harvest. <br />Timber harvest on Fool Creek did not result in a significant increase in <br />summer storm peaks, attesting to the assumption that in water limiting <br />systems the late summer precipitation is used on-site with or without over <br />story vegetation (Troendle 1987). <br />Observations made on Fool Creek, as well as other plot studies, at the Fraser <br />Experimental Forest led to the development of a series of sub alpine water <br />balance models that began in the 1970's. The first of these models, <br />MELTMOD, simulated accumulation and melt of snow. This was followed <br />by the WATBAL model, which incorporated MELTMOD, but in addition <br />simulated a water balance for forest vegetation (Leaf and Brink 1973). The <br />next generation model was LUMOD (Leaf and Alexander 1975), a land use <br />simulator that incorporated output from an even-aged growth and yield <br />model (RMYLD) (Edminster 1978) in the WATBAL model to simulate <br />water yield responses to clear cutting. <br />These early models assumed that clear cutting had the greatest impact upon <br />snow pack accumulation, because at the time it was believed that the <br />measured increase.. of snow, present in openings following timber harvest, <br />was the result of increased deposition during the snow fall event and <br />redistribution of snow intercepted in the surrounding canopy, between <br />events. This relationship was incorporated in the models as a"Rho" <br />distribution function (see Troendle and Leaf 1980) in which snow retention <br />in the opening (or accumulation) was a factor of opening size. Thus, the <br />6