<br />Bulletin American Meteorological Society
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<br />run, avalanches occur under rare conditions of recog-
<br />nizably high avalanche danger, when cloud seeding
<br />would be suspended under accepted procedures. In
<br />areas of high avalanche frequency, such as many chutes
<br />in the Red Mountain Pass area of the San Juan Moun-
<br />tains, many avalanches run during nearly every major
<br />storm, and successful forecast and warning procedures
<br />have been developed, at least partially under the spur
<br />of prospective precipitation management. The occur-
<br />rence of delayed avalanches, after the storm has passed,
<br />is related partly to the augmented part of the snow load
<br />and mostly to features of snow stratigraphy and meta-
<br />morphosis not affected by precipitation management. To
<br />the extent that precipitation management focuses at-
<br />tention on avalanche warnings and countermeasures,
<br />it will tend to reduce, not increase, the hazard.
<br />
<br />3) GEOMORPHIC PROCESSES
<br />
<br />In its effect on geomorphic processes of soil erosion,
<br />mudflow activity, and transport of dissolved solutes,
<br />snowpack works through processes at a secondary level,
<br />through indirect links with vegetation and small mam-
<br />mals. Soil erosion occurs mostly in summer and where
<br />vegetative protection is lacking, and it tends to be
<br />greater at the margins of late-lying snowbanks where
<br />vegetation is sparse. Thus, an increase in the extent of
<br />late-lying snowbanks would likely have a discernible
<br />but highly localized effect on soil erosion. In the San
<br />Juan Mountains it was concluded that "other forms of
<br />man-induced erosion usually overwhelm the natural
<br />variability since they involve increases of orders of
<br />magnitude rather than a few tens of percent" (Caine,
<br />1976).
<br />
<br />4) STREAM RUNOFF
<br />
<br />Snowpack augmentation affects stream runoff and reo
<br />lated characteristics mostly in the headwaters portion of
<br />watercourses where regulation is usually absent. Simu.
<br />lation of particular sites under study has shown that
<br />precipitation management there would have no identi-
<br />fiable effect on the frequency and magnitude of flood
<br />flows.
<br />
<br />5) ALPINE VEGETATION
<br />
<br />The impact of snowpack augmentation on alpine vege-
<br />tation has been investigated mostly by installing snow
<br />fences to increase local snow accumulation in a gross
<br />manner and then observing the subsequent vegetational
<br />changes. In the San Juan Mountains, Webber et al.
<br />(1976) found that a I-week delay in snowmelt would
<br />occasion only a small reduction in biomass productivity,
<br />becoming serious for a 4- to 5-week delay. They con-
<br />cluded that a 15-30% snowpack increase over several
<br />decades would cause both qualitative and quantitative
<br />changes in vegetation, minor in nature and affecting
<br />probably <10% of the alpine area, and that the inci-
<br />dence of rare species might increase as a result. "These
<br />conclusions," they said, "refute the popular notion that
<br />tundra is a fragile ecosystem."
<br />On the San Juan Ecology Project, several study plots
<br />were located in subalpine forests and adjacent grassy
<br />
<br />495
<br />
<br />parks. The distribution of tree species was found to be
<br />strongly related to snowmelt date, which, in turn, de-
<br />pended greatly on elevation and exposure, southern
<br />slopes in the forest zone often becoming snowfree be-
<br />tweeen storms during the winter. Spruce growth was
<br />independent of snowpack depth, the amount of growth
<br />being apparently genetically controlled, whereas aspen
<br />was more responsive to spring soil temperature. Seasonal
<br />growth of ponderosa pine was positively correlated with
<br />the precipitation of the previous December.
<br />Stable aspen stands give way to fir, then spruce, as
<br />one goes to sites with longer snow duration and lower
<br />temperatures (Dix and Richardson, 1976). The seedling
<br />stage is the most sensitive to increased snow duration,
<br />and the maximum density of seedlings would tend to
<br />shift to sites that now have earlier snowfree dates.
<br />Variations in wood production directly attributable
<br />to delay of snowfree date were not detected. In spruce
<br />and fir, wood production was found to be constant.
<br />Among the herbaceous plants, the timing of the
<br />earliest phases of seasonal development was found to
<br />vary directly with the snowfree date, but this depen-
<br />dency became less and less marked as the season pro-
<br />gressed, and all species completed their development
<br />within the growing season. Although precipitation man-
<br />agement might delay the phenological coming of spring,
<br />especially in pockets of snow accumulation, it was con-
<br />sidered unlikely to have a direct effect on herbaceous
<br />populations except perhaps to reduce biomass produc-
<br />tion somewhat.
<br />In oak brush, which in parts of the San Juan Moun-
<br />tains is an important browse for elk, production was
<br />found most closely related to the amount of the previous
<br />summer's precipitation and to be very little affected by
<br />snowpack.
<br />In the Medicine Bow Mountains, decomposition of
<br />litter was found to be unaffected by increased snowpack.
<br />Leaching of nutrients from the soil did not appear
<br />to be large, but adequate determination of it was not
<br />achieved because of premature termination of the study
<br />due to funding cuts (Knight, 1975).
<br />
<br />6) ANIMAL POPULATIONS
<br />The relationship between snowpack augmentation and
<br />the winter range of elk was studied in the San Juan
<br />Mountains (Sweeney and Steinhoff, 1976). About 28%
<br />of the relevant elk winter range, as mapped by the
<br />Colorado Division of Wildlife, fell within the study area
<br />of the Skywater cloud seeding experiment, all of that
<br />range being within the portion of the study area desig-
<br />nated as upwind flank. It was found that a hoof
<br />penetrable snow depth of 40 cm initiated downslope
<br />migration, whereas a penetrable depth of 70 cm or more
<br />was avoided. In a model of winter range in the Mission-
<br />ary Ridge area, a 15% snowpack increase was found to
<br />correspond to a decrease in this part of the winter range
<br />varying from 0 to 20% depending largely upon ante-
<br />cedent snow conditions. Springtime upslope movement
<br />was regulated by the greening of vegetation rather than
<br />by retreat of snow line, and in each season there ap-
<br />peared to be ample habitat available for calving. The
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