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<br />"I,' ~''!')J~f\ <br />f)J:,..o.... ;] <br /> <br />The disposition of silver in Boil and vegetation was <br />measured 1n spring and fall on five transects which <br />included subalpine meadows, and spruce and aspen <br />communities. Over the 4 years of field study, no <br />increases In silver concentration were found. How- <br />ever, seasonal fluctuations indicate higher levels <br />in spring than 1~ fall, as has been reported in <br />studies from other areas. In stream water, the data <br />from other studies (United States Geological Survey <br />1970, 1972, 1973) suggest a direct relationship be- <br />tween stream discharge and silver concentration, hut <br />thi9 undoubtedly derives from naturally occurring <br />silver In the field area. During the study period, <br />the highest discharge of both silver and water <br />occurred in t973. This follo~ed a ~inter with less <br />cloud seeding than the previous two, but ~ith a <br />higher than normal snowfall. <br /> <br />Silver concentrations in the soil and vegetation <br />around a generatDr show the highest levels adjacent <br />to the generator itself with a decline to background <br />levels in less than 200 m distance down~ind. Even <br />with an extended period of operational cloud seeding <br />(up to 100 years) silver accumulation in the soil <br />will not reach a 1 ppm level. Field observations <br />and laboratory studies on soil columns both show that <br />most silver iodide is adsorbed sufficiently strongly <br />on surface soil and litter particles to minimize <br />further movement, at least in the short-term. No <br />impact by silver iodide on pldnt growth or animal <br />populations has been observed in this study. <br /> <br />Field and laboratory studies do show some uptake of <br />silver by plants from application of the free ions <br />of silver nitrate, reagent-grade silver iodide, and <br />silver iodide which has passed through a seeding <br />generator. However, in general, less uptake occurs <br />from silver iodide than from the more soluble silver <br />nitrate, and the resulting concentrations tend to be <br />lower in the above-ground portion of subalpine mea- <br />dow plants than in the applied solution. Within the <br />plant community, silver Is most concentrated in the <br />litter, roots, and folfage ~ith highest concentration <br />in the surface soil zone of the plant-soil system. <br /> <br />This surface soil zone, in which most silver accumu- <br />lation occurs, has a high microbial biomass and <br />activity in terrestrial ecosystems, so there is the <br />potential for a decrease in the rates of organic <br />decomposition. This could produce an accelerated <br />rate of organic matter accumulation at the soil <br />surface, if plant-growth continues at normal rates. <br />However, experimental evidence suggests that silver <br />concentrations of at least 2 ppm (one or two orders <br />of magnitude higher than those presently found in the <br />litter zone) would be needed to initiate this process. <br /> <br />PLANTS <br /> <br />In the San Juan Mountains, plant studies have been <br />made 1n the alpine tundra; the subalpine forest of <br />spruce, fir, and aspen; the subalpine meadows; and in <br />the oak brush of the montane zone. These investi- <br />gatiOns were concerned primarily with the effects <br />of snow cover on the phenology and productivity of <br />selected plant species, and on phytosociology of the <br />plant communities. <br /> <br />Phytosodological studies were conducted in both the <br />subalpine forests and in the alpine tundra. They <br />have established a quantitative description of the <br />vegetation, placing it in some perspective with plant <br />communities else~here, and have indicated the types <br />of vegetation responses that may be anticipated with <br />particular environmental changes. Gradients in snow <br /> <br />duration and moisture were shown to relate quite <br />strongly to vegetation species composition. In the <br />subalpine forests. spruce is associated with a longer- <br />lasting snow cover than fir, while aspen lies even <br />further down the contInuum of snoW cover duration. <br />Similar relationships to snow cover were found for <br />the tundra plant communities. This suggests that a <br />long-term increase in the duration of the winter <br />snowpsck in both forest and tundra situations will <br />induce a change in the species composition in favor <br />of those plants which are more tolerant of a late- <br />lying snow cover. <br /> <br />Observations of snow cover duration, air and soil <br />temperature, soil moisture, solar radiation, and <br />subalpine tree moisture stress indicate that the <br />sequence of plant growth and development in spring <br />and early summer is also related to the duration of <br />snow cover. or to local conditions re[lecting it. In <br />the alpine, snow fences were used to augment snow <br />accumulation on experimental siteS. Comparative ob- <br />servations on experimental and control plots showed <br />that initiation of vegetative growth ~as delayed <br />under experi~ental conditions in almost all species <br />examined. In the subalpine, the relationship bet..,een <br />snow and initiation of stem elongation growth in <br />Englemann spruce was not clear, although rate of <br />elongation, initiation of radial growth, vegetative <br />bud burst. and floral bud burst are all negatively <br />correlated with the snow cover duration. Tree <br />moisture stress showed a strong positive correlation <br />with the snow depth during the snowmelt period. <br />Relatively high daytime moisture stress ~as associated <br />..,ith cold soils resulting from late-lying snow. The <br />initiation of shoot growth of oak also followed date <br />of snow clearning. <br /> <br />Late-lying snow resulted in shorter active growth <br />periods for tundra plants, subalpine herbac~ous <br />plants, and trees. With shortened active gro~th <br />periuds, both alpine and subalpine herbaceous plants <br />demonstrated a "catch up" faCility, I.e. the ability <br />to comp~ete a sequence of phenological events in a <br />shorter period of time. However, data indicate that <br />the capacity for seed germination was inhibited in <br />seeda Qf those species which had sn abbrevi~ted <br />gro....nng season. <br /> <br />In the alpine. a delay in the initiation of gro~th <br />resulted in lower productivity on some sites. Simu- <br />lation modelling predicts that this effect would be <br />slightly greater on plant communities occupying <br />xeric sites than on those of more mesic areas. It <br />amounted to a reduction in aboveground productivity <br />of 17 percent in the former case and 14 percent in <br />the latter, assuming a 15 day del~y in snowmelt in <br />both cases. <br /> <br />Examination of bolewood biomass production by spruce <br />over a 20 year period showed very little varia- <br />tion in annual growth increment. This indicates <br />little response to temporal changes in the snow <br />cover. However, the technique used in this analysis <br />seemed to lack sensitivity. The lack of response <br />was not supported by the microscopic examination of <br />wood cores taken during the growth period, or by <br />phenological observations of radial growth. <br /> <br />Results from both alpine and subalpine situations <br />indicate that the cessation of plant growth in late <br />summer and fall was quite regular from year to year, <br />suggesting a photoperiod control. Thus a late-lying <br />snow cover causes a shorter growing period. This <br />could result" in reduced productivity if not compen- <br />sated by an increase in the growth rate. In some <br /> <br />9 <br />