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<br />gradual decrease in, biomsss occurred due to the <br />periodic mortality of individual trees that is common <br />in mature climax communities. The second type of per- <br />turbation occurred at the 3500m location on Missionary <br />Ridge where a severe loss in standing crop is shown <br />for 197~; this loss can be attributed to a high wind- <br />storm that caused severe wind throw on that high eleva- <br />tion site. Ovington (1962) stated that in mature <br />climax forests" the biomass is fairly constant from <br />year to year, as a result of an overall equilibrium <br />between production and decomposition; this type of <br />biomass pattern can be seen at the lower elevationa1 <br />plots at both locations. Kira ~ a1. (1967) concluded <br />that mortality rates in forests of cool climates <br />fluctuate from year to year and that in certain years, <br />several trees are lost in one year due to environ- <br />mental catastrophes, such 8S storms. Thus, the <br />biomass values of such forests will fluctuate over <br />time and the equilibrium value of climax can only be <br />recognized on a long-term basis. These subalpine <br />forests can therefore be best described as a <br />"disturbance climax"; the influences of snow manipu- <br />lation on such a system are difficult to separate <br />from the other environmental influences and could <br />only be studied over a long time period. <br /> <br />Influences of snow on the(spruce-fir association. <br /> <br />The direct influences of snow on the spruce-fir <br />association can be organized into two categories; <br />first, its effect on the length of the growing season, <br />and second, the physical effects of snow on the trees <br />themselves. ' <br /> <br />The snow melt ,pattern on the intensive study sites <br />varied considerably between the years 1972 and 1973 <br />(Figure 4). In 1972, the plots were free from snow <br />almost a month earlier than the following year when <br />snow persisted beyond the date of cambial activation <br />as estimated by Blaue (1973). In general, snow <br />remains much later in the season on the Wolf Creek <br /> <br /> 400 <br />E 350 <br />~ 300 <br />X <br />~ 250 <br />. <br />W 200 <br />a <br />~ 150 <br />0 <br />Z 100 <br />~ <br /> 50 <br /> <br />##ffoo,o, I <br />## 0,0,. <br />## O'o,......~ <br />..................# ~~ <br />'. <br />.. <br />'. <br />DEe JAN FEB MAR APR MAY JUNE JULY <br /> <br /> <br />, " <br /> <br />I <br /> <br />Pass locations than on Missionary Ridge and, accepting <br />these data, cambial initiation may often occur while <br />snoW is still on the ground. Blaue (op cit.) found <br />that the length of the growing season is set primarily <br />by photoperiod, with variables such as temperature <br />having a'minor effect. From these data, it could be <br />conciluded that the length of the growing season is <br />largely independent of the direct effects of persist- <br />ing : snow. <br /> <br />I <br /> <br />I <br /> <br />Dir4ct physical influences of snow on individual trees <br />is negligible on trees of the intermediate class or <br />greater; however, saplings and seedlings can be <br />adversely affected by extended periods of snow cover- <br />age:which increase the probability of snow breakage, <br />snow mold infection, or simply elimination of <br />sunlight. These conditions were observed to increase <br />definitely on the biomass plots in the heavy snow year <br />of 1973, compared to the other years of the study. <br />Considering the small stature and hence, small wood <br />pr04uction, of trees of these size classes, the wood <br />production of the stand as a whole is not significant- <br />ly affected. Such events sho~ld be noted, however, <br />because these smaller trees represent the future of <br />these stands and any such damage could reduce the <br />number of trees available for replacing those lost in <br />the overs tory. <br /> <br />I <br /> <br />I <br /> <br />I <br /> <br />Ii <br />If <br /> <br />l <br /> <br />.t' <br />, <br />i <br />~ <br />I, <br />I <br />I <br /> <br />I~ <br />i <br />c <br /> <br />'1 <br /> <br />Indirect effects of snow on wood production are those <br />influences on the forest microclimate including <br />modification of the soil temperature and soil water <br />regimes during the early part ~f the growing season. <br />The:influences of these facto~s on the physiology of <br />trees during the growing season are being analyzed <br />by the Tree Moisture Stress P~oject and are included <br />in the report of the next sec~ion. <br /> <br />Regardless of influences of snow within a given <br />growing season, the bolewood production of individual <br />trees of the spruce-fir association has been shown <br />to remain relatively const8nt'~ver the past 20 years <br /> <br /> 400 <br />E 360 <br />~ 300 <br />X <br />~ 250 <br />. <br />w 200 <br />0 <br />~ 150 <br />0 <br />z 100 <br />~ <br /> 50 <br /> <br />. ~ <br />........~~...... <br />........ ....... <br />........................... \ <br />.. <br />.... <br />, <br />, <br />, <br /> <br />I. <br />II <br />.1 <br />II <br /> <br />ii <br /> <br />IY <br />I <br />II <br /> <br />~ <br />II <br />" <br />9 <br />II <br /> <br /> <br />DEe JAN FEB MAR APR /'ylAY JUNE JULY <br /> <br />MISSIONARY RIDGE - 3200m MISSIONARY RIDGE-3500m <br />~ DATE OF CAMBIAL ACTIVATION (BLAUE,19[73) <br />1972 1973.......... <br /> <br /> 400 <br />E 350 <br />~ 300 <br />X <br />~ 250 <br />. <br />w <br />a 200 <br />~ 150 <br />0 <br />Z 100 <br />~ <br /> 50 <br /> <br />##...... <br /># ...... I <br />### ~~~ . <br />................ ..# ~~~ <br />.... ..........0# .... <br />'. <br />" <br />" <br />\'1- <br />, <br />, <br />, <br />, <br />, <br />JULY <br /> <br /> <br />DEe JAN FEB MAR APR <br /> <br />WOLF CREEK PASS - 3100m <br /> <br /> 400 <br />E 350 <br />~ 300 <br />x <br />~ 250 <br />. <br />w <br />0 200 <br />~ 150 <br />0 <br />Z 100 <br />~ <br /> 50 <br /> <br />#........ i <br />## ....' <br />### ~........ <br />..................... ........ <br />'. <br />" <br />............ <br />" <br />", <br /> <br /> <br />DEe JAN FEB MAR APR <br />WOLF CREEK PA1S-3300m <br /> <br />intensive sites, 1972-1913 <br /> <br />Figure 4 - Snow depth and duration at <br /> <br />23 <br />