Skógræktarritið - 15.05.2001, Page 142

Skógræktarritið - 15.05.2001, Page 142
are even reported to be a leading factor affecting forest degrada- tion in the industrial zone (Selikhovkin, 1993). Reindeer husbandry provides a traditional form of subsistence for the Saami people. The wild rein- deer population amounts to around lóthousand whereas tame reindeer number around 70 thousand. Although these popu- lations cover various areas, tame reindeer are tended under more or less the same natural condi- tions as wild reindeer (as far as the Saami people are concerned). Their migration is dictated by the availability of fresh pastures. During the summer, the reindeer disperse over a wide range of for- est territory, because at this time they favour the leaves and twigs of the mountain birch as well as the various grasses and herbs. Cladina-lichens are only eaten when wet. Damage to vegetation caused by reindeer trampling seems to be minimal. The winter pastures are situated mainly on the plains and have a predomi- nance of Cladina vegetation. Tame reindeer are concentrated near the villages during winter and, as a result, winter pastures around the villages become over- grazed. This has resulted in the establishment of grasses, such as Nardus stricta, Descfiampsia cespitosa and D. flexuosa. Recreation and tourism. The sur- roundings of industrial centers and more distant sites are similar- ly popular destinations for some number of people - either for relaxation, or exploring activity. Skiing, camping and hiking have locally detrimental effects, but vegetation usually recovers after the pressure decreases. The most successful invaders of such sites are graminoids, apocarpic moss- es, and fruticose and foliose lichens. Succession after such small-scale disturbance often results in some increase in species diversity compared with adjoinong sample plots. The dam- age caused by off road vehicular traffic, local drilling and local fires, especially caused by spilling of fuel, are potentially serious causes of degradation of landscapes. Conclusion Although many studies have investigated birch forests as part of the vegetation cover of in Murmansk Province, numerous unsolved problems relating to birch forest ecosystems still exist. On the one hand, Betula pubescens is reported as a species to be highly resistant to aerial pollution, whereas on the other hand, birch timberline ecosystems are referred to as the most sensitive in relation to damage caused by pollution. To make a comprehensive study of the birch forests' ability to resist and regenerate after disturbance caused by pollution, we need: 1) to use the available information on their structure and composi- tion relative to the habitat; 2) to examine all possible birch forest ecosystem parameters, such as the coenopopulation structure and properties, the litter and soil composition and processes, the microbiota and so on; 3) to organize the investigations along gradients of the main eco- logical factors. References (*= in Russian, **= with English summary) Ahti T., Hamet-Ahti L., )alas I., 1968. Vegetation zones and their sec- tions in northernmost Europe. - Ann. Bot. Fenn. N. 5. P. 169-211. Anon. 1965, 1968*. Handbook of the climate of the USSR. Issue 2, Murmansk Province. Part 2, Air and soil temperature; Part 4, Air humidity, rainfall and snow cover. Hydrometeorological Publishers, Leningrad. Avrorin, N.A.,Kachurin, M.Kh., Korovkin, A.A. 1936*. Materials on the vegetation of Khibiny Moun- tains. Proceedings of SOPS, Kola series, N 11. Hámet-Ahti, L. 1963. Zonation of the mountain birch forests in northern- most Fennoscandia. - Ann. Bot. Soc. ‘Vanamo’, T. 34, N 4. 128 p. Geologicheskoe opisanie (Geological description). 1958. ln: Geologia SSSR (Geology of USSR) XXVII. Murmanskaya oblast’ (Murmansk Regionl, pp. 180-247. Ioscow. Hill, M.O. TWINSPAN. A Fortran pro- gram forarranging multivariate data in ordered two-way table by classification of the individuals and attributes. - Ecology and Systematics. Cornell University, Ithaca, New York, 1979. 49 p. ignatov, M.S. , Afonina, O.M. (eds.) 1992. Check-list of mosses of the former USSR.-Arctoa, vol. 1 (1-2), pp.l-86. Konstantinova N.A., Potiomkin, A.D. Schljakov, R.N. 1992. Check-list of Hepaticea and Anthocerotae of the former USSR. - Arctoa, vol. 1 (1-2), pp.87 -127. Lid, |„ Lid, D.T. 1994. Norsk Flora. Det Norske Samlaget, Oslo. 1014 p. Nekrasova, T.P. 1938*. The vegetation of the alpine and subalpine zones of Chuna-tundra on the Kola Peninsula Transactions of Lapland State Reserve. I: 7-176. Neshatayev, V.Yu. & Neshatayeva, V.Yu. Birch forests of the Lapland State Reserve. - ln: Kozlov, M.V., Haukioja, E. & Yarmishko, V.T. (eds.) Aerial pollutions in Kola Peninsula: Proceedings of the International Workshop. April 14- 16, 1992, St. Petersburg. Apatity, 1993, pp. 328-338. Santesson, R. The lichens and licheni- colous fungy of Sweden and Norway. Lund. 240 pp. Selikhovkin, A. 1993. Stressing agents in forests of the Kola Peninsula - ln: Kozlov, M.V., Haukioja, E. & Yarmishko, V.T. (Eds.) Aerial pollu- tions in Kola Peninsula: Proceed- ings of the International Workshop. April 14-16, 1992, St. Petersburg. Apatity, 1993, pp. 47-52. Ushakova, G.l. 1997**. Biogeochemi- cal sycling of elements and soil for- mation in the forests of the Kola peninsula. Apatity. 150 pp. 140 SKÓGRÆKTARRITIÐ 2001 l .tbl.
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