Second year after the fire broke out on Vidlič Mountain during the summer of 2007, the changes of burnt down beech wood vegtation were recorded. Fitocenological research of the beeech wood habitat at the location of Visoka Stena two years after the fire, was carried out in accordance with Braun-Blanquet method. The results of the terrain research were given in the form of fitocenological table. It was noticed that the most present species were Rubus idaeus, Epilobium angustifolium, Galium mollugo, Doronicum columnae, Lactuca muralis and Securigera varia. Turf grass such as Brachypodium sylvaticum, Poa nemoralis, Poa badensis, Festuca varia, Festuca valesiaca and Agrostis capillaris was also present which is a significant factor in the succession process as grass is a powerful colonist. The conclusion was that revitalization of the beech wood depends on how much the beech trees had been destroyed by the fire.

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Norway spruce is one of the most important economic species is Bosnia and Herzegovina. It is the species at the edge of its natural range; nevertheless it attains significant growth and yield results. The species is often used for afforestation purposes. In the previous period, 4 progeny tests of Norway spruce were established in Bosnia and Herzegovina. The offspring from 6 natural populations: Han Pijesak 1, Han Pijesak 2, Foča, Potoci, Olovo and Kneževo were build-in the progeny tests. In 2016, the samples of Norway spruce from 2 progeny tests: Srebrenica and Drinić were collected. In total, 360 samples were collected. DNA isolation was done according to Dumoline et al. (1990). For assessment of genetic differences among populations, co-dominant nSSR microsatellite system had been used. The number of effective alleles ranged from 7.78 in the population Potoci up to 15 in the population Kneževo, the average number of alleles was 13. The observed heterozygosity ranged from 0.61 for the population Han Pijesak 2 up to 0.68 for population Kneževo. The average observed heterozygosity was 0.65. Fixation index was in the range from-0.073 in the population Potoci, to 0.030 for the population Han Pijesak 2. The average value of Wright fixation index is-0.007. The average fixation index indicates the existence of a very small number of homozygotes. Concerning the variability among populations it has been concluded that the total level of genetic differentiation among populations was very low (FST= 0.026). The result of Nei's genetic distance shows that the populations Olovo and Potoci are separated from

The paper presents the results of the analysis of genetic variability of eight populations of silver fir (Abies alba Mill.) in Serbia obtained using SSR markers. The genomic DNA was isolated from tissue of needles of all eight populations. Due to the costly and lengthy process a small number of the SSR markers for Abies alba have been developed, so in this study were used the microsatellite markers of related species. The obtained results indicate a low level of the genetic variability between natural populations of silver fir. The total number of alleles detected with nine SSR markers in eight studied populations of silver fir is 28. The range of alleles varies from two for NFF15 to six for SF78 with an average of 3.1 alleles per locus. The mean value of genetic similarity between populations is 0.92. The smallest genetic similarity between pairs of populations is 0.82 (Dubočica Bare and Stara Planina; Dubočica Bare and Tara) and the greatest genetic similarity is 1 (Zlatar and Stara Planina, Zlatar and Tara, Stara Planina and Tara). A basic insight into the level of genetic diversity of natural populations of silver fir in Serbia, which are located in a relatively small area, has been given using a set of SSR markers. The obtained results can be used in the future strategy for the management and regeneration of silver fir forests.

Lavadinović V., Isajev V., Rakonjac L., Popović V., Lučić A.: Douglas-fir provenance phenology observations. Ekologia (Bratislava), Vol. 32, No. 4, p. 376-382, 2013.Introduction of species involves adaptation, productivity and success in new types of environmental conditions. The introduction also includes confirmation to bring in only species which are superior on their natural habitat. In Canada and western North America, Douglas fir (Pseudotsuga menziesii/Mirb./Franco) is one of the most ecologically and economically value trees. In Europe, New Zealand, Australia and Chile, Douglas fir is important as an exotic fast-growing timber species. Douglas fir has one of the widest natural ranges of any tree species, extending from the Pacific Coast to the eastern slope of the Rocky Mountains and from 19°N in Mexico to 55°N in western Canada. In Serbia, from the original seeds introduced from British Columbia and Canada, the experimental Douglas-fir provenance is established in a few locations. One of the main dangers for the Douglas fir is its sensitivity to the occurrence of late frost in spring and early occurrence of frost in the autumn. The aim of the paper is to test the effect of environment on the expression of Douglas-fir seed transfer. Bud burst phenology is closely related to genecology of introduced species. Douglas fir is susceptible to cold climate and most of its genetic structure and ability depends on its ecological adaptability. In order to avoid errors introduction of Douglas-fir provenances that are sensitive to the occurrence of extreme temperature, applied are researching for buds phenological changes Douglas fir, as an introduced species, has to be tested at the provenance level before its introduction to the new sites in Serbia.