broj: 3-4/2013
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| RIJEČ UREDNIŠTVA | ||
| Uredništvo | ||
| WHERE DID POLITICALLY BASED PERSONNEL RECRUITMENT AND NON-MARKET MANAGEMENT LEAD US pdf HR EN | 133 | |
| IZVORNI ZNANSTVENI ČLANCI | ||
| Andrej Rozman, Alen Vajdetič, Jurij Diaci | UDK 630*234 (Abies alba Mill.) (001) | |
| A PROTECTED SILVER FIR (Abies alba Mill.) STAND IN SECONDARY SUCCESSION ON A FORMER PASTURE IN POLJANSKA DOLINA, SLOVENIA pdf HR EN | 135 | |
| Drago BRUMEC, Črtomir ROZMAN, Marjan JANŽEKOVIČ, Jernej TURK, Štefan ČELAN | UDK 630*10+156 (001) | |
| AN ASSESSMENT OF DIFFERENT SCENARIOS FOR AGROFORESTRY ENVIRONMENT REGULATION OF DEGRADED LAND USING INTEGRATED SIMULATION AND A MULTI-CRITERIA DECISION MODEL – A CASE STUDY pdf HR EN | 147 | |
| Athanasios STAMPOULIDIS, Elias MILIOS*, Kyriaki KITIKIDOU | UDK 630*23 (Juniperus excelsea M. Bieb.) (001) | |
| THE REGENERATION OF PURE Juniperus excelsa M. Bieb. STANDS IN PRESPA NATIONAL PARK IN GREECE pdf HR EN | 163 | |
| Miloš Koprivica, Bratislav Matović, Snežana Stajić, Vlado Čokeša, Đorđe Jović | UDK 630*814+524+537 (001) | |
| DEAD WOOD IN MANAGED BEECH FORESTS IN SERBIA pdf HR EN | 173 | |
| Abstract: Dead wood in forests of Serbia hasn`t been studied so far, although it is an important component of forest ecosystems. This paper presents results of investigating volume, biomass, and carbon stock bound in the dead wood of beech high forests. The sample includes eleven pure beech stands selected in six forest regions. They are all uneven-aged stands that have been managed for the last several decades, mostly under selection or group-selection. Their site class is I/II–III/IV. The altitude ranges from 400 to 1380 m. One stand belongs to submontane (Fagetum moesiacae submontanum B. Jov. 1967) and ten to montane (Fagetum moesiacae montanum B. Jov. 1953) beech forests. A systematic sample was used to determine the presence, quantity, diameter structure of volume, and state of dead wood considering its degree of decomposition both in standing and lying position. Sample plots of 500 m2, at a distance of 100 x 100 m were used as elements of the sample. Altogether 242 sample plots were established. The volume of aboveground dead wood was determined by applying familiar dendrometric methods, while the dry biomass was calculated on the basis of its volume and wood density at different degrees of decomposition. The biomass of belowground dead wood i.e. roots of stumps and snags was obtained directly using the relevant regression equations. The quantity of the carbon bound in dead wood was calculated by multiplying dry biomass of dead wood by 0.5 coefficient. A simple and a stratified sample were used for the purposes of estimating the average and total volume, biomass, and carbon stock of dead wood. It was concluded that the average aboveground deadwood volume in all studied stands amounted to 19.24 m3 ha–1. The aboveground biomass of dead wood was 6.06 t ha–1 and belowground 17.34 t ha–1, or 23.40 t ha–1 in total. The carbon-bound stock in the total estimated dry biomass of dead wood was 11.70 t C ha–1. Key words: dead wood; managed beech forests; stand; volume; biomass; carbon; sample | ||
| PRETHODNO PRIOPĆENJE | ||
| Kristijan Tomljanović, Marijan Grubešić, Dean Konjević, Zlatko Tomašić | UDK 630*156 (Perdix perdix L.) | |
| SUCCESS OF RELEASING AND REINTRODUCING GREY PARTRIDGE (Perdix perdix L.) INTO THE WILDERNESS FROM ARTIFICIAL BREEDING IN HUNTING GROUND OF CENTRAL CROATIA pdf HR EN | 185 | |
| PREGLEDNI ČLANCI | ||
| Dinka Matošević, Ivana Pajač Živković | UDK 630*453+145.7 | |
| ALIEN PHYTOPHAGOUS INSECT AND MITE SPECIES ON WOODY PLANTS IN CROATIA pdf HR EN | 191 | |