DIGITALNA ARHIVA ŠUMARSKOG LISTA
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T. Dubravac, S. Dekanić, V. Roth: DINAMIKAOŠTEĆENOSTI I STRUKTURAKROŠANJA STABALA HRASTA... Šumarski list – Posebni broj (2011), 74-89 Posarić,D., 2008:Obnova spačvanskih šuma hrasta Rust,S., A. Roloff,2004:Acclimation of crown lužnjaka (Quercus roburL.) oplodnim sječama – structure to drought inQuercus roburL. – intra mogućnosti poboljšanja postojećeg načina rada. and inter-annual variation of abscission and Šumarski list, CXXXII(1–2): 53–63. traits of shed twigs. Basic andApplied Ecology 5 (3): 283–291. Potočić,N., I.Seletković,2009: Oštećenost šuma u Hrvatskoj 2009. godine. “Hrvatske šume” Teslak,K., 2010:Utjecaj strukturnih i prostorno-vre d.o.o. i Hrvatski šumarski institut, str. 29, Zagreb. menskih odrednica na planiranje gospodarenja šumama hrasta lužnjaka (Quercus roburL.). Di- Pretzsch, H., 2009: Forest dynamics, growth and sertacija, Šumarski fakultet Sveučilišta u Za yield.Springer-Verlag, 664str., Berlin Heidelberg. grebu, str. 212, Zagreb. Prpić,B., 1992: Odabiranje oštećenih stabala za sječu Thomas,F.M., R.Blank, G.Hartmann,2002: i obnova sastojina opustošenih propadanjem. Abiotic and biotic factors and their interactions Šum. list CXVI(11–12): 515–522. as causes of oak decline in Central Europe. For. Prpić,B., 1996: Propadanje šuma hrasta lužnjaka. U: Path. 32:277–307. Klepac, D. (ur.), Hrast lužnjak u Hrvatskoj, Tikvić, I., Ž. Zečić, D. Ugarković, D. Posa- HAZU Centar za znanstveni radVinkovci i Hrrić, 2009. Oštećenost stabala i kakvoća drvnih vatske šume, 273–298. sortimenata hrasta lužnjaka na spačvanskom po Prpić, B.,A. Vranković, Đ.Rauš, S.Matić,A. dručju. Šumarski list, CXXXIII(5–6): 237–248. Pranjić, Š.Meštrović,1994: Utjecaj ekoloTikvić, I., D.Ugarković, J.Gašpar, 2011:Pro ških i gospodarskih činilaca na sušenje hrasta storna analiza odumiranja stabala hrasta luž lužnjaka u gospodarskoj jedinici Kalje šumskog njaka (Quercus roburL.) za potrebe adaptivnoga gospodarstva Sisak, Glasnik za šumske pokuse gospodarenja šumskim ekosustavima u Hrvat 30:361–419. skoj(Spatial Analysis of Pedunculate Oak Mor Prpić, B., Z. Seletković, G. Žnidarić, 1994: tallity Rate for Adaptive Forest Ecosystem Ekološki i biološki uzroci propadanja stabala Management in Croatia). Croatian Journal of hrasta lužnjaka (Quercus robur L.) u nizinskoj Forest Engineering 32(1): 43–56. šumiTuropoljski lug. Glasnik za šumske pokuse Vajda,Z., 1948: Utjecaj klimatskih kolebanja na su 30:193–222. šenje hrastovih posavskh i donjopodravskih Redfern, D.B., R. C.Boswell,2004:Assessment šuma nizinskih šuma. Institutza šumarskaistra of crown condition in forest trees: comparison of živanjaMinistarstva šumarstvaN. R. Hrvatske, methods, sources of variation and observer bias. str. 154, Zagreb. Forest Ecology and Management, 188: 149–160. Wargo, P. M., 1996: Consequences of environmental Ritz,C., J. C.Streibig,2008:Nonlinear regression stress on oak: predisposition to pathogens.Ann. with R.Springer, str. 144,NewYork. Sci. For. 53:359–368. SUMMARY: The crown damage of a tree has a very prominent place among the broad spectrum of factors defining the pedunculate oak (Quercus roburL.) decline and dieback, largely due to the fact that it represents the first visible symptom of the decline in tree‘s vitality. Besides, crown damage is a key factor for the selection of trees with high risk of dying during the sanitary and salvage cuttings, in order to salvage high value timber that would be otherwise lost or severely degraded when the tree dies. Aim of this contribution is to investigate dynamics of crown damage of pedunculate oak trees, as well as the effect of the crown damage on tree’s basal area increment during longer time period in two most important types of pedunculate oak forests in Croatia. Research was done on permanent experimental plots situated in the stands of pedunculate oak and common hornbeam (II-G-10) and stands of pedunculate oak and Genista elata (II-G-20). In total, 38 permanent experimental plots were used, out of which 13 were re-measured with intervals of 9 to 17 years (Table 1). In first measurement, all trees on plots were permanently tagged, and map of tree locations and crown projections was made. Trees were measured for diameter at breast height (DBH), total tree height and height to crown base. Crown length was calculated as the difference between the total tree height and height to crown base, while the crown ratio was calculated as the ratio of crown length and total tree height. From the map of horizontal crown projections the average crown width was calculated as a mean of |