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Phenology of Quercus ithaburensis with emphasis on the effect of fire
Institution:1. Department of Forestry Technologies and Construction, Faculty of Forestry and Wood Sciences, Czech University of Life Sciences Prague, Kamýcká 1176, Praha 6 - Suchdol, 16521, Czech Republic;2. Silva Tarouca Research Institute for Landscape and Ornamental Gardening, public research institution, v.v.i., Květnové náměstí, 391252 43, Pr?honice, Czech Republic;1. Department of Earth and Environment, Boston University, 675 Commonwealth Ave., Boston, MA, United States;2. Jet Propulsion Laboratory, California Institute of Technology, 4800 Oak Grove Dr., Pasadena, CA, United States;3. Department of Biology, Boston University, 5 Cummington Mall, Boston, MA, United States;1. Croatian Forest Research Institute, Division of Ecology, Cvjetno naselje 41, 10450 Jastrebarsko, Croatia;2. Department of Geoinformation Science, University of Zagreb, Faculty of Geodesy, Ka?i?eva 26, 10001 Zagreb, Croatia;1. Dept. of Remote Sensing and GIS, Faculty of Geography, University of Tehran, Tehran, Iran;2. Forest Research Division, Research Institute of Forests and Rangelands, Agricultural Research, Education and Extension Organization (AREEO), Tehran, Iran;3. Forests and Rangelands Research Department, Khuzestan Agricultural and Natural Resources Research and Education Center, Agricultural Research Education and Extension Organization, AREEO, Ahvaz, Iran;1. Department of Ecology and Evolutionary Biology, University of California, Santa Cruz, 1156 High Street, Santa Cruz, California 95064, USA;2. Department of Forest Management, College of Forestry and Conservation, University of Montana, 32 Campus Drive, Missoula, Montana 59812, USA
Abstract:Observations on the phenology of Quercus ithaburensis were carried out during three consecutive years in Yahudia Nature Reserve, Israel. Bud-break occurred mostly in February with minor bud breaks in March–April, May and September–October. Trees shed leaves in October through January with a peak in December–January, but even during these months at least 10% of the trees remained evergreen. Branch growth took place during February–April. Shedding of 1-year old branches was recorded in half of the observations, accompanied by the formation of abscission tissue. Acorns generally began to ripen in November and shedding extended from December until January. The percentage of acorns attaining full ripeness varied considerably from branch to branch and from year to year, reaching approx. 20% of the number of acorns found in May. Ripe acorns appeared exclusively on 2-year old branches. The degree of fire damage to trees greatly depended on the intensity of the fire, which in turn depended on weather conditions, quantity of dry pasture vegetation, and the location of the tree relative to cairns. Most trees were located within cairns, which constituted insulation belts, as no herbaceous vegetation grows on them. The effect of grazing intensity was decisive to the extent that fire damaged trees. Reduction of the bulk of dry pasture vegetation, affected the number of trees harmed, both as to their revival and their re-budding potential. Heavy grazing reduced to nearly half the number of trees suffering damage. After an early summer fire, budding was monitored, but not after a late summer fire.
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