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BRAUN-BLANQUETIA, vol. 46, 2010 225 FLORISTIC CHANGE DURING EARLY PRIMARY SUCCESSION ON LAVA, MOUNT ETNA, SICILY * ** Roger DEL MORAL , Emilia POLI MARCHESE * Department of Biology, Box 351800, University of Washington, Seattle, Washington (USA) E-mail: [email protected] ** Università di Catania, c/o Dipartimento di Botanica, via A. Longo 19, I-95125, Catania (Italia) E-mail: [email protected] ABSTRACT sis; GF=growth-form; GPS=global po- can lead to alternative stable vegetation sitioning system; HC=half-change; types (FATTORINI &HALLE, 2004; TEM- Weinvestigatedthedegreetowhi- NMS=nonmetricmultidimensionalsca- PERTON &ZIRR,2004;YOUNG etal.2005). ch vegetation becomes more similar ling; PS=percent similarity. Convergence can be recognized if during primary succession and asked sample similarity increases with age, whether the age of a lava site alone NOMENCLATURE: Pignatti (1982). but chronosequence methods may con- determinesspeciescompositiononothe- found site and stochastic effects with rwise similar sites or if site-specific effects due to age. Though chronose- factors are more important. The study INTRODUCTION quence methods must be employed in wasconfinedto lavaflowsfoundbetwe- long trajectories (DEL MORAL&GRISHIN, en 1,000 and 1,180 m on the south side The mechanisms that guide the 1999), the underlying assumption that of Mount Etna, Italy that formed from assembly of species are complex (KED- all sites were initially identical has ra- 1892 to 1169 or earlier. Ground layer DY, 1992; WALKER & DEL MORAL, 2003). rely been tested. Here we explore the cover wasmeasured at15exposed sites During primary succession, landscape relationship between time and develop- and 12 sites under shrubs, using ten 1- context and chance produce mosaics ment on a small part of Mount Etna, m2 quadrats in five plots at each site. -
Department of Agriculural and Forestry Sciences
Department of Agriculural and Forestry Sciences PhD in Sciences and Technologies for the Forest and Environmental Management – XXVIII Cycle Scientific Sector-Disciplinary AGR/05 Plant Biodiversity in West Bank: Strategic tools for Conservation and Management PhD Thesis Presented by Dott. ssa NISREEN AL-QADDI Coordinatore Supervisor Prof. Bartolomeo Schirone Prof. Bartolomeo Schirone Signature ……………………. Signature ……………………. Tutors: Prof. Bartolomeo Schirone Dr. Federico Vessella Dr. Marco Cosimo Simeone. Dr. Michela Celestini This Thesis submitted in fullfillment of requirments for the Degree of Doctor of Philosophy. Academic years 2013-2016 DIPARTIMENTO DI SCIENZE AGRARIE E FORESTALI Corso di Dottorato di Ricerca in Scienze e tecnologie per la gestione forestale ed ambientale –XXVIII Ciclo Settore Scientifico-Disciplinare AGR/05 Plant Biodiversity in West Bank: Strategic tools for Conservation and Management Tesi di dottorato di ricerca Dottorando Dott. ssa NISREEN AL-QADDI Coordinatore Supervisor Prof. Bartolomeo Schirone Prof. Bartolomeo Schirone Firma ……………………. Firma ……………………. Tutors: Prof. Bartolomeo Schirone Dott. Federico Vessella Dott. Marco Cosimo Simeone. Dott.ssa. Michela Celestini Anni Accademici 2013-2016 The Phd thesis “Plant Biodiversity in West Bank: Strategic tools for Conservation and Management” has been defined by Nisreen Alqaddi (Palestine) in June 27, 2016. The Thesis comitte memebers are: Prof. Bartolomeo Schirone, Universita’ degli Studi della TusciaDAFNE. Prof. Maurizio Badiani, Universita’ degli Studi di Reggio Calabria, Dip. di Agraria. Prof. Massimo Trabalza Marinucci, Universita’ degli Studi di Perugia, Dip. di Medicina Veterinaria. Tutors: Prof. Bartolomeo Schirone. Dr. Federico Vessella. Dr. Marco Cosimo Simeone. Dr. Michela Celestini. DEDICATION This Thesis dedicated to My Father, who has raised me to be the person I am today, thank you for all the unconditional love, guidance, and support that you have always given me, thank for everything that you have done, you are to me what to earth the sun is. -
Vascular Plant Species Diversity of Mt. Etna
Vascular plant species diversity of Mt. Etna (Sicily): endemicity, insularity and spatial patterns along the altitudinal gradient of the highest active volcano in Europe Saverio Sciandrello*, Pietro Minissale* and Gianpietro Giusso del Galdo* Department of Biological, Geological and Environmental Sciences, University of Catania, Catania, Italy * These authors contributed equally to this work. ABSTRACT Background. Altitudinal variation in vascular plant richness and endemism is crucial for the conservation of biodiversity. Territories featured by a high species richness may have a low number of endemic species, but not necessarily in a coherent pattern. The main aim of our research is to perform an in-depth survey on the distribution patterns of vascular plant species richness and endemism along the elevation gradient of Mt. Etna, the highest active volcano in Europe. Methods. We used all the available data (literature, herbarium and seed collections), plus hundreds of original (G Giusso, P Minissale, S Sciandrello, pers. obs., 2010–2020) on the occurrence of the Etna plant species. Mt. Etna (highest peak at 3,328 mt a.s.l.) was divided into 33 belts 100 m wide and the species richness of each altitudinal range was calculated as the total number of species per interval. In order to identify areas with high plant conservation priority, 29 narrow endemic species (EE) were investigated through hot spot analysis using the ``Optimized Hot Spot Analysis'' tool available in the ESRI ArcGIS software package. Results. Overall against a floristic richness of about 1,055 taxa, 92 taxa are endemic, Submitted 7 November 2019 of which 29 taxa are exclusive (EE) of Mt. -
List of 735 Prioritised Plant Taxa of CARE-MEDIFLORA Project
List of 735 prioritised plant taxa of CARE-MEDIFLORA project In situ and/or ex situ conservation actions were implemented during CARE-MEDIFLORA for 436 of the prioritised plant taxa. Island(s) of occurrence: Balearic Islands (Ba), Corsica (Co), Sardinia (Sa), Sicily (Si), Crete (Cr), Cyprus (Cy) Occurrence: P = present; A = alien (not native to a specific island); D = doubtful presence Distribution type: ENE = Extremely Narrow Endemic (only one population) NE = Narrow Endemic (≤ five populations) RE = Regional Endemic (only one Island) IE = Insular Endemic (more than one island) W = distributed in more islands or in a wider area. Distribution type defines the "regional responsibility" of an Island on a plant species. Criteria: Red Lists (RL): plant species selected is included in the red list (the plant should be EN, CR or VU in order to justify a conservation action); Regional Responsibility (RR): plant species selected plays a key role for the island; the "regional responsibility" criterion is the first order of priority at local level, because it establishes a high priority to plants whose distribution is endemic to the study area (an island in our specific case). Habitats Directive (HD): plant species selected is listed in the Annexes II and V of the Habitat Directive. Wetland plant (WP): plant species selected is a wetland species or grows in wetland habitat. Island(s) where Distribution Island(s) where Taxon (local checklists) Island(s) of occurrence conservation action(s) type taxon prioritised were implemented Ba Co Sa Si Cr Cy RL RR HD WP Ex situ In situ Acer granatense Boiss. P W 1 Ba Ba Acer obtusatum Willd. -
Ethnobotanical Study of Medicinal Flora in the North East of Algeria - an Empirical Knowledge in Djebel Zdimm (Setif)
Journal of Materials Science and Engineering A 5 (1-2) (2015) 50-59 doi: 10.17265/2161-6213/2015.1-2.007 D DAVID PUBLISHING Ethnobotanical Study of Medicinal Flora in the North East of Algeria - An Empirical Knowledge in Djebel Zdimm (Setif) Sabah Chermat1* and Rachid Gharzouli2 1. Department of Pharmacy, Faculty of Medicine, University of Setif, Setif 19000, Algeria 2. Department of Plant Ecology, Faculty of Natural Sciences and Life, University of Sétif, Setif 19000, Algeria Abstract: On the high plains of Setif, the old inhabitants have built a real knowledge of medicinal plants properties. Traditional knowledge about plants and their properties are still fairly common. Our scientific motivation stems from the absence of any flora and ethnobotanical study in this area. During different field campaigns, we identified 93 medicinal species belonging to 32 botanical families. This number reflects the wealth of medicinal plants that are still traditionally used. To gather as much information on the use of plants, a series of ethnobotanical surveys were conducted in the field during periods of picking from villagers, herbalists and traditional healers. According to those surveyed, the fresh leaves and seeds are considered the most popular and common parts that can address several diseases where oral and dermal administration are recommended. The most used plants are: Artemisia herba-alba, Argyrolobium saharae, Gymnosporia senegalensis, Ormenis africana, Pallenis spinosa, Thymus ciliatus, Pistacia atlantica, Paronychia arabica, Globularia alypum, Ajuga iva, Peganum harmala, Ruta chalepensis, Tapsia garganica, Pituranthos scoparius. Djebel Zdimm offers floristic diversity and a sizeable traditional therapeutic knowledge. The safeguarding and preservation of this ancestral heritage is one of our objectives in this semi-arid steppe. -
Literaturverzeichnis
Literaturverzeichnis Abaimov, A.P., 2010: Geographical Distribution and Ackerly, D.D., 2009: Evolution, origin and age of Genetics of Siberian Larch Species. In Osawa, A., line ages in the Californian and Mediterranean flo- Zyryanova, O.A., Matsuura, Y., Kajimoto, T. & ras. Journal of Biogeography 36, 1221–1233. Wein, R.W. (eds.), Permafrost Ecosystems. Sibe- Acocks, J.P.H., 1988: Veld Types of South Africa. 3rd rian Larch Forests. Ecological Studies 209, 41–58. Edition. Botanical Research Institute, Pretoria, Abbadie, L., Gignoux, J., Le Roux, X. & Lepage, M. 146 pp. (eds.), 2006: Lamto. Structure, Functioning, and Adam, P., 1990: Saltmarsh Ecology. Cambridge Uni- Dynamics of a Savanna Ecosystem. Ecological Stu- versity Press. Cambridge, 461 pp. dies 179, 415 pp. Adam, P., 1994: Australian Rainforests. Oxford Bio- Abbott, R.J. & Brochmann, C., 2003: History and geography Series No. 6 (Oxford University Press), evolution of the arctic flora: in the footsteps of Eric 308 pp. Hultén. Molecular Ecology 12, 299–313. Adam, P., 1994: Saltmarsh and mangrove. In Groves, Abbott, R.J. & Comes, H.P., 2004: Evolution in the R.H. (ed.), Australian Vegetation. 2nd Edition. Arctic: a phylogeographic analysis of the circu- Cambridge University Press, Melbourne, pp. marctic plant Saxifraga oppositifolia (Purple Saxi- 395–435. frage). New Phytologist 161, 211–224. Adame, M.F., Neil, D., Wright, S.F. & Lovelock, C.E., Abbott, R.J., Chapman, H.M., Crawford, R.M.M. & 2010: Sedimentation within and among mangrove Forbes, D.G., 1995: Molecular diversity and deri- forests along a gradient of geomorphological set- vations of populations of Silene acaulis and Saxi- tings. -
Assessment of Plant Species Diversity Associated with the Carob Tree (Ceratonia Siliqua, Fabaceae) at the Mediterranean Scale
Plant Ecology and Evolution 151 (2): 185–193, 2018 https://doi.org/10.5091/plecevo.2018.1423 REGULAR PAPER Assessment of plant species diversity associated with the carob tree (Ceratonia siliqua, Fabaceae) at the Mediterranean scale Alex Baumel1,*, Pascal Mirleau1, Juan Viruel2, Magda Bou Dagher Kharrat3, Stefano La Malfa4, Lahcen Ouahmane5, Katia Diadema6, Marwa Moakhar1, Hervé Sanguin7 & Frédéric Médail1 1Institut Méditerranéen de Biodiversité et d’Ecologie marine et continentale (IMBE) [IMBE is sponsored by Aix Marseille University, Avignon University, CNRS and IRD], Station marine d’Endoume, Chemin de la Batterie des Lions, FR-13007 Marseille, France 2Royal Botanic Gardens, Kew, Richmond, Surrey, TW9 3DS, United Kingdom 3Université Saint-Joseph, Faculté des sciences, Laboratoire Caractérisation Génomique des Plantes, B.P. 11-514 Riad El Solh, Beyrouth 1107 2050, Lebanon 4Università degli Studi di Catania, Dipartimento di Agricoltura, Alimentazione e Ambiente (Di3A) Via Valdisavoia 5 – IT-95123 Catania, Italy 5Université Cadi Ayyad Marrakech, Faculté des Sciences Semlalia, Laboratoire d’Ecologie et Environnement, Morocco 6Conservatoire Botanique National Méditerranéen de Porquerolles (CBNMed), 34 avenue Gambetta, FR-83400 Hyères, France 7Laboratoire des Symbioses Tropicales et Méditerranéennes (LSTM) [LSTM is sponsored by Univ Montpellier, CIRAD, IRD, INRA, Montpellier SupAgro], TA A-82/J Campus International de Baillarguet FR-34398 Montpellier cedex 5, France *Author for correspondence: [email protected] Background and aims – The thermophilous woodlands of the Mediterranean region constitute reservoirs of genetic resources for several fruit trees. Among them, the carob tree (Ceratonia siliqua) is a key component of traditional Mediterranean agroecosystems but its ecology was never assessed at the scale of its whole distribution area. -
Scrub and Grassland
Scrub and grassland CORINE BIOTOPES MANUAL 49 -.-../._---------------------------- 3 SCRUB AND GRASSLAND 31 Healh and scrub 1111 31 Heath and scrub Temperate shrubby areas: Atlantic and alpine heaths, subalpine bush and taH herb communities, deciduous forest recoloniza I tion, hedgerows, dwarf conifers. WETHEATHS Ericion tetralicis; Ulicion minoris p.; Genistion mfcranl/to-anglícae p. Humid, peaty or semi-peaty heaths (other than blanket bogs). (Lebrun el al., 1949; ElIenberg, 1963; Depasse el al., 1970; Géhu, 1973; Westhoff and den Held, 1975; Noirfalise and Vanesse, 1976; De Sloover el al., 1978; Rivas-Martinez, 1979; Gimingham el al., 1979; Bournérias, 1979; Noirfalise et al., 1980; de Smidt, 1981; Polunin I and Walters, 1985) I NORTHERN WET HEATHS Wet heaths with Erica tetralbe and sphagnums. I SOUTHERN WET HEATHS I \Vet heaths with Erica tetralix and E. ciliaris and sphagnums. PURPLE MOORGRASS WET HEATHS Degraded facies of wet heaths, dominated by lv/alinia caerulea. DRYHEATHS Calluno~Ulicetea Mesophile or xerophile heaths on siliceous, podsolic soils in moist Atlantic and sub·Atlantic cIimates of plains and low mountains. (Gimingham, 1972; Géhu, 1973; NoirfaIise and Vanesse, 1976; Gimingham et al., 1979; Bournérias, 1979; Noirfalise el al., 1980; Ratcliffe, 1980; Polunin and Walters, 1985; Webb, 1986) SUBMüNTANE VACCINIUM HEATHS Calluna-Genistion pi/asae p.; Vaccinion vitis-idaeae p. Heaths rich in Vaccinium spp., usuaIly with Calluna vulgaris, of the northern and western British Isles, the Hercynian ranges and the lower levels of the Alps, the pyrenees and the Cordillera Cantabrica. (Lebrun el al., 1949; ElIenberg, 1963; Schumacker, 1973; Noirfalise and Vanesse, 1976; De Sloover el al., 1978; Rivas-Martinez, 1979; Gimingham el al., 1979; Noirfalise el al., 1980; l Ratcliffe, 1980; Webb, 1986; Noirfalise, 1987; Salomez, in litt. -
Foreign Exploration and Host Specificity Testing of Biological
FOREIGN EXPL ORATION & HOST SPECIFICIT Y TESTING OF BIOLOGICAL CO NTROL AGENTS OF FRENCH BROOM IN CALIFORNIA INTERNATIONAL BROOM INITIATIVE PROJECT 2001-2002 Andy Sheppard Principal Scientist Foreign Exploration & Host Specificity Testing of Biological Control Agents of French Broom in California Final Report 31 January 2002 Andy Sheppard1 Thierry Thomann2 & Sylvie Agret2 1 CSIRO Entomology, GPO Box, 1700 Canberra ACT 2601 2 CSIRO European laboratory, Campus International de Baillarguet, 34980 Montferrier-sur-Lez, France. Executive summary This is the final report on work carried out for the biological control of French broom in California by Commonwealth Scientific and Industrial Research Organisation at its European Laboratory in France in collaboration with the USDA European Biological Control Laboratory. Survey trips have been completed to Tunisia, southern Spain and western Portugal. Available resources limited a full suite of planned trips. Morocco and eastern Mediterranean Turkey are the only countries that still need to be surveyed. A recent study of the taxonomy of Genista suggests Morocco is the key region for undiscovered potential biocontrol agents. Analysis of the results of previous trips is presented including validation of the sampling regime and the impacts of seed feeding insects on the seed production of French broom and close relatives. Insect biology and culture development studies have been completed for the psyllid Arytinnis hakani. This species was found to have 5 nymphal instars and be multi-voltine with a 40-45 day generation time, passing the hot summer months as early instar nymphs. Lepidapion argentatum specificity and taxonomic status is unclear from current literature but a PhD project based around this group has recently obtained funding. -
EGU2014-8360-1, 2014 EGU General Assembly 2014 © Author(S) 2014
Geophysical Research Abstracts Vol. 16, EGU2014-8360-1, 2014 EGU General Assembly 2014 © Author(s) 2014. CC Attribution 3.0 License. Primary succession on slopes exposed to intense erosion: the case of Vesuvius Grand Cone Adriano Stinca, Giovanni Battista Chirico, and Giuliano Bonanomi Università di Napoli, Dipartimento di Agraria, Portici (NA), Italy ([email protected]) Mt. Vesuvius (1281 m a.s.l.) is an active volcano dominating the central part of the Campania Region coastline, with a distinctive barren crater summit, known as Grand Cone, formed during the eruption of AD 79. Local envi- ronmental factors hindered the colonization of the Vesuvius Grand Cone by vascular plants after the last eruptions of 1906 and 1944. The Grand Cone exhibits very steep planar slopes (33-35 degrees), covered by unconsolidated pyroclastic deposits, mainly formed by lapilli and gravels, characterized by an extremely low water holding ca- pacity and very low organic matter and nitrogen contents, and exposed to intense water and wind erosion. In the last decade Genista aetnensis (Biv.) DC. (Fabaceae), has been expanding over the Grand Cone, facilitating the colonization by other species, especially herbaceous, with a dramatic change of the landscape appearance of the Vesuvius Grand Cone. G. aetnensis is a plant endemic of Mt. Etna and Eastern Sardinia and was firstly introduced at the base of Mt. Vesuvius within reforestation programs after the eruption of 1906. This plant is a nitrogen fixing species with a strong ability to colonize andosols, much more pronounced than the indigenous brooms (Cytisus scoparius and Spartium junceum). An intensive investigation has been conducted to explore the eco-hydrological processes driving the vegetation dynamics observed on the slopes of Grand Cone. -
Seed Propagation of Mediterranean Trees and Shrubs SEED PROPAGATION of MEDITERRANEAN TREES and SHRUBS
APAT Agency for the protection of the environment and for technical services Seed propagation of mediterranean trees and shrubs SEED PROPAGATION OF MEDITERRANEAN TREES AND SHRUBS Legal Information The Agency for the protection of the environment and for technical services nor any person or company acting on the behalf of the Agency is responsible for the use that may be made of the information contained in this report. APAT - Agency for the protection of the environment and for technical services Via Vitaliano Brancati, 48 - 00144 Roma - Italy A great deal of information is available on the Internet. It can be accessed through the Italian server (www.apat.it) © APAT ISBN 88-448-0081-0 May be reproduced citing the source Graphic Layout Layout: Franco Iozzoli, APAT Cover: Paolo Orlandi, APAT Printing Co-ordination APAT Printed in Italy by I.G.E.R. srl - Viale C. T. Odescalchi, 67/A - 00147 Roma Printed on ecological paper Printing completed in April 2003 AUTORI The present publication is the translation of Chapter 12 of the ANPA Handbook ‘Propagation of Mediterranean trees and shrubs from seed’ (Propagazione per seme di alberi e arbusti della flora mediterranea). Beti Piotto and Anna Di Noi Editors, 2001 CONTENTS Contents ACKNOWLEDGMENTS 1 PREFACE 3 G. Cesari INTRODUCTION 5 B. Piotto 1. WHY PROPAGATE TREES AND SHRUBS OF THE MEDITERRANEAN FLORA FROM SEED B. Piotto, A. Di Noi 7 2. TREES AND SHRUBS WITHIN THE MEDITERRANEAN ENVIRONMENT: SUBDIVISION ACCORDING TO MORPHOLOGICAL CHARACTERISTICS AND TO TEMPERATURE ZONES B. Piotto, A. Di Noi 9 2.1. Subdivision according to morphological characteristics 9 2.2. -
Contribution to the Floristic and Ethnobotanic Study of the Most
ARTICLES Mediterranean Botany ISSNe 2603-9109 https://doi.org/10.5209/mbot.64567 Contribution to the floristic and ethnobotanic study of the most utilized medicinal plants in the Sétifian Tell (south of the Tamentout forest) east Algeria KarimaYaici1, Saliha Dahamna1 & MohamedToumi2 Received: 11 September 2018 / Accepted: 24 January 2020 /Published online: 6 March 2020 Abstract. This study aims to know the natural heritage of the Tamentout forest through a floristic inventory made in several cantons and to evaluate the uses of traditional medicine in the Sétifian Tell, by conducting an ethnobotanical study at the level of several localities in the region. A quantitative and qualitative analysis of the listed flora identified 101 plant species, which are divided into 38 families and 97 genera. An important representation of the Asteraceae (19%), Fabaceae and Lamiaceae families (11%) are noted. The floristic study emphasizes the presence of several biological types, with a codominance of hemicryptophytes (with 42%) and therophytes (31%). The Mediterranean floristic element constitutes the most important chorological ensemble (52%). The ethnobotanical survey was conducted among 82 informants, with a total of 290 questionnaire cards. All the results were processed by statistical processing software: Excel 2007 and IBM SPSS Statistics version 23. These results showed that the leaves are the most used part (43%) and that the methods of use are prepared in the form of infusion (25%), poultices (18%), and decoction (11%). The most common forms of use are herbal tea (46%), powder (25%), and essential oil (19%). The oral route is the most widely used route of administration (51%). The most common pathologies are those of the digestive system (20%) and the respiratory system (18%).