Tree Invasions: Patterns, Processes, Challenges and Opportunities
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Technical Guidelines for Reforestation at Ex-Coal-Mining Areas
Technical Guidelines for Reforestation at Ex-Coal-Mining Areas - Based on the outcomes of experimental reforestation activities at ex-coal-mining areas in South Kalimantan, Indonesia - Japan International Forestry Promotion and Cooperation Center (JIFPRO) March 2015 Technical Guidelines for Reforestation at Ex-Coal-Mining Areas - Based on the outcomes of experimental reforestation activities at ex-coal-mining areas in South Kalimantan, Indonesia - Eiichiro Nakama, Seiichi Ohta, Yasuo Ohsumi, Tokunori Mori and Satohiko Sasaki Japan International Forestry Promotion and Cooperation Center Fakhrur Razie, Hamdani Fauzi and Mahrus Aryadi Lambung Mangkurat University, Indonesia Japan International Forestry Promotion and Cooperation Center March 2015 Foreword During the past decades, deforestation and forest degradation continues especially in developing countries. According to the report of the Food and Agriculture Organization of the United Nation (FAO), approximately 13 million hectors of global forests have been lost annually due to forest land conversion to other land uses, forest fires and natural disasters, while reforestation and natural regeneration account for an increase of approx. 7.8 million hectors of forest cover. This means the net loss of global forest is estimated at 5.2 million hectors. Adverse impacts of forest conversion to farmland can be minimized as far as the land is properly used and managed in a sustainable manner. However, in some cases, problem soils are exposed and abandoned as degraded land. Deforestation by mining is a big issue these years. Problem soils such as strong acid soils and/or too much heavy metal soils appear at the ex-mining areas. In some cases it is too difficult to reforestate. -
Falcataria Moluccana Molucca Albizia Fabaceae
Falcataria moluccana Molucca albizia Fabaceae Forest Starr, Kim Starr, and Lloyd Loope United States Geological Survey--Biological Resources Division Haleakala Field Station, Maui, Hawai'i January, 2003 OVERVIEW Falcataria moluccana has been widely planted throughout the world for ornament and reforestation. It was first introduced to Hawai'i in 1917 by Joseph Rock (Little and Skolmen 1989). In Hawai'i, F. moluccana has been planted by the hundreds of thousands for ornament and reforestation. Trees are attractive and the wood is useful for a variety of things from furniture making to canoe building. However, trees are spreading from initial plantings to adjacent pastures, forests, and disturbed areas. Because of its widespread distribution throughout the state coupled with its popularity, perhaps the best approach currently would be to control the tree in certain sites where it is not wanted, such as natural areas, pastures, and farmland. Seeds tend to fall nearby and trees do not disperse over a long distance (miles), except when people move the tree to a new area. If this dispersal trend were to change, such as if a vector to spread the trees further arrived or if it was planted again on a grand scale to new areas, the tree may become a bigger problem. TAXONOMY Family: Fabaceae (pea family) (Wagner et al. 1999). Latin name: Falcataria moluccana (Miq.) Barneby and Grimes (Herbarium Pacificum Staff 1998). Synonyms: Paraserianthes falcataria (L.) I. Nielsen (Wagner et al. 1999), Albizia falcataria (L.) Fosberg, A. falcata (L.) Backer (Little and Skolmen 1989). Common names: Molucca albizia (Little and Skolmen 1989). Taxonomic notes: There seems to be a lot of name changing and rearranging that has occurred within this complex. -
Invasive Alien Species in Protected Areas
INVASIVE ALIEN SPECIES AND PROTECTED AREAS A SCOPING REPORT Produced for the World Bank as a contribution to the Global Invasive Species Programme (GISP) March 2007 PART I SCOPING THE SCALE AND NATURE OF INVASIVE ALIEN SPECIES THREATS TO PROTECTED AREAS, IMPEDIMENTS TO IAS MANAGEMENT AND MEANS TO ADDRESS THOSE IMPEDIMENTS. Produced by Maj De Poorter (Invasive Species Specialist Group of the Species Survival Commission of IUCN - The World Conservation Union) with additional material by Syama Pagad (Invasive Species Specialist Group of the Species Survival Commission of IUCN - The World Conservation Union) and Mohammed Irfan Ullah (Ashoka Trust for Research in Ecology and the Environment, Bangalore, India, [email protected]) Disclaimer: the designation of geographical entities in this report does not imply the expression of any opinion whatsoever on the part of IUCN, ISSG, GISP (or its Partners) or the World Bank, concerning the legal status of any country, territory or area, or of its authorities, or concerning the delineation of its frontiers or boundaries. 1 CONTENTS ACKNOWLEDGEMENTS...........................................................................................4 EXECUTIVE SUMMARY ...........................................................................................6 GLOSSARY ..................................................................................................................9 1 INTRODUCTION ...................................................................................................12 1.1 Invasive alien -
Synoptic Overview of Exotic Acacia, Senegalia and Vachellia (Caesalpinioideae, Mimosoid Clade, Fabaceae) in Egypt
plants Article Synoptic Overview of Exotic Acacia, Senegalia and Vachellia (Caesalpinioideae, Mimosoid Clade, Fabaceae) in Egypt Rania A. Hassan * and Rim S. Hamdy Botany and Microbiology Department, Faculty of Science, Cairo University, Giza 12613, Egypt; [email protected] * Correspondence: [email protected] Abstract: For the first time, an updated checklist of Acacia, Senegalia and Vachellia species in Egypt is provided, focusing on the exotic species. Taking into consideration the retypification of genus Acacia ratified at the Melbourne International Botanical Congress (IBC, 2011), a process of reclassification has taken place worldwide in recent years. The review of Acacia and its segregates in Egypt became necessary in light of the available information cited in classical works during the last century. In Egypt, various taxa formerly placed in Acacia s.l., have been transferred to Acacia s.s., Acaciella, Senegalia, Parasenegalia and Vachellia. The present study is a contribution towards clarifying the nomenclatural status of all recorded species of Acacia and its segregate genera. This study recorded 144 taxa (125 species and 19 infraspecific taxa). Only 14 taxa (four species and 10 infraspecific taxa) are indigenous to Egypt (included now under Senegalia and Vachellia). The other 130 taxa had been introduced to Egypt during the last century. Out of the 130 taxa, 79 taxa have been recorded in literature. The focus of this study is the remaining 51 exotic taxa that have been traced as living species in Egyptian gardens or as herbarium specimens in Egyptian herbaria. The studied exotic taxa are accommodated under Acacia s.s. (24 taxa), Senegalia (14 taxa) and Vachellia (13 taxa). -
Volume-Based Nutrient Content of Acacia Mangium, Eucalyptus Deglupta Paraserianthesd an Falcataria Industrian I L Tree Plantation Easn Si T Kalimantan, Indonesia
512 Journal of Tropical Forest Science 13 (3): 512-526 (2001) VOLUME-BASED NUTRIENT CONTENT OF ACACIA MANGIUM, EUCALYPTUS DEGLUPTA PARASERIANTHESD AN FALCATARIA INDUSTRIAN I L TREE PLANTATION EASN SI T KALIMANTAN, INDONESIA J. Mackensen, Institut of Soil Science and Forest Nutrition, University of Gottingen, Busgenweg 2, 37077 Gottingen, Germany D. Ruhiyat Faculty Forestry,of Mulawarman 1013,University,Box O. Samarinda,P. East Kalimantan, Indonesia & H. Folster* Institut of Soil Science and Forest Nutrition, University of Gottingen, Busgenweg2, 37077 Gottingen, Germany Received December 1999______________________________________________ MACKENSEN, J., RUHIYAT, D. & FOLSTER, H. 2001. Volume-based nutrient content of Acacia mangium, Eucalyptus deglupta and Paraserianthes falcataria in industrial tree plantation Easn si t Kalimantan, Indonesia. Nutrient concentrations in stemwood, stembark, branches and leaves of Acacia mangium, Eucalyptus deglupta and Paraserianthes falcataria were analysed and compared to results by other studies. Nutrient concentrations differed significantly across components. Species-specific differences were profound. The weight-volume ratio for A. mangium and E. deglupta was described best with an exponential model, while for P. falcataria a simple linear model was sufficient. All equations were highly significant (R2> 0.83). Stand nutrient storage in 200 m* ha'1 stemwood and stembark ranged between 75-202 kg N, 2.6-9.5 kg P . ,Nutrient 10-2d 73-20 85-16, an Mg K a g 1k C g 8 k g 1sk store n branchei d d san storagg M d eleavean a C , s29-164 d K amounte an e , th P f %d o 70-223an o dt N e th %f o in stems. -
Important Notice Regarding the Spread of Noxious Invasive Alien
Important notice regarding the spread of noxious invasive alien Stinkbean plants (Paraserianthes lophantha (Willd.), also known as the Australian Albizia, Plume Albizia or Mountain Albezia Stinkbean. (Paraserianthes lophantha (Willd.) Evergreen shrub or small tree, with bipinnate leaves and large, yellow-whitish spikes. Scientific name: Paraserianthes lophantha (Willd.) I.C. Nielsen Common names: plume albizia, mountain albizia Family: Fabaceae (Leguminosae) After more than a decade of hard work Noordhoek residents, with the help of various government and city departments, have managed to control extensive stands of invasive Rooikrans and Longleaf Wattle in and around the suburb, along with several other less common invasive species. Enter the Stinkbean. A common problem with managing invasive species is that once a primary invader is removed, secondary opportunistic invaders fill the vacant ecological niche. This is the case with the rapid spread of Stinkbean into Noordhoek. The plant is originally from the Perth area of Australia, which has a climate similar to ours making the region susceptible to invasion. Stinkbean is also invasive in Chile, the Canary Islands, Portugal, New Zealand and even parts of Australia. Sinkbean has spread rapidly here. These fast growing trees are often mistaken for Blackwood, common along the Garden Route and of similar appearance, with fine fronded leaves, varigated bark and attractive cream flowers. No guessing why they are called Stinkbean. The plant bears many seeds from its first year of growth. This is a primary reason to stop its spread in our neighbourhood. As the old saw goes, “one years seeding is ten years weeding.” In the case of stinkbean it can be significantly worse as the seeds are thought to remain viable many years, similar to Rooikrans and Wattle. -