Climate and Biodiversity (2015)
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This Keyword List Contains Indian Ocean Place Names of Coral Reefs, Islands, Bays and Other Geographic Features in a Hierarchical Structure
CoRIS Place Keyword Thesaurus by Ocean - 8/9/2016 Indian Ocean This keyword list contains Indian Ocean place names of coral reefs, islands, bays and other geographic features in a hierarchical structure. For example, the first name on the list - Bird Islet - is part of the Addu Atoll, which is in the Indian Ocean. The leading label - OCEAN BASIN - indicates this list is organized according to ocean, sea, and geographic names rather than country place names. The list is sorted alphabetically. The same names are available from “Place Keywords by Country/Territory - Indian Ocean” but sorted by country and territory name. Each place name is followed by a unique identifier enclosed in parentheses. The identifier is made up of the latitude and longitude in whole degrees of the place location, followed by a four digit number. The number is used to uniquely identify multiple places that are located at the same latitude and longitude. For example, the first place name “Bird Islet” has a unique identifier of “00S073E0013”. From that we see that Bird Islet is located at 00 degrees south (S) and 073 degrees east (E). It is place number 0013 at that latitude and longitude. (Note: some long lines wrapped, placing the unique identifier on the following line.) This is a reformatted version of a list that was obtained from ReefBase. OCEAN BASIN > Indian Ocean OCEAN BASIN > Indian Ocean > Addu Atoll > Bird Islet (00S073E0013) OCEAN BASIN > Indian Ocean > Addu Atoll > Bushy Islet (00S073E0014) OCEAN BASIN > Indian Ocean > Addu Atoll > Fedu Island (00S073E0008) -
Biodiversity and Ecology of Afromontane Rainforests with Wild Coffea Arabica L
Feyera Senbeta Wakjira (Autor) Biodiversity and ecology of Afromontane rainforests with wild Coffea arabica L. populations in Ethiopia https://cuvillier.de/de/shop/publications/2260 Copyright: Cuvillier Verlag, Inhaberin Annette Jentzsch-Cuvillier, Nonnenstieg 8, 37075 Göttingen, Germany Telefon: +49 (0)551 54724-0, E-Mail: [email protected], Website: https://cuvillier.de General introduction 1 GENERAL INTRODUCTION 1.1 Background The term biodiversity is used to convey the total number, variety and variability of living organisms and the ecological complexes in which they occur (Wilson 1988; CBD 1992; Rosenzweig 1995). The concept of biological diversity can be applied to a wide range of spatial and organization scales, including genetics, species, community, and landscape scales (Noss 1990; Austin et al. 1996; Tuomisto et al. 2003). It is becoming increasingly apparent that knowledge of the role of patterns and processes that determine diversity at different scales is at the very heart of an understanding of variation in biodiversity. Processes influencing diversity operate at different spatial and temporal scales (Rosenzweig 1995; Gaston 2000). A variety of environmental events and processes, including past evolutionary development, biogeographic processes, extinctions, and current influences govern the biodiversity of a particular site (Brown and Lomolino 1998; Gaston 2000; Ricklefs and Miller 2000). Biodiversity is valued and has been studied largely because it is used, and could be used better, to sustain and improve human well-being (WWF 1993; WCMC 1994). However, there has been a rapid decline in the biodiversity of the world during the past two to three decades (Wilson 1988; Whitmore and Sayer 1992; Lugo et al. -
Tulbagh Renosterveld Project Report
BP TULBAGH RENOSTERVELD PROJECT Introduction The Cape Floristic Region (CFR) is the smallest and richest floral kingdom of the world. In an area of approximately 90 000km² there are over 9 000 plant species found (Goldblatt & Manning 2000). The CFR is recognized as one of the 33 global biodiversity hotspots (Myers, 1990) and has recently received World Heritage Status. In 2002 the Cape Action Plan for the Environment (CAPE) programme identified the lowlands of the CFR as 100% irreplaceable, meaning that to achieve conservation targets all lowland fragments would have to be conserved and no further loss of habitat should be allowed. Renosterveld , an asteraceous shrubland that predominantly occurs in the lowland areas of the CFR, is the most threatened vegetation type in South Africa . Only five percent of this highly fragmented vegetation type still remains (Von Hase et al 2003). Most of these Renosterveld fragments occur on privately owned land making it the least represented vegetation type in the South African Protected Areas network. More importantly, because of the fragmented nature of Renosterveld it has a high proportion of plants that are threatened with extinction. The Custodians of Rare and Endangered Wildflowers (CREW) project, which works with civil society groups in the CFR to update information on threatened plants, has identified the Tulbagh valley as a high priority for conservation action. This is due to the relatively large amount of Renosterveld that remains in the valley and the high amount of plant endemism. The CAPE program has also identified areas in need of fine scale plans and the Tulbagh area falls within one of these: The Upper Breede River planning domain. -
The Rarest and Least Protected Forests in Biodiversity Hotspots
Biodivers Conserv DOI 10.1007/s10531-012-0384-1 ORIGINAL PAPER The rarest and least protected forests in biodiversity hotspots Thomas W. Gillespie • Boris Lipkin • Lauren Sullivan • David R. Benowitz • Stephanie Pau • Gunnar Keppel Received: 20 March 2012 / Accepted: 4 October 2012 Ó Springer Science+Business Media Dordrecht 2012 Abstract The goal of biodiversity hotspots is to identify regions around the world where conservation priorities should be focused. We undertake a geographic information system and remote sensing analysis to identify the rarest and least protected forests in biodiversity hotspots. World Wildlife Fund ecoregions with terrestrial forest were subset from 34 biodiversity hotspots and forest cover calculated from GlobCover data at a 300 m pixel resolution. There were 276 ecoregions in 32 biodiversity hotspots classified as containing terrestrial forests. When the first quartile of forest ecoregions was subset based on smallest extent of forest cover in protected areas, there were 69 rare forests identified within 20 biodiversity hotspots. Most rare forest ecoregions (45) occurred on islands or island archipelagos and 47 rare forest ecoregions contained less than 10 % forest cover in pro- tected areas. San Fe´lix-San Ambrosio Islands Temperate Forests, Tubuai Tropical Moist Forests, Maldives-Lakshadweep-Chagos Archipelago Tropical Moist Forests, and Yap Electronic supplementary material The online version of this article (doi:10.1007/s10531-012-0384-1) contains supplementary material, which is available to authorized users. T. W. Gillespie (&) Á B. Lipkin Á L. Sullivan Á D. R. Benowitz Department of Geography, University of California Los Angeles, Los Angeles, CA 90095-1524, USA e-mail: [email protected] B. -
Global Ecological Forest Classification and Forest Protected Area Gap Analysis
United Nations Environment Programme World Conservation Monitoring Centre Global Ecological Forest Classification and Forest Protected Area Gap Analysis Analyses and recommendations in view of the 10% target for forest protection under the Convention on Biological Diversity (CBD) 2nd revised edition, January 2009 Global Ecological Forest Classification and Forest Protected Area Gap Analysis Analyses and recommendations in view of the 10% target for forest protection under the Convention on Biological Diversity (CBD) Report prepared by: United Nations Environment Programme World Conservation Monitoring Centre (UNEP-WCMC) World Wide Fund for Nature (WWF) Network World Resources Institute (WRI) Institute of Forest and Environmental Policy (IFP) University of Freiburg Freiburg University Press 2nd revised edition, January 2009 The United Nations Environment Programme World Conservation Monitoring Centre (UNEP- WCMC) is the biodiversity assessment and policy implementation arm of the United Nations Environment Programme (UNEP), the world's foremost intergovernmental environmental organization. The Centre has been in operation since 1989, combining scientific research with practical policy advice. UNEP-WCMC provides objective, scientifically rigorous products and services to help decision makers recognize the value of biodiversity and apply this knowledge to all that they do. Its core business is managing data about ecosystems and biodiversity, interpreting and analysing that data to provide assessments and policy analysis, and making the results -
Land and Maritime Connectivity Project: Road Component Initial
Land and Maritime Connectivity Project (RRP SOL 53421-001) Initial Environmental Examination Project No. 53421-001 Status: Draft Date: August 2020 Solomon Islands: Land and Maritime Connectivity Project – Multitranche Financing Facility Road Component Prepared by Ministry of Infrastructure Development This initial environmental examination is a document of the borrower. The views expressed herein do not necessarily represent those of the ADB’s Board of Directors, Management, or staff, and may be preliminary in nature. In preparing any country program or strategy, financing any project, or by making any designation of or reference to any particular territory or geographic area in this document, the Asian Development Bank does not intend to make any judgments as to the legal or other status of any territory or area. Solomon Islands: Land and Maritime Connectivity Project Road Component – Initial Environmental Examination Table of Contents Abbreviations iv Executive Summary v 1 Introduction 1 1.1 Background to the Project 1 1.2 Scope of the Environmental Assessment 5 2 Legal and Institutional Framework 6 2.1 Legal and Planning Framework 6 2.1.1 Country safeguard system 6 2.1.2 Other legislation supporting the CSS 7 2.1.3 Procedures for implementing the CSS 9 2.2 National Strategy and Plans 10 2.3 Safeguard Policy Statement 11 3 Description of the Subprojects 12 3.1 Location and Existing Conditions – SP-R1 12 3.1.1 Existing alignment 12 3.1.2 Identified issues and constraints 14 3.2 Location and Existing Conditions – SP-R5 15 3.2.1 Location -
Zoologische Verhandelingen
Corals of the South-west Indian Ocean: VI. The Alcyonacea (Octocorallia) of Mozambique, with a discussion on soft coral distribution on south equatorial East African reefs Y. Benayahu, A. Shlagman & M.H. Schleyer Benayahu, Y., A. Shlagman & M.H. Schleyer. Corals of the South-west Indian Ocean: VI. The Alcyo- nacea (Octocorallia) of Mozambique, with a discussion on soft coral distribution on south equatorial East African reefs. Zool. Verh. Leiden 345, 31.x.2003: 49-57, fig. 1.— ISSN 0024-1652/ISBN 90-73239-89-3. Y. Benayahu & A. Shlagman. Department of Zoology, George S. Wise Faculty of Life Sciences, Tel Aviv University, Ramat Aviv 69978, Israel (e-mail: [email protected]). M.H. Schleyer. Oceanographic Research Institute, P.O. Box 10712, Marine Parade 4056, Durban, South Africa. Key words: Mozambique; East African reefs; Octocorallia; Alcyonacea. A list of 46 species of Alcyonacea is presented for the coral reefs of the Segundas Archipelago and north- wards in Mozambique, as well as a zoogeographical record for the Bazaruto Archipelago in southern Mozambique. Among the 12 genera listed, Rhytisma, Lemnalia and Briareum were recorded on Mozambi- can reefs for the first time and the study yielded 27 new zoogeographical records. The survey brings the number of soft coral species listed for Mozambique to a total of 53. A latitudinal pattern in soft coral diversity along the south equatorial East African coast is presented, with 46 species recorded in Tanza- nia, 46 along the northern coast of Mozambique, dropping to 29 in the Bazaruto Archipelago in southern Mozambique and rising again to 38 along the KwaZulu-Natal coast in South Africa. -
Climate Forcing of Tree Growth in Dry Afromontane Forest Fragments of Northern Ethiopia: Evidence from Multi-Species Responses Zenebe Girmay Siyum1,2* , J
Siyum et al. Forest Ecosystems (2019) 6:15 https://doi.org/10.1186/s40663-019-0178-y RESEARCH Open Access Climate forcing of tree growth in dry Afromontane forest fragments of Northern Ethiopia: evidence from multi-species responses Zenebe Girmay Siyum1,2* , J. O. Ayoade3, M. A. Onilude4 and Motuma Tolera Feyissa2 Abstract Background: Climate-induced challenge remains a growing concern in the dry tropics, threatening carbon sink potential of tropical dry forests. Hence, understanding their responses to the changing climate is of high priority to facilitate sustainable management of the remnant dry forests. In this study, we examined the long-term climate- growth relations of main tree species in the remnant dry Afromontane forests in northern Ethiopia. The aim of this study was to assess the dendrochronological potential of selected dry Afromontane tree species and to study the influence of climatic variables (temperature and rainfall) on radial growth. It was hypothesized that there are potential tree species with discernible annual growth rings owing to the uni-modality of rainfall in the region. Ring width measurements were based on increment core samples and stem discs collected from a total of 106 trees belonging to three tree species (Juniperus procera, Olea europaea subsp. cuspidate and Podocarpus falcatus). The collected samples were prepared, crossdated, and analyzed using standard dendrochronological methods. The formation of annual growth rings of the study species was verified based on successful crossdatability and by correlating tree-ring widths with rainfall. Results: The results showed that all the sampled tree species form distinct growth boundaries though differences in the distinctiveness were observed among the species. -
Lesotho Fourth National Report on Implementation of Convention on Biological Diversity
Lesotho Fourth National Report On Implementation of Convention on Biological Diversity December 2009 LIST OF ABBREVIATIONS AND ACRONYMS ADB African Development Bank CBD Convention on Biological Diversity CCF Community Conservation Forum CITES Convention on International Trade in Endangered Species CMBSL Conserving Mountain Biodiversity in Southern Lesotho COP Conference of Parties CPA Cattle Post Areas DANCED Danish Cooperation for Environment and Development DDT Di-nitro Di-phenyl Trichloroethane EA Environmental Assessment EIA Environmental Impact Assessment EMP Environmental Management Plan ERMA Environmental Resources Management Area EMPR Environmental Management for Poverty Reduction EPAP Environmental Policy and Action Plan EU Environmental Unit (s) GA Grazing Associations GCM Global Circulation Model GEF Global Environment Facility GMO Genetically Modified Organism (s) HIV/AIDS Human Immuno Virus/Acquired Immuno-Deficiency Syndrome HNRRIEP Highlands Natural Resources and Rural Income Enhancement Project IGP Income Generation Project (s) IUCN International Union for Conservation of Nature and Natural Resources LHDA Lesotho Highlands Development Authority LMO Living Modified Organism (s) Masl Meters above sea level MDTP Maloti-Drakensberg Transfrontier Conservation and Development Project MEAs Multi-lateral Environmental Agreements MOU Memorandum Of Understanding MRA Managed Resource Area NAP National Action Plan NBF National Biosafety Framework NBSAP National Biodiversity Strategy and Action Plan NEAP National Environmental Action -
Comparative Wood Anatomy of Afromontane and Bushveld Species from Swaziland, Southern Africa
IAWA Bulletin n.s., Vol. 11 (4), 1990: 319-336 COMPARATIVE WOOD ANATOMY OF AFROMONTANE AND BUSHVELD SPECIES FROM SWAZILAND, SOUTHERN AFRICA by J. A. B. Prior 1 and P. E. Gasson 2 1 Department of Biology, Imperial College of Science, Technology & Medicine, London SW7 2BB, U.K. and 2Jodrell Laboratory, Royal Botanic Gardens, Kew, Richmond, Surrey, TW9 3DS, U.K. Summary The habit, specific gravity and wood anat of the archaeological research, uses all the omy of 43 Afromontane and 50 Bushveld well preserved, qualitative anatomical charac species from Swaziland are compared, using ters apparent in the charred modem samples qualitative features from SEM photographs in an anatomical comparison between the of charred samples. Woods with solitary ves two selected assemblages of trees and shrubs sels, scalariform perforation plates and fibres growing in areas of contrasting floristic com with distinctly bordered pits are more com position. Some of the woods are described in mon in the Afromontane species, whereas Kromhout (1975), others are of little com homocellular rays and prismatic crystals of mercial importance and have not previously calcium oxalate are more common in woods been investigated. Few ecological trends in from the Bushveld. wood anatomical features have previously Key words: Swaziland, Afromontane, Bush been published for southern Africa. veld, archaeological charcoal, SEM, eco The site of Sibebe Hill in northwest Swazi logical anatomy. land (26° 15' S, 31° 10' E) (Price Williams 1981), lies at an altitude of 1400 m, amidst a Introduction dramatic series of granite domes in the Afro Swaziland, one of the smallest African montane forest belt (White 1978). -
A New Map of Standardized Terrestrial Ecosystems of Africa
Major contributors to this publication include: The Association of American Geographers is a nonprofit scientific and educational society with a membership of over 10,500 individuals from more than 60 countries. AAG members are geographers and related professionals who work in the public, private, and academic sectors to advance the theory, methods, and practice of geography. This booklet is published by AAG as a special supplement to the African Geographical Review. The U.S. Geological Survey (USGS) was created in 1879 as a science agency charged with providing information and understanding to help resolve complex natural resource problems across the nation and around the world. The mission of the USGS is to provide relevant, impartial scientific information to 1) describe and understand the Earth, 2) minimize loss of life and property from natural disasters, 3) manage water, biological, energy, and mineral resources, and 4) enhance and protect our quality of life. NatureServe is an international conservation nonprofit dedicated to providing the sci- entific basis for effective conservation action. NatureServe’s network in the Americas includes more than 80 member institutions that collect and maintain a unique body of scientific knowledge about the species and ecosystems. The information products, data management tools, and biodiversity expertise that NatureServe’s scientists, technologists, and other professionals provide help meet local, national, and global conservation needs. The Regional Centre for Mapping of Resources for Development (RCMRD) was es- tablished in Nairobi, Kenya in 1975 to provide quality Geo-Information and allied Information Technology products and services in environmental and resource manage- ment for sustainable development in our member countries and beyond. -
Human Population Reduction Is Not a Quick Fix for Environmental Problems
Human population reduction is not a quick fix for environmental problems Corey J. A. Bradshaw1 and Barry W. Brook The Environment Institute and School of Earth and Environmental Sciences, The University of Adelaide, Adelaide, SA 5005, Australia Edited by Paul R. Ehrlich, Stanford University, Stanford, CA, and approved September 15, 2014 (received for review June 5, 2014) The inexorable demographic momentum of the global human of Earth’s human population because resource demands and population is rapidly eroding Earth’s life-support system. There are living space increase with population size, and proportional consequently more frequent calls to address environmental prob- ecological damage increases even when consumption patterns lems by advocating further reductions in human fertility. To exam- stabilize (22, 23); it is therefore essential that scenarios for future ine how quickly this could lead to a smaller human population, we human population dynamics are explored critically if we are to used scenario-based matrix modeling to project the global popula- plan for a healthy future society (24). tion to the year 2100. Assuming a continuation of current trends in There have been repeated calls for rapid action to reduce the mortality reduction, even a rapid transition to a worldwide one- world population humanely over the coming decades to centuries child policy leads to a population similar to today’s by 2100. Even (1, 3), with lay proponents complaining that sustainability a catastrophic mass mortality event of 2 billion deaths over a hypo- advocates ignore the “elephant in the room” of human over- st thetical 5-y window in the mid-21 century would still yield around population (25, 26).