The Ecology and Potential Factors Limiting the Success of Sable Antelope in South- Eastern Zimbabwe: Implications for Conservation
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The Miombo Woodlands of Central, Eastern and Southern Africa
90 The Miombo Woodlands of Central, Eastern and Southern Africa Philomena Tuite and John J. Gardiner Dept. of Crop Science, Horticulture and Forestry, University College Dublin, Belfield. Dublin 4. Summary Aspects of the environment and ecology of Miombo woodlands are described. Attention is given to the widespread nature of their distrihution area and the role played by Miombo at local and national levels. A matrix of woodland-use is presented. This offers some insight into changing resource-usc patterns in Miombo, and highlights the conflicts which may ensue with the adoption of certain woodland management strategies. Iutroduction In Africa, tropical dry forests and woodlands constitute between 70 - 80% of all forested land (Murphy & Lugo 1986). South of the Equator, (50 to 25 0 S) Miombo woodlands are the main dry for· est type in the continent, occupying an estimated area of 7 million square kilometres (Griffith 1961). Thus, Miombo represents one of the most widespread, yet compact forest types in the world. Almost 50% of the land area of both Tanzania and Zambia, and large tracts of Mozambique, Malawi, Zimbabwe, Zaire and Angola support Miombo (Fig. 1). This aereal distribution corresponds roughly to the Zambezian Floral Domain of White (1965), recognised for its floristic richness and the widespread occurrence of the tree genera Brachystegia, lulbernardia and Isoberlinia. Despite the widespread nature of this woodland type, its long history of exploitation and the increasing human·related pressure and needs within the countries mentioned, Miombo resource-use re mains largely undocumented. The data base on inventory, silviculture, IRISH FORESTRY, 1990. Vol. 47 (2)' 90·107 THE MIOMBO WOODLANDS 91 • I _. -
Conservation Biology and Controlling International Status of the African Wild Trade in Endangered Dog, Lycaon Pictus Species
U PDATE IncludingEndangered a Reprint Species of theTechnical latest USFWS Bulletin School of Natural Resources and Environment August 7994 Vol. 7 7 No. 70 THE UNIVERSITY OF MICHIGAN In this Issue Conservation Biology and Controlling International Status of the African Wild Trade in Endangered Dog, Lycaon pictus Species Resilience and Resistance: Old Growth Forests and the Relevance for Conservation Puerto Rican Parrot Biology and Management Conservation Biology and Status of the African wild dog, Lycaon pictus by - Joshua R, Ginsberg - The African wild dog (Lycaon Causes of Decline Loss of habitat and direct persecu- pictus) was once found from Senegal to tion by humans were probably respon- South Africa. Inhabiting a wide range of A number of explanations and hy- sible for initial declines and local extinc- ecosystems, from deserts to the alpine potheses have been invoked to explain tions. Morerecently, other factors which meadows of Mount Kilimanjaro (re- the pan-African decline in Lycaon num- may have led to local or regional de- viewed in Fanshawe et al. 1991 ; Ginsberg bers (Fanshawe et al. 1991). Wild dogs clines in numbers include competition andMacdonald 1990),Lycaon wasprob- occur at low densities relative to other with other carnivores (Frame 1986; ably found in all environments except large predators. For example, while Sinclair, in press); direct conflict with true rainforests. Well over a hundred lions frequently occur at densities of one humans (Childes 1988; Hines 1990; thousand wild dogs, or five times that lion per five square kilometers (Schaller Malcolm 1979); disease (Creel et al., in many, may have lived in Africa at the 1972), wild dog densities average one press; Burrows et al. -
Hippotragus Equinus – Roan Antelope
Hippotragus equinus – Roan Antelope authorities as there may be no significant genetic differences between the two. Many of the Roan Antelope in South Africa are H. e. cottoni or equinus x cottoni (especially on private properties). Assessment Rationale This charismatic antelope exists at low density within the assessment region, occurring in savannah woodlands and grasslands. Currently (2013–2014), there are an observed 333 individuals (210–233 mature) existing on nine formally protected areas within the natural distribution range. Adding privately protected subpopulations and an Cliff & Suretha Dorse estimated 0.8–5% of individuals on wildlife ranches that may be considered wild and free-roaming, yields a total mature population of 218–294 individuals. Most private Regional Red List status (2016) Endangered subpopulations are intensively bred and/or kept in camps C2a(i)+D*†‡ to exclude predators and to facilitate healthcare. Field National Red List status (2004) Vulnerable D1 surveys are required to identify potentially eligible subpopulations that can be included in this assessment. Reasons for change Non-genuine: While there was an historical crash in Kruger National Park New information (KNP) of 90% between 1986 and 1993, the subpopulation Global Red List status (2008) Least Concern has since stabilised at c. 50 individuals. Overall, over the past three generations (1990–2015), based on available TOPS listing (NEMBA) Vulnerable data for nine formally protected areas, there has been a CITES listing None net population reduction of c. 23%, which indicates an ongoing decline but not as severe as the historical Endemic Edge of Range reduction. Further long-term data are needed to more *Watch-list Data †Watch-list Threat ‡Conservation Dependent accurately estimate the national population trend. -
Animals of Africa
Silver 49 Bronze 26 Gold 59 Copper 17 Animals of Africa _______________________________________________Diamond 80 PYGMY ANTELOPES Klipspringer Common oribi Haggard oribi Gold 59 Bronze 26 Silver 49 Copper 17 Bronze 26 Silver 49 Gold 61 Copper 17 Diamond 80 Diamond 80 Steenbok 1 234 5 _______________________________________________ _______________________________________________ Cape grysbok BIG CATS LECHWE, KOB, PUKU Sharpe grysbok African lion 1 2 2 2 Common lechwe Livingstone suni African leopard***** Kafue Flats lechwe East African suni African cheetah***** _______________________________________________ Red lechwe Royal antelope SMALL CATS & AFRICAN CIVET Black lechwe Bates pygmy antelope Serval Nile lechwe 1 1 2 2 4 _______________________________________________ Caracal 2 White-eared kob DIK-DIKS African wild cat Uganda kob Salt dik-dik African golden cat CentralAfrican kob Harar dik-dik 1 2 2 African civet _______________________________________________ Western kob (Buffon) Guenther dik-dik HYENAS Puku Kirk dik-dik Spotted hyena 1 1 1 _______________________________________________ Damara dik-dik REEDBUCKS & RHEBOK Brown hyena Phillips dik-dik Common reedbuck _______________________________________________ _______________________________________________African striped hyena Eastern bohor reedbuck BUSH DUIKERS THICK-SKINNED GAME Abyssinian bohor reedbuck Southern bush duiker _______________________________________________African elephant 1 1 1 Sudan bohor reedbuck Angolan bush duiker (closed) 1 122 2 Black rhinoceros** *** Nigerian -
Using Natural Fertilizers in Miombo Woodlands by Emmanuel Chidumayo
ISSUES 'IN AFRICAN BIODIVERSITY THE BIODIVERSITY SUPPORT PROGRAM IYwmber 2, May 1999 Using Natural Fertilizers in Miombo Woodlands By Emmanuel Chidumayo Introduction Miombo woodlands grow on the ancient central African plateau and its escarpments. They form a swathe across the continent from Angola to Mozambique, and extend from lhnzania and southern Congo in the north, to Zimbabwe in the south. Scientists distin- guish miombo from other savanna woodland and forest formations by the presence of legume trees belonging to the genera Brachustegia, Julbernardia, and Isoberlinia. The climate in the miombo zone is subhumid, characterized by a short seasonal rainfall rang- ing from 650 mm to 1,400 mm, occurring from November to March, and a long dry sea- son (April to October/November). Miombo is divided with the wetter type (with > 1,000 mm of rainfall) occurring in the north, and drier type (with < 1,000 mm) (White 1983) occurring in the south of the miombo zone. Miombo occurs on geologically old and acidic (pH 4-6) soils with low fertility. A charac- teristic association between miombo tree species and ectomycorrhizal fungi significantly increases mineral uptake from the soil. There is higher species diversity in miombo woodlands and associated wetlands or dambos than, for example, acacia woodlands. Miombo is of outstanding international importance for the conservation of plants and birds, many of whichare endemic to the region. It provides seasonal habitat for two large, spectacular antelope in Africa, the roan and sable. Miombo trees are typically highly resilient to the annual fires that sweep across the region, and resprout rapidly after anthropogenic disturbance; however, woodland regeneration can be stalled or prevented if trees are uprooted and the connection with ectomycorrhiza is disturbed. -
Miombo Ecoregion Vision Report
MIOMBO ECOREGION VISION REPORT Jonathan Timberlake & Emmanuel Chidumayo December 2001 (published 2011) Occasional Publications in Biodiversity No. 20 WWF - SARPO MIOMBO ECOREGION VISION REPORT 2001 (revised August 2011) by Jonathan Timberlake & Emmanuel Chidumayo Occasional Publications in Biodiversity No. 20 Biodiversity Foundation for Africa P.O. Box FM730, Famona, Bulawayo, Zimbabwe PREFACE The Miombo Ecoregion Vision Report was commissioned in 2001 by the Southern Africa Regional Programme Office of the World Wide Fund for Nature (WWF SARPO). It represented the culmination of an ecoregion reconnaissance process led by Bruce Byers (see Byers 2001a, 2001b), followed by an ecoregion-scale mapping process of taxa and areas of interest or importance for various ecological and bio-physical parameters. The report was then used as a basis for more detailed discussions during a series of national workshops held across the region in the early part of 2002. The main purpose of the reconnaissance and visioning process was to initially outline the bio-physical extent and properties of the so-called Miombo Ecoregion (in practice, a collection of smaller previously described ecoregions), to identify the main areas of potential conservation interest and to identify appropriate activities and areas for conservation action. The outline and some features of the Miombo Ecoregion (later termed the Miombo– Mopane Ecoregion by Conservation International, or the Miombo–Mopane Woodlands and Grasslands) are often mentioned (e.g. Burgess et al. 2004). However, apart from two booklets (WWF SARPO 2001, 2003), few details or justifications are publically available, although a modified outline can be found in Frost, Timberlake & Chidumayo (2002). Over the years numerous requests have been made to use and refer to the original document and maps, which had only very restricted distribution. -
CBD First National Report
Coordinated by: Francisco Mabjaia, Permanent Secretary, for the Coordination of Environmental Affairs (MICOA) and Felicidade Munguambe, National Biodiversity Programme Coordinator, (MICOA) Edited by: John (IMPACT0 Lda.) and Felicidade Munguambe (MICOA) With contributions from: Arlito Cuco (National Directorate of Forestry and Wildlife DNFFB); Calane da Silva (National Herbarium); Paulino Munisse (National Herbarium); Dulcinea Baquete (MICOA) Alfonso (DNFFB); Carlos (Natural History Museum); Helena Motta (MICOA); (MICOA); Hermes Pacule (Fisheries Research Institute); (Department of Biological Sciences, Eduardo Mondlane University, EMU); and John (IMPACT0 Lda.) Diagrams: Viriato Chiconele (Department of Biological Science, EMU) Published by: IMPACT0 This publication was made possible by the financial support of the Global Environmental Facility and the United Nations Environmental Programme Ministry for the Coordination of Environmental Affairs, Mozambique, 1997 EXECUTIVESUMMARY The National on the Conservation Marromeu complex, the Chimanimani of Biological Diversity in Mozambique has and the Maputaland Centre of been prepared in accordance with Article 26 Endemism, of the Convention of which Parties to prepare periodic Since the signing of the Peace Accord in reports measures taken to implement 1992 and the consolidation of peace CBD provisions and fhe effectiveness of the country new and challenging such measures. The Report covers opportunities now exist for na resource implementation activities carried out scientists gather primary -
Transboundary Species Project
TRANSBOUNDARY SPECIES PROJECT ROAN, SABLE AND TSESSEBE Rowan B. Martin Species Report for Roan, Sable and Tsessebe in support of The Transboundary Mammal Project of the Ministry of Environment and Tourism, Namibia facilitated by The Namibia Nature Foundation and World Wildlife Fund Living in a Finite Environment (LIFE) Programme Cover picture adapted from the illustrations by Clare Abbott in The Mammals of the Southern African Subregion by Reay H.N. Smithers Published by the University of Pretoria Republic of South Africa 1983 Transboundary Species Project – Background Study Roan, Sable and Tsessebe CONTENTS 1. BIOLOGICAL INFORMATION ...................................... 1 a. Taxonomy ..................................................... 1 b. Physical description .............................................. 3 c. Habitat ....................................................... 6 d. Reproduction and Population Dynamics ............................. 12 e. Distribution ................................................... 14 f. Numbers ..................................................... 24 g. Behaviour .................................................... 38 h. Limiting Factors ............................................... 40 2. SIGNIFICANCE OF THE THREE SPECIES ........................... 43 a. Conservation Significance ........................................ 43 b. Economic Significance ........................................... 44 3. STAKEHOLDING ................................................. 48 a. Stakeholders ................................................. -
Trade in Endangered Species Order 2011
Reprint as at 14 September 2014 Trade in Endangered Species Order 2011 (SR 2011/369) Trade in Endangered Species Order 2011: revoked, on 14 September 2014, by clause 4 of the Trade in Endangered Species Order 2014 (LI 2014/259). Jerry Mateparae, Governor-General Order in Council At Wellington this 10th day of October 2011 Present: His Excellency the Governor-General in Council Pursuant to section 53 of the Trade in Endangered Species Act 1989, His Excellency the Governor-General, acting on the advice and with the consent of the Executive Council, makes the following order. Contents Page 1 Title 2 2 Commencement 2 Note Changes authorised by subpart 2 of Part 2 of the Legislation Act 2012 have been made in this official reprint. Note 4 at the end of this reprint provides a list of the amendments incorporated. This order is administered by the Department of Conservation. 1 Reprinted as at cl 1 Trade in Endangered Species Order 2011 14 September 2014 3 New Schedules 1, 2, and 3 substituted in Trade in 2 Endangered Species Act 1989 4 Revocation 2 Schedule 3 New Schedules 1, 2, and 3 substituted in Trade in Endangered Species Act 1989 Order 1 Title This order is the Trade in Endangered Species Order 2011. 2 Commencement This order comes into force on the 28th day after the date of its notification in the Gazette. 3 New Schedules 1, 2, and 3 substituted in Trade in Endangered Species Act 1989 The Trade in Endangered Species Act 1989 is amended by revoking Schedules 1, 2, and 3 and substituting the schedules set out in the Schedule of this order. -
Chapter 15 the Mammals of Angola
Chapter 15 The Mammals of Angola Pedro Beja, Pedro Vaz Pinto, Luís Veríssimo, Elena Bersacola, Ezequiel Fabiano, Jorge M. Palmeirim, Ara Monadjem, Pedro Monterroso, Magdalena S. Svensson, and Peter John Taylor Abstract Scientific investigations on the mammals of Angola started over 150 years ago, but information remains scarce and scattered, with only one recent published account. Here we provide a synthesis of the mammals of Angola based on a thorough survey of primary and grey literature, as well as recent unpublished records. We present a short history of mammal research, and provide brief information on each species known to occur in the country. Particular attention is given to endemic and near endemic species. We also provide a zoogeographic outline and information on the conservation of Angolan mammals. We found confirmed records for 291 native species, most of which from the orders Rodentia (85), Chiroptera (73), Carnivora (39), and Cetartiodactyla (33). There is a large number of endemic and near endemic species, most of which are rodents or bats. The large diversity of species is favoured by the wide P. Beja (*) CIBIO-InBIO, Centro de Investigação em Biodiversidade e Recursos Genéticos, Universidade do Porto, Vairão, Portugal CEABN-InBio, Centro de Ecologia Aplicada “Professor Baeta Neves”, Instituto Superior de Agronomia, Universidade de Lisboa, Lisboa, Portugal e-mail: [email protected] P. Vaz Pinto Fundação Kissama, Luanda, Angola CIBIO-InBIO, Centro de Investigação em Biodiversidade e Recursos Genéticos, Universidade do Porto, Campus de Vairão, Vairão, Portugal e-mail: [email protected] L. Veríssimo Fundação Kissama, Luanda, Angola e-mail: [email protected] E. -
Understanding the Behavioural Trade-Offs Made by Blue Wildebeest (Connochaetes Taurinus): the Importance of Resources, Predation and the Landscape
Understanding the behavioural trade-offs made by blue wildebeest (Connochaetes taurinus): the importance of resources, predation and the landscape Rebecca Dannock Bachelor of Science (Hons) in Zoology A thesis submitted for the degree of Doctor of Philosophy at The University of Queensland in 2016 School of Biological Sciences Abstract Prey individuals must constantly make decisions regarding safety and resource acquisition to ensure that they acquire enough resources without being predated upon. These decisions result in a trade-off between resource acquisition behaviours (such as foraging and drinking) and safety behaviours (such as grouping and vigilance). This trade- off is likely to be affected by the social and environmental factors that an individual experiences, including the individual’s location in the landscape. The overall objective of my PhD was to understand the decisions a migratory ungulate makes in order to acquire enough resources, while not becoming prey, and to understand how these decisions are influenced by social and environmental factors. In order to do this, I studied the behaviour of blue wildebeest (Connochaetes taurinus) in Etosha National Park, Namibia, between 2013 and 2015. I studied wildebeests’ behaviour while they acquired food and water and moved within the landscape. Along with observational studies, I also used lion (Panthera leo) roar playbacks to experimentally manipulate perceived predator presence to test wildebeests’ responses to immediate predation risk. For Chapter 2 I studied the foraging-vigilance trade-off of wildebeest to determine how social and environmental factors, including the location within the landscape, were correlated with wildebeests’ time spent foraging and vigilant as well as their bite rate. -
Sustainable Management of Miombo Woodlands
Sustainable management of Miombo woodlands Food security, nutrition and wood energy Sustainable management of Miombo woodlands Food security, nutrition and wood energy This paper was prepared by Davison J. Gumbo from CIFOR Zambia and Marc Dumas-Johansen, Giulia Muir, Fritjof Boerstler and Zuzhang Xia from FAO. FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS Rome, 2018 Recommended citation: Gumbo, D.J., Dumas-Johansen, M., Muir, G., Boerstler, F., Xia, Z. 2018. Sustainable management of Miombo woodlands – Food security, nutrition and wood energy. Rome, Food and Agriculture Organization of the United Nations. The designations employed and the presentation of material in this information product do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations (FAO) concerning the legal or development status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The mention of specific companies or products of manufacturers, whether or not these have been patented, does not imply that these have been endorsed or recommended by FAO in preference to others of a similar nature that are not mentioned. The views expressed in this information product are those of the author(s) and do not necessarily reflect the views or policies of FAO. ISBN 978-92-5-130423-5 © FAO, 2018 FAO encourages the use, reproduction and dissemination of material in this information product. Except where otherwise indicated, material may be copied, downloaded and printed for private study, research and teaching purposes, or for use in non-commercial products or services, provided that appropriate acknowledgement of FAO as the source and copyright holder is given and that FAO’s endorsement of users’ views, products or services is not implied in any way.