25 Years On: a Look at Endangered Species
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Projet De Motion Sur La Dégradation De
WCC-2012-Res-023-EN Support for national and regional initiatives for the conservation of large mammals in the Sahara RECOGNIZING IUCN’s mission, since its creation, to promote the conservation of biodiversity; AWARE that desert ecosystems and their biodiversity are particularly vulnerable to natural and anthropogenic climate change; RECOGNIZING that the Sahara is very rich in biodiversity, which is often underestimated and is potentially important in the provision of ecosystem services and genetic resources; RECOGNIZING that the populations of large mammals have declined dramatically in desert ecosystems, and in the Sahara in particular; ALARMED that all eight species of Saharan ungulates as well as their subspecies are either threatened with extinction or already extinct, the Bubal Hartebeest (Alcelaphus buselaphus buselaphus) is classified as Extinct, the Scimitar-horned Oryx (Oryx dammah) is Extinct in the Wild and six others are classified as Endangered or Critically Endangered; RECOGNIZING that the African Lion (Panthera leo leo) and the African Wild Dog (Lycaon pictus) have been exterminated from the Sahara and that the Northwest African cheetah (Acinonyx jubatus hecki) is classified as Critically Endangered; AWARE that three of the large mammal species living in the desert require vast ranges in order to survive; NOTING that desert ecosystems have attracted very little interest or support from the global conservation community, despite covering over 17% of the world’s biomass and containing a high level of biodiversity, including -
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. -
Confirming the Pleistocene Age of the Qurta Rock
EGYPTIAN ARCHAEOLOGY Confirming the Pleistocene age of the Qurta rock art An article in EA 33 made the case for the existence of Pleistocene rock art at Qurta, c.15km north of Kom Ombo. Further fieldwork and laboratory analyses during 2008-09 have proved its pre- Holocene age as Dirk Huyge and Dimitri A G Vandenberghe discuss. The circumstances of the finding of the Qurta rock art in 2005 were described in our 2008 report in EA 33 (pp.25- 28). At Qurta, on the east bank of the Nile between Edfu and Aswan, three rock art sites have been identified: Qurta I, II and III (henceforth QI, QII and QIII). They are located in higher parts of the Nubian sandstone scarp bordering the Nile floodplain. At each site several rock art locations, panels and individual figures have been identified, with a total of at least 185 distinct images. Naturalistically drawn aurochs (Bos primigenius ) are predominant (over 75% of the total number of drawings), View of Qurta II showing the location of rock art panel QII.4.2, which is partly covered by Nubian sandstone rock debris and sediment accumulations followed by birds, hippopotami, gazelle, fish and hartebeest. In addition, some indeterminate During the 2008 field campaign, it became clear that creatures and several highly-stylized representations of rock art panel QII.4.2 was partly covered by sediment human figures appear at the sites. On the basis of the accumulations that were trapped between the engraved intrinsic characteristics of the rock art, its patination and rock face and coarse Nubian sandstone rock debris degree of weathering, as well as the archaeological and that had become separated from the scarp. -
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. -
Gazella Dorcas) in North East Libya
The conservation ecology of the Dorcas gazelle (Gazella dorcas) in North East Libya Walid Algadafi A thesis submitted in partial fulfilment of the requirements of the University of Wolverhampton for the degree of Doctor of Philosophy April 2019 This work and any part thereof has not previously been presented in any form to the University or to any other body whether for the purposes of assessment, publication or any other purpose (unless previously indicated). Save for any express acknowledgements, references and/or bibliographies cited in the work, I confirm that the intellectual content of the work is the result of my own efforts and of no other person. The right of Walid Algadafi to be identified as author of this work is asserted in accordance with ss.77 and 78 of the Copyright, Designs and Patents Act 1988. At this date, copyright is owned by the author. Signature: Date: 27/ 04/ 2019 I ABSTRACT The Dorcas gazelle (Gazella dorcas) is an endangered antelope in North Africa whose range is now restricted to a few small populations in arid, semi-desert conditions. To be effective, conservation efforts require fundamental information about the species, especially its abundance, distribution and genetic factors. Prior to this study, there was a paucity of such data relating to the Dorcas gazelle in Libya and the original contribution of this study is to begin to fill this gap. The aim of this study is to develop strategies for the conservation management of Dorcas gazelle in post-conflict North East Libya. In order to achieve this aim, five objectives relating to current population status, threats to the species, population genetics, conservation and strategic population management were identified. -
Dry Season Browsing by Sable Antelope in Northern Botswana
Notes and records Dry season browsing by sable antelope in Methods northern Botswana The study area was located on the northern edge of the Michael C. Hensman*, Norman Owen-Smith, Francesca Okavango Delta in Botswana. An adult female sable in Parrini and Barend F.N. Erasmus each of three herds was fitted with a GPS collar to facilitate Animal, Plant, and Environmental Sciences, The University of observations. When the herd being observed from a vehicle the Witwatersrand, Private Bag 3, Wits, 2050, South Africa was foraging, we selected the closest female and watched her feeding from 10 to 50 m away. Beginning on any tenth minute of the hour, we recorded whether this animal Introduction was browsing, grazing or performing other activities on every tenth second over a minute (n = 879 1-min The late dry season is a crucial period for grazing observations). Records were pooled within each morning ungulates because the nutritional value of the remaining and afternoon observation session so that these sessions brown grass is lowest then and levels of crude protein and represented independent samples (n = 113 ranging in digestible organic matter may fall below the maintenance duration from 3 to 13 min). Following initial observations requirements of herbivores (Owen-Smith, 1982). During of browsing in late 2009, records representing early wet this adverse period, mixed feeders like impala (Aepyceros season conditions were collected from December 2009 melampus) increase the proportion of browse in the form of through January 2010 (n = 46), mid-dry season condi- the leaves of the woody plants they consume (Owen-Smith tions through August–September 2010 (n = 36), and late & Cooper, 1985). -
African Animals Extinct in the Holocene
SNo Common Name\Scientific Name Extinction Date Range Mammals Prehistoric extinctions (beginning of the Holocene to 1500 AD) Atlas Wild Ass 1 300 North Africa Equus africanus atlanticus Canary Islands Giant Rats 2 Before 1500 AD. Spain (Canary Islands) Canariomys bravoi and Canariomys tamarani Giant Aye-aye 3 1000 AD. Madgascar Daubentonia robusta Giant Fossa 4 Unknown Madgascar Cryptoprocta spelea 5 Hipposideros besaoka 10000 BC. Madgascar Homotherium 6 10000 BC. Africa Homotherium sp. Koala Lemur 7 1420 AD. Madagascar Megaladapis sp. Lava Mouse 8 Before 1500 Spain (Canary Islands) Malpaisomys insularis Malagasy Aardvark 9 200 BC Madagascar Plesiorycteropus sp. Malagasy Hippopotamus 10 1000 AD. Madgascar Hippopotamus sp. Megalotragus 11 10000 BC. Africa Megalotragus sp. North African Elephant 12 300 AD. North Africa Loxodonta africana pharaoensis Pelorovis 13 2000 BC. Africa Pelorovis sp. Sivatherium 14 6000 BC. Africa Sivatherium sp. Recent Extinctions (1500 to present) Atlas Bear 1 1870s North Africa Ursus arctos crowtheri Aurochs Unknown (Africa), 2 North Africa Bos primigenius 1627(Europe) Bluebuck 3 1799 South Africa Hippotragus leucophaeus Bubal Hartebeest 4 1923 North Africa Alcelaphus buselaphus buselaphus Cape Lion 5 1860 South Africa Panthera leo melanochaitus Cape Serval 6 Unknown South Africa Leptailurus serval serval Cape Warthog 7 1900 South Africa Phacochoerus aethiopicus aethiopicus Kenya Oribi 8 Unknown Kenya Ourebia ourebi kenyae Large Sloth Lemur 9 1500s Madagascar Palaeopropithecus sp. Lesser Mascarene Flying Fox 10 -
GNUSLETTER Vol 37#2.Pdf
GNUSLETTER Volume 37 / Number 2 December 2020 ANTELOPE SPECIALIST GROUP IUCN Species Survival Commission Antelope Specialist Group GNUSLETTER is the biannual newsletter of the IUCN Species Survival Commission Antelope Specialist Group (ASG). First published in 1982 by first ASG Chair Richard D. Estes, the intent of GNUSLETTER, then and today, is the dissemination of reports and information regarding antelopes and their conservation. ASG Members are an important network of individuals and experts working across disciplines throughout Africa, Asia and America. Contributions (original articles, field notes, other material relevant to antelope biology, ecology, and conservation) are welcomed and should be sent to the editor. Today GNUSLETTER is published in English in electronic form and distributed widely to members and non-members, and to the IUCN SSC global conservation network. To be added to the distribution list please contact [email protected]. GNUSLETTER Editorial Board - David Mallon, ASG Co-Chair - Philippe Chardonnet, ASG Co-Chair ASG Program Office - Tania Gilbert, Marwell Wildife The Antelope Specialist Group Program Office is hosted and supported by Marwell Wildlife https://www.marwell.org.uk The designation of geographical entities in this report does not imply the expression of any opinion on the part of IUCN, the Species Survival Commission, or the Antelope Specialist Group concerning the legal status of any country, territory or area, or concerning the delimitation of any frontiers or boundaries. Views expressed in GNUSLETTER are those of the individual authors, Cover photo: Young female bushbuck (Tragelaphus scriptus), W National Park and Biosphere Reserve, Niger (© Daniel Cornélis) 2 GNUSLETTER Volume 37 Number 2 December 2020 FROM IUCN AND ASG………………………………………………………. -
Trade in Endangered Species Order 2008
2008/39 Trade in Endangered Species Order 2008 Anand Satyanand, GovernorGeneral Order in Council At Wellington this 25th day of February 2008 Present: His Excellency the GovernorGeneral in Council Pursuant to section 53 of the Trade in Endangered Species Act 1989, His Excellency the GovernorGeneral, acting on the advice and with the consent of the Executive Council, makes the following order. Contents Page 1 Title 2 2 Commencement 2 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 1 cl 1 Trade in Endangered Species Order 2008 2008/39 Order 1 Title This order is the Trade in Endangered Species Order 2008. 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. 4 Revocation The Trade in Endangered Species Order 2005 (SR 2005/93) is revoked. 2 2008/39 Schedule cl 3 New Schedules 1, 2, and 3 substituted in Trade in Endangered Species Act 1989 Schedule 1 s 3(1) Species endangered by trade T rade The classes, families, and species listed in this schedule are arranged in descending order by class then in alphabetical order by order, family, and species. -
The Gazelle in Ancient Egyptian Art Image and Meaning
Uppsala Studies in Egyptology - 6 - Department of Archaeology and Ancient History Uppsala University For my parents Dorrit and Hindrik Åsa Strandberg The Gazelle in Ancient Egyptian Art Image and Meaning Uppsala 2009 Dissertation presented at Uppsala University to be publicly examined in the Auditorium Minus of the Museum Gustavianum, Uppsala, Friday, October 2, 2009 at 09:15 for the degree of Doctor of Philosophy. The examination will be conducted in English. Abstract Strandberg, Åsa. 2009. The Gazelle in Ancient Egyptian Art. Image and Meaning. Uppsala Studies in Egyptology 6. 262 pages, 83 figures. Published by the Department of Archaeology and Ancient History, Uppsala University. xviii +262 pp. ISSN 1650-9838, ISBN 978-91-506-2091-7. This thesis establishes the basic images of the gazelle in ancient Egyptian art and their meaning. A chronological overview of the categories of material featuring gazelle images is presented as a background to an interpretation. An introduction and review of the characteristics of the gazelle in the wild are presented in Chapters 1-2. The images of gazelle in the Predynastic material are reviewed in Chapter 3, identifying the desert hunt as the main setting for gazelle imagery. Chapter 4 reviews the images of the gazelle in the desert hunt scenes from tombs and temples. The majority of the motifs characteristic for the gazelle are found in this context. Chapter 5 gives a typological analysis of the images of the gazelle from offering processions scenes. In this material the image of the nursing gazelle is given particular importance. Similar images are also found on objects, where symbolic connotations can be discerned (Chapter 6). -
Gazella Dorcas and Gazella Leptoceros) in Egypt
Contemporary status and distribution of gazelle species (Gazella dorcas and Gazella leptoceros) in Egypt by Husam El Alqamy and Sherif Baha El Din Abstract. Only two gazelle species are currently present in a wild state in Egypt. These are Dor- cas Gazelle (Gazella dorcas) and Slender-horned Gazelle (Gazella leptoceros). The latest infor- mation available about the status and distribution of these two species collected during the period 1997–2005 indicates that the population size and range of both species continue to shrink at dif- ferent rates. The conservation status of the two species is reviewed and a quantitative estimation for the range of the two species is provided using IUCN’s Area of Occurrence and Area of Occu- pancy guidelines. Kurzfassung. Gegenwärtig kommen in Ägypten in freier Wildbahn nur noch zwei Gazellenarten vor: die Dorkasgazelle (Gazella dorcas) und die Dünengazelle (Gazella leptoceros). Neue Infor- mationen aus den Jahren 1997–2005 über den Status und die Verbreitung zeigen, dass sowohl die Populationen beider Arten als auch die Größe ihres Verbreitungsgebietes in unterschiedlicher Ge- schwindigkeit weiter abnehmen. Der Schutzstatus beider Arten wird dargestellt und eine quantita- tive Analyse des Vorkommensgebietes anhand der von IUCN entwickelten Richtlinien „Area of Occurrence“ und „Area of Occupancy“ wird vorgenommen. Keywords. Antelopes, gazelles, range, conservation status, distribution, Area of Occurrence, Area of Occupancy. Introduction Except for the Mediterranean littoral belt and a few mountain peaks, the Egyptian deserts are classified as hyper-arid deserts receiving less than 100 mm of annual precipitation (AYAD & GHABOUR 1986). These deserts are therefore of very low productivity and many animal populations, especially large mammals, have to cover large distances in the pursuit of fa- vourable habitats and feeding grounds.