Baseline and Impact Assessment: Proposed Chloorkop Landfill Expansion
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Sour Paspalum
Sour Paspalum - Tropical Weed or Forage? ALAN A. BEETLE Bissinda (Gabon), bitter grass (Philippines), camalote de antena (Mexico), canamazo (Cuba), cafiamazo hembro (Cuba), Highlight: Where carpetgraSs (Axonopus compressus) will cafiamazo amargo (Cuba), capim amargoso (Brazil), capim grow, sour paspalum (Paspalum conjugatum) has no place and marreca (Brazil), capim papuao (Brazil), carabao grass (Phil- is probably a sign of poor management. However, in areas of ippines), cintillo (Peru), co dang (Indochina), calapi (Philip- poor or sour soils, in shade and in times of drought, sour pas- pines), djuba-gov6 (Gabon), &inga (Gabon), gamalote (Costa palum comes into its own throughout the tropics as a valuable Rica), ge’singa (Gabon), gisinga (Gabon), grama de antena component of the total forage resource. Paspalum is a rather large genus “numbering nearly 400” species (Chase, 1929). Sour paspalum (Paspalum conjugatum) stands by itself in this genus as suggested by Chase (1929) who created for it, alone, the Section Conjugata (Fig. 1). Its most unusual character is the vigorously stoloniferous habit allowing, at times, for a rapidly formed perennial ground cover. Sour paspalum has been assumed to be native where it occurs in the Americas, from Florida to Texas and southward to Peru, Bolivia, and northern Argentina, from sea level to 4,000 ft elevation. The grass was first described from a specimen collected in Surinam (Dutch Guiana). Sour paspalum has been assumed, however, to be intro- duced wherever it occurs in the Old World tropics (Fig. 2) and Pacific Islands. The early trade routes were between Australia, Singapore, and Africa. Probably both carpetgrass (Axonopus compressus) and sour paspalum, being of similar distribution and ecology, were spread at the same time to the same places. -
Herpetofaunal Survey of the Ongeluksnek (Malekgalonyane) Nature Reserve in the Foothills of the Drakensberg, Eastern Cape Province, South Africa
Herpetology Notes, volume 13: 717-730 (2020) (published online on 25 August 2020) Herpetofaunal survey of the Ongeluksnek (Malekgalonyane) Nature Reserve in the foothills of the Drakensberg, Eastern Cape Province, South Africa Werner Conradie1,2,* Brian Reeves3, Sandile Mdoko3, Lwandiso Pamla3, and Oyama Gxabhu3 Abstract. The results of a herpetofaunal survey of Ongeluksnek Nature Reserve, Eastern Cape Province, South Africa are presented here. Combination of visual encounter survey methods and standard Y-shape trap arrays were used to conduct the survey. A total of 26 species (eight amphibians and 18 reptiles) were recorded, representing 29 quarter-degree grid cell records, of which 62% represented the first records for these units. Furthermore, we document the presence of three species of snakes (Crotaphopeltis hotamboeia, Hemachatus haemachatus and Homoroselaps lacteus) for the first time for the whole degree square of 3028 (approx. 100 km2). This study highlights the need to survey poorly known regions to enable us to understand and document the full distributional extent of species. We also discuss the impact of uncontrolled fires on the absence of grassland specialised species during our survey. Keywords. Amphibia, Reptilia, karroid, conservation, biodiversity, fire Introduction has been done in the southern and western regions (e.g. Branch and Braack, 1987), while the northern and The herpetofaunal richness of South Africa is central areas associated with the former homelands of considered to be amongst the highest in the world the Ciskei and Transkei remained poorly surveyed. In (Branch, 1998; Bates et al., 2014; Du Preez and recent years a series of rapid biodiversity studies has Carruthers, 2017; Tolley et al., 2019). -
Freshwater Fishes
WESTERN CAPE PROVINCE state oF BIODIVERSITY 2007 TABLE OF CONTENTS Chapter 1 Introduction 2 Chapter 2 Methods 17 Chapter 3 Freshwater fishes 18 Chapter 4 Amphibians 36 Chapter 5 Reptiles 55 Chapter 6 Mammals 75 Chapter 7 Avifauna 89 Chapter 8 Flora & Vegetation 112 Chapter 9 Land and Protected Areas 139 Chapter 10 Status of River Health 159 Cover page photographs by Andrew Turner (CapeNature), Roger Bills (SAIAB) & Wicus Leeuwner. ISBN 978-0-620-39289-1 SCIENTIFIC SERVICES 2 Western Cape Province State of Biodiversity 2007 CHAPTER 1 INTRODUCTION Andrew Turner [email protected] 1 “We live at a historic moment, a time in which the world’s biological diversity is being rapidly destroyed. The present geological period has more species than any other, yet the current rate of extinction of species is greater now than at any time in the past. Ecosystems and communities are being degraded and destroyed, and species are being driven to extinction. The species that persist are losing genetic variation as the number of individuals in populations shrinks, unique populations and subspecies are destroyed, and remaining populations become increasingly isolated from one another. The cause of this loss of biological diversity at all levels is the range of human activity that alters and destroys natural habitats to suit human needs.” (Primack, 2002). CapeNature launched its State of Biodiversity Programme (SoBP) to assess and monitor the state of biodiversity in the Western Cape in 1999. This programme delivered its first report in 2002 and these reports are updated every five years. The current report (2007) reports on the changes to the state of vertebrate biodiversity and land under conservation usage. -
Ecological Assessment for the Hlabisa Landfill Site
Ecological Assessment for the Hlabisa landfill site Compiled by: Ina Venter Pr.Sci.Nat Botanical Science (400048/08) M.Sc. Botany trading as Kyllinga Consulting 53 Oakley Street, Rayton, 1001 [email protected] In association with Lukas Niemand Pr.Sci.Nat (400095/06) M.Sc. Restoration Ecology / Zoology Pachnoda Consulting 88 Rubida Street, Murryfield x1, Pretoria [email protected] i Table of Contents 1. Introduction .................................................................................................................................... 1 1.1. Uncertainties and limitations .................................................................................................. 1 2. Site .................................................................................................................................................. 1 2.1. Location ................................................................................................................................... 1 2.2. Site description ....................................................................................................................... 1 3. Background information ................................................................................................................. 4 3.1. Vegetation ............................................................................................................................... 4 3.2. Centres of floristic endemism ................................................................................................ -
29 Figure8. the Limited Rank Hydrophilic Sedge and Grass Patches Within the Central Valley Bottom Wetland Provide Suitable Roost
Figure8. The limited rank hydrophilic sedge and grass patches within the central valley bottom wetland provide suitable roosting and foraging habitat for African Grass Owls. The high levels of human disturbances on the site including hunting with dogs; severely restricts the likelihood of any nests and limits potential roosting suitability. The annual burning of the site restricts the vegetative cover along the valley bottom wetland. Off-road bikes, quads and vehicle tracks transverse the entire site as well as helicopter training and landing on the site and open areas to the south of the site adjacent to the Waterval cemetery. African Grass Owls are found exclusively in rank grass, typically, although not only, at fair altitudes. Grass Owls are secretive and nomadic breeding in permanent and seasonal vleis, which it vacates while hunting or post-breeding, although it will breed in any area of long grass and it is not necessarily associated with wetlands. It marshlands it is usually outnumbered by the more common Marsh Owl (Asio capensis) 10:1 (Tarboton et al. 1987). Grass Owls nest on the ground within a system of tunnels constructed in mostly tall grass; peak-breeding activity (February- April) tends to coincide with maximum grass cover (Steyn 1982). Grass Owls specialise in large rodent prey, particularly Otomys vlei rats, although a wide range of rodent prey species, including Rhabdomys, Praomys, Mus, and Suncus, are taken (Earle 1978). Some local and nomadic movements in response to fluctuating food supplies, fire and the availability of suitable habitat can be expected (Steyn 1982). The ecological requirements of this species make it susceptible to many land-use changes impacting contemporary South Africa. -
VET-35: Staggers (Tremorgenic Syndrome)
University of Kentucky College of Agriculture, VET-35 Food and Environment Cooperative Extension Service Forage-Related Cattle Disorders Staggers (Tremorgenic Syndrome) Michelle Arnold, Veterinary Diagnostic Laboratory Table 1. Three main grass types associated with tremorgenic syndrome. “Staggers” is an all-inclusive term for a group of nervous system disorders Indole-diterpenoid Species caused by indole-diterpenoid mycotoxins Disease/Grass Affected Fungus Mycotoxins: “Tremorgens” Affected produced by various types of fungi on Perennial Ryegrass Staggers Neotyphodium lolii Lolitrem B Cattle, Sheep forages. These mycotoxins are collec- Grass: Lolium perenne Paxilline Horses, Llamas tively known as “tremorgens” (Table 1), Paspalum Staggers Claviceps paspali Paspalitrems A-C Cattle, Horses and they may be found in several types Grass: P. dilatatum (Dallisgrass) paspalinine Buffalo of grasses at varying stages of maturity. Grass: P. notatum (Bahiagrass) The three main grass types associated Bermudagrass Tremors Claviceps cynodontis Paspalitrems A & B Cattle, Horses with tremorgenic syndrome are Pas- Grass: Cynodon dactylon Paspaline palum spp. (dallisgrass and bahiagrass), paspalinine Cynodon dactylon (bermudagrass) and Lolium perenne (perennial ryegrass). Clinical signs are characterized by Regardless of fungal type, clinical • As the condition worsens, the animal tremors and incoordination that tend to signs of staggers are similar. may exhibit staggering, head shaking, worsen with excitement or movement. • When at rest, animals appear to move salivation, collapse and seizures or Cases of perennial ryegrass staggers and graze normally. other neurologic signs (opisthotonus, are most likely to occur when perennial • The earliest signs are head tremors nystagmus). Deaths rarely occur except ryegrass infected with the endophyte and muscle twitching (fasciculations) from accidental trauma or from conse- Neothyphodium lolii is grazed inten- of the neck and shoulders which later quences of being recumbent (downer). -
Biodiversity and Ecology of Critically Endangered, Rûens Silcrete Renosterveld in the Buffeljagsrivier Area, Swellendam
Biodiversity and Ecology of Critically Endangered, Rûens Silcrete Renosterveld in the Buffeljagsrivier area, Swellendam by Johannes Philippus Groenewald Thesis presented in fulfilment of the requirements for the degree of Masters in Science in Conservation Ecology in the Faculty of AgriSciences at Stellenbosch University Supervisor: Prof. Michael J. Samways Co-supervisor: Dr. Ruan Veldtman December 2014 Stellenbosch University http://scholar.sun.ac.za Declaration I hereby declare that the work contained in this thesis, for the degree of Master of Science in Conservation Ecology, is my own work that have not been previously published in full or in part at any other University. All work that are not my own, are acknowledge in the thesis. ___________________ Date: ____________ Groenewald J.P. Copyright © 2014 Stellenbosch University All rights reserved ii Stellenbosch University http://scholar.sun.ac.za Acknowledgements Firstly I want to thank my supervisor Prof. M. J. Samways for his guidance and patience through the years and my co-supervisor Dr. R. Veldtman for his help the past few years. This project would not have been possible without the help of Prof. H. Geertsema, who helped me with the identification of the Lepidoptera and other insect caught in the study area. Also want to thank Dr. K. Oberlander for the help with the identification of the Oxalis species found in the study area and Flora Cameron from CREW with the identification of some of the special plants growing in the area. I further express my gratitude to Dr. Odette Curtis from the Overberg Renosterveld Project, who helped with the identification of the rare species found in the study area as well as information about grazing and burning of Renosterveld. -
Volume 2. Animals
AC20 Doc. 8.5 Annex (English only/Seulement en anglais/Únicamente en inglés) REVIEW OF SIGNIFICANT TRADE ANALYSIS OF TRADE TRENDS WITH NOTES ON THE CONSERVATION STATUS OF SELECTED SPECIES Volume 2. Animals Prepared for the CITES Animals Committee, CITES Secretariat by the United Nations Environment Programme World Conservation Monitoring Centre JANUARY 2004 AC20 Doc. 8.5 – p. 3 Prepared and produced by: UNEP World Conservation Monitoring Centre, Cambridge, UK UNEP WORLD CONSERVATION MONITORING CENTRE (UNEP-WCMC) www.unep-wcmc.org The UNEP World Conservation Monitoring Centre is the biodiversity assessment and policy implementation arm of the United Nations Environment Programme, the world’s foremost intergovernmental environmental organisation. UNEP-WCMC aims to help decision-makers recognise the value of biodiversity to people everywhere, and to apply this knowledge to all that they do. The Centre’s challenge is to transform complex data into policy-relevant information, to build tools and systems for analysis and integration, and to support the needs of nations and the international community as they engage in joint programmes of action. UNEP-WCMC provides objective, scientifically rigorous products and services that include ecosystem assessments, support for implementation of environmental agreements, regional and global biodiversity information, research on threats and impacts, and development of future scenarios for the living world. Prepared for: The CITES Secretariat, Geneva A contribution to UNEP - The United Nations Environment Programme Printed by: UNEP World Conservation Monitoring Centre 219 Huntingdon Road, Cambridge CB3 0DL, UK © Copyright: UNEP World Conservation Monitoring Centre/CITES Secretariat The contents of this report do not necessarily reflect the views or policies of UNEP or contributory organisations. -
Reptiles and Amphibians of the Goegap Nature Reserve
their time underground in burrows. These amphibians often leave their burrows after heavy rains that are seldom. Reptiles And Amphibians Of The There are reptiles included in this report, which don’t occur here in Goegap but at the Augrabies Falls NP. So you can find here also the Nile monitor and the flat liz- Goegap Nature Reserve ard. Measuring reptiles By Tanja Mahnkopf In tortoises and terrapins the length is measured at the shell. Straight along the mid- line of the carapace. The SV-Length is the length of head and body (Snout to Vent). In lizards it easier to look for this length because their tail may be a regenerated one Introduction and these are often shorter than the original one. The length that is mentioned for the The reptiles are an ancient class on earth. The earliest reptile fossils are about 315 species in this report is the average to the maximum length. For the snakes I tried to million years old. During the aeons of time they evolved a great diversity of extinct give the total length because it is often impossible to say where the tail begins and and living reptiles. The dinosaurs and their relatives dominated the earth 150 million the body ends without holding the snake. But there was not for every snake a total years ago. Our living reptiles are remnants of that period or from a period after the length available. dinosaurs were extinct. Except of the chameleons (there are only two) you can find all reptiles in the appen- Obviously it looks like reptiles are not as successful as mammals. -
Index of Handbook of the Mammals of the World. Vol. 9. Bats
Index of Handbook of the Mammals of the World. Vol. 9. Bats A agnella, Kerivoula 901 Anchieta’s Bat 814 aquilus, Glischropus 763 Aba Leaf-nosed Bat 247 aladdin, Pipistrellus pipistrellus 771 Anchieta’s Broad-faced Fruit Bat 94 aquilus, Platyrrhinus 567 Aba Roundleaf Bat 247 alascensis, Myotis lucifugus 927 Anchieta’s Pipistrelle 814 Arabian Barbastelle 861 abae, Hipposideros 247 alaschanicus, Hypsugo 810 anchietae, Plerotes 94 Arabian Horseshoe Bat 296 abae, Rhinolophus fumigatus 290 Alashanian Pipistrelle 810 ancricola, Myotis 957 Arabian Mouse-tailed Bat 164, 170, 176 abbotti, Myotis hasseltii 970 alba, Ectophylla 466, 480, 569 Andaman Horseshoe Bat 314 Arabian Pipistrelle 810 abditum, Megaderma spasma 191 albatus, Myopterus daubentonii 663 Andaman Intermediate Horseshoe Arabian Trident Bat 229 Abo Bat 725, 832 Alberico’s Broad-nosed Bat 565 Bat 321 Arabian Trident Leaf-nosed Bat 229 Abo Butterfly Bat 725, 832 albericoi, Platyrrhinus 565 andamanensis, Rhinolophus 321 arabica, Asellia 229 abramus, Pipistrellus 777 albescens, Myotis 940 Andean Fruit Bat 547 arabicus, Hypsugo 810 abrasus, Cynomops 604, 640 albicollis, Megaerops 64 Andersen’s Bare-backed Fruit Bat 109 arabicus, Rousettus aegyptiacus 87 Abruzzi’s Wrinkle-lipped Bat 645 albipinnis, Taphozous longimanus 353 Andersen’s Flying Fox 158 arabium, Rhinopoma cystops 176 Abyssinian Horseshoe Bat 290 albiventer, Nyctimene 36, 118 Andersen’s Fruit-eating Bat 578 Arafura Large-footed Bat 969 Acerodon albiventris, Noctilio 405, 411 Andersen’s Leaf-nosed Bat 254 Arata Yellow-shouldered Bat 543 Sulawesi 134 albofuscus, Scotoecus 762 Andersen’s Little Fruit-eating Bat 578 Arata-Thomas Yellow-shouldered Talaud 134 alboguttata, Glauconycteris 833 Andersen’s Naked-backed Fruit Bat 109 Bat 543 Acerodon 134 albus, Diclidurus 339, 367 Andersen’s Roundleaf Bat 254 aratathomasi, Sturnira 543 Acerodon mackloti (see A. -
Mammals of the Kafa Biosphere Reserve Holger Meinig, Dr Meheretu Yonas, Ondřej Mikula, Mengistu Wale and Abiyu Tadele
NABU’s Follow-up BiodiversityAssessmentBiosphereEthiopia Reserve, Follow-up NABU’s Kafa the at NABU’s Follow-up Biodiversity Assessment at the Kafa Biosphere Reserve, Ethiopia Small- and medium-sized mammals of the Kafa Biosphere Reserve Holger Meinig, Dr Meheretu Yonas, Ondřej Mikula, Mengistu Wale and Abiyu Tadele Table of Contents Small- and medium-sized mammals of the Kafa Biosphere Reserve 130 1. Introduction 132 2. Materials and methods 133 2.1 Study area 133 2.2 Sampling methods 133 2.3 Data analysis 133 3. Results and discussion 134 3.1 Soricomorpha 134 3.2 Rodentia 134 3.3 Records of mammal species other than Soricomorpha or Rodentia 140 4. Evaluation of survey results 143 5. Conclusions and recommendations for conservation and monitoring 143 6. Acknowledgements 143 7. References 144 8. Annex 147 8.1 Tables 147 8.2 Photos 152 NABU’s Follow-up Biodiversity Assessment at the Kafa Biosphere Reserve, Ethiopia Small- and medium-sized mammals of the Kafa Biosphere Reserve Holger Meinig, Dr Meheretu Yonas, Ondřej Mikula, Mengistu Wale and Abiyu Tadele 130 SMALL AND MEDIUM-SIZED MAMMALS Highlights ´ Eight species of rodents and one species of Soricomorpha were found. ´ Five of the rodent species (Tachyoryctes sp.3 sensu (Sumbera et al., 2018)), Lophuromys chrysopus and L. brunneus, Mus (Nannomys) mahomet and Desmomys harringtoni) are Ethiopian endemics. ´ The Ethiopian White-footed Mouse (Stenocephalemys albipes) is nearly endemic; it also occurs in Eritrea. ´ Together with the Ethiopian Vlei Rat (Otomys fortior) and the African Marsh Rat (Dasymys griseifrons) that were collected only during the 2014 survey, seven endemic rodent species are known to occur in the Kafa region, which supports 12% of the known endemic species of the country. -
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.