Evidence for the Role of Infectious Disease in Species Extinction and Endangerment
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SDG Indicator Metadata (Harmonized Metadata Template - Format Version 1.0)
Last updated: 4 January 2021 SDG indicator metadata (Harmonized metadata template - format version 1.0) 0. Indicator information 0.a. Goal Goal 15: Protect, restore and promote sustainable use of terrestrial ecosystems, sustainably manage forests, combat desertification, and halt and reverse land degradation and halt biodiversity loss 0.b. Target Target 15.5: Take urgent and significant action to reduce the degradation of natural habitats, halt the loss of biodiversity and, by 2020, protect and prevent the extinction of threatened species 0.c. Indicator Indicator 15.5.1: Red List Index 0.d. Series 0.e. Metadata update 4 January 2021 0.f. Related indicators Disaggregations of the Red List Index are also of particular relevance as indicators towards the following SDG targets (Brooks et al. 2015): SDG 2.4 Red List Index (species used for food and medicine); SDG 2.5 Red List Index (wild relatives and local breeds); SDG 12.2 Red List Index (impacts of utilisation) (Butchart 2008); SDG 12.4 Red List Index (impacts of pollution); SDG 13.1 Red List Index (impacts of climate change); SDG 14.1 Red List Index (impacts of pollution on marine species); SDG 14.2 Red List Index (marine species); SDG 14.3 Red List Index (reef-building coral species) (Carpenter et al. 2008); SDG 14.4 Red List Index (impacts of utilisation on marine species); SDG 15.1 Red List Index (terrestrial & freshwater species); SDG 15.2 Red List Index (forest-specialist species); SDG 15.4 Red List Index (mountain species); SDG 15.7 Red List Index (impacts of utilisation) (Butchart 2008); and SDG 15.8 Red List Index (impacts of invasive alien species) (Butchart 2008, McGeoch et al. -
Critically Endangered - Wikipedia
Critically endangered - Wikipedia Not logged in Talk Contributions Create account Log in Article Talk Read Edit View history Critically endangered From Wikipedia, the free encyclopedia Main page Contents This article is about the conservation designation itself. For lists of critically endangered species, see Lists of IUCN Red List Critically Endangered Featured content species. Current events A critically endangered (CR) species is one which has been categorized by the International Union for Random article Conservation status Conservation of Nature (IUCN) as facing an extremely high risk of extinction in the wild.[1] Donate to Wikipedia by IUCN Red List category Wikipedia store As of 2014, there are 2464 animal and 2104 plant species with this assessment, compared with 1998 levels of 854 and 909, respectively.[2] Interaction Help As the IUCN Red List does not consider a species extinct until extensive, targeted surveys have been About Wikipedia conducted, species which are possibly extinct are still listed as critically endangered. IUCN maintains a list[3] Community portal of "possibly extinct" CR(PE) and "possibly extinct in the wild" CR(PEW) species, modelled on categories used Recent changes by BirdLife International to categorize these taxa. Contact page Contents Tools Extinct 1 International Union for Conservation of Nature definition What links here Extinct (EX) (list) 2 See also Related changes Extinct in the Wild (EW) (list) 3 Notes Upload file Threatened Special pages 4 References Critically Endangered (CR) (list) Permanent -
Table 5: Threatened Species in Each Country (Totals by Taxonomic Group)
IUCN Red List version 2020-1: Table 5 Last updated: 19 March 2020 Table 5: Threatened species in each country (totals by taxonomic group) * Reptiles, fishes, molluscs, other invertebrates, plants, fungi & protists: please note that for these groups, there are still many species that have not yet been assessed for the IUCN Red List and therefore their status is not known (i.e., these groups have not yet been completely assessed). Therefore the figures presented below for these groups should be interpreted as the number of species known to be threatened within those species that have been assessed to date, and not as the overall total number of threatened species for each group. AFRICA Other Fungi & North Africa Mammals Birds Reptiles* Amphibians Fishes* Molluscs* Plants* Total* Inverts* Protists* Algeria 14 15 8 3 45 12 30 26 2 155 Egypt 18 14 13 0 62 1 56 8 0 172 Libya 10 8 6 0 38 1 4 8 0 75 Morocco 18 18 13 2 55 38 33 56 5 238 Tunisia 14 11 6 1 42 8 13 10 2 107 Western Sahara 10 5 1 0 39 2 1 0 0 58 Other Fungi & Sub-Saharan Africa Mammals Birds Reptiles* Amphibians Fishes* Molluscs* Plants* Total* Inverts* Protists* Angola 22 33 7 0 55 7 4 43 0 171 Benin 16 12 7 1 46 2 1 21 0 106 Botswana 11 16 1 0 2 0 0 3 0 33 Burkina Faso 11 12 3 0 4 1 0 5 0 36 Burundi 16 14 0 1 17 3 3 134 0 188 Cabo Verde 4 7 6 0 38 13 0 51 0 119 Cameroon 47 29 13 57 126 13 13 592 0 890 Central African Republic 19 16 5 0 4 0 0 29 0 73 Chad 16 16 5 0 1 4 0 6 0 48 Comoros 5 14 5 0 17 0 77 9 0 127 Congo 18 7 6 1 60 7 0 56 0 155 Congo, The Democratic Republic of the 42 -
Guidelines for Appropriate Uses of Iucn Red List Data
GUIDELINES FOR APPROPRIATE USES OF IUCN RED LIST DATA Incorporating, as Annexes, the 1) Guidelines for Reporting on Proportion Threatened (ver. 1.1); 2) Guidelines on Scientific Collecting of Threatened Species (ver. 1.0); and 3) Guidelines for the Appropriate Use of the IUCN Red List by Business (ver. 1.0) Version 3.0 (October 2016) Citation: IUCN. 2016. Guidelines for appropriate uses of IUCN Red List Data. Incorporating, as Annexes, the 1) Guidelines for Reporting on Proportion Threatened (ver. 1.1); 2) Guidelines on Scientific Collecting of Threatened Species (ver. 1.0); and 3) Guidelines for the Appropriate Use of the IUCN Red List by Business (ver. 1.0). Version 3.0. Adopted by the IUCN Red List Committee. THE IUCN RED LIST OF THREATENED SPECIES™ GUIDELINES FOR APPROPRIATE USES OF RED LIST DATA The IUCN Red List of Threatened Species™ is the world’s most comprehensive data resource on the status of species, containing information and status assessments on over 80,000 species of animals, plants and fungi. As well as measuring the extinction risk faced by each species, the IUCN Red List includes detailed species-specific information on distribution, threats, conservation measures, and other relevant factors. The IUCN Red List of Threatened Species™ is increasingly used by scientists, governments, NGOs, businesses, and civil society for a wide variety of purposes. These Guidelines are designed to encourage and facilitate the use of IUCN Red List data and information to tackle a broad range of important conservation issues. These Guidelines give a brief introduction to The IUCN Red List of Threatened Species™ (hereafter called the IUCN Red List), the Red List Categories and Criteria, and the Red List Assessment process, followed by some key facts that all Red List users need to know to maximally take advantage of this resource. -
DRAFT of 13 July 2012
THE IUCN RED LIST OF THREATENED SPECIES: STRATEGIC PLAN 2017-2020 Citation: IUCN Red List Committee. 2017. The IUCN Red List of Threatened Species™ Strategic Plan 2017 - 2020. Prepared by the IUCN Red List Committee. Cover images (left to right) and photographer credits: IUCN & Intu Boehihartono; Brian Stockwell; tigglrep (via Flickr under CC licence); IUCN & Gillian Eborn; Gianmarco Rojas; Michel Roggo; IUCN & Imene Maliane; IUCN & William Goodwin; IUCN & Christian Winter The IUCN Red List of Threatened SpeciesTM Strategic Plan 2017 – 2020 2 THE IUCN RED LIST OF THREATENED SPECIES: STRATEGIC PLAN 2017-2020 January 2017 The IUCN Red List Partnership ............................................................................................ 4 Introduction ............................................................................................................................... 5 The IUCN Red List: a key conservation tool ....................................................................... 6 The IUCN Red List of Threatened Species: Strategic Plan 2017-2020 ......................... 7 Result 1. IUCN Red List taxonomic and geographic coverage is expanded ............. 8 Result 2. More IUCN Red List Assessments are prepared at national and, where appropriate, at regional scales .......................................................................................... 8 Result 3. Selected species groups are periodically reassessed to allow the IUCN Red List Index to be widely used as an effective biodiversity indicator. .................... -
Two New Harlequin Frogs (Anura: Atelopus) from the Andes of Northern Peru Pablo J
Southern Illinois University Carbondale OpenSIUC Publications Department of Zoology 2008 Two New Harlequin Frogs (Anura: Atelopus) from the Andes of Northern Peru Pablo J. Venegas Alessandro Catenazzi Southern Illinois University Carbondale, [email protected] Karen Siu Ting Jorge Carrillo Follow this and additional works at: http://opensiuc.lib.siu.edu/zool_pubs Published in Salamandra , Issue 44 (2008) at http://www.salamandra-journal.com/ index.php?option=com_docman&Itemid=66 Recommended Citation Venegas, Pablo J., Catenazzi, Alessandro, Siu Ting, Karen and Carrillo, Jorge. "Two New Harlequin Frogs (Anura: Atelopus) from the Andes of Northern Peru." (Jan 2008). This Article is brought to you for free and open access by the Department of Zoology at OpenSIUC. It has been accepted for inclusion in Publications by an authorized administrator of OpenSIUC. For more information, please contact [email protected]. Two new harlequin frogs from Peru SALAMANDRA 44 3 163-176 Rheinbach, 20 August 2008 ISSN 0036-3375 Two new harlequin frogs (Anura: Atelopus) from the Andes of northern Peru Pablo J. Venegas, Alessandro Catenazzi, Karen Siu-Ting & Jorge Carrillo Abstract. Two new species of Atelopus (harlequin frogs) are described from the Andes of northern Peru, one from the northern Cordillera de Huancabamba (Departamento de Piura), 2,950 m elevation, and the other from an inter-Andean valley of the upper Marañon basin, Cordillera Central (Departamento de La Libertad), 2,620 m elevation. We also suggest the possible link between infection by the chytrid fungus and mortality of harlequin frogs in the upper Marañon basin in 999. Key words. Bufonidae, Atelopus patazensis sp. -
Batrachochytrium Dendrobatidis in Peru
xvi AMPHIBIAN DISEASES MUTHS, E., B. S. PEDERSEN, AND F S. PEDERSEN. 2009. How relevant is op- LITERATURE CITED portunistic Bd sampling: Are we ready for the big picture? Herpe- tol. Rev. 40(2):183–184. BOYLE, D. G., D. B. BOYLE, V. OLSEN, J. A. T. MORGAN, AND A. D. HYATT. 2004. OUELLET, M., I. MIKAELIAN, B. D. PAULI, J. RODRIGUE, AND D. M. GREEN. Rapid quantitative detection of chytridiomycosis (Batrachochytri- 2005. Historical evidence of widespread chytrid infection in North um dendrobatidis) in amphibian samples using real-time Taqman American amphibian populations. Conserv. Biol. 19:1431–1440. PCR assay. Dis. Aquat. Org. 60:141–148. RODRIGUEZ, E. M., T. GAMBLE, M. V. HIRT, AND S. COTNER. 2009. Presence BREM, F., J. R. MENDELSON III, AND K. R. LIPS. 2007. Field-Sampling Pro- of Batrachochytrium dendrobatidis at the headwaters of the Mis- tocol for Batrachochytrium dendrobatidis from Living Amphib- sissippi River, Itasca State Park, Minnesota, USA. Herpetol. Rev. ians, Using Alcohol Preserved Swabs. Version 1.0 (18 July 2007). 40(1):48–50. Electronic document accessible at <http://www.amphibianark. SADINSKI, W., M. ROTH, S. TRELEVEN, J. THEYERL, AND P. DUMMER. DETECTION org/resources/other-documents/#Chytrid>. Conservation Inter- OF THE CHYTRID FUNGUS BATRACHOCHYTRIUM DENDROBATIDIS, ON RECENTLY national, Arlington, Virginia. METAMORPHOSED AMPHIBIANS IN THE NORTH-CENTRAL UNITED STATES. HERPE- HYATT, A. D., D. G. BOYLE, V. OLSEN, D. B. BOYLE, L. BERGER, D. OBENDORF, TOL. REV. 41(2):170–175. A. DALTON, K. KRIGER, M. HERO, H. HINES, R. PHILLOT, R. CAMPBELL, G. STEINER, S. I., AND R. M. LEHTINEN. -
Rules of Procedure for IUCN Red List Assessments 2017–2020
Rules of Procedure for IUCN Red List Assessments 2017–2020 Version 3.0 Citation: IUCN. 2016. Rules of Procedure for IUCN Red List Assessments 2017–2020. Version 3.0. Approved by the IUCN SSC Steering Committee in September 2016. Downloadable from: http://cmsdocs.s3.amazonaws.com/keydocuments/Rules_of_Procedure_for_Red_List_2017- 2020.pdf Rules of Procedure for IUCN Red List Assessments 2017–2020 Version 3.0 Contents The IUCN Red List Assessment Process Establishment and Appointment of Red List Authorities Types of Red List Authority Red List Authority Roles and Responsibilities The Red List Authority Coordinator Red List Authority Coordinator Responsibilities Overlapping Red List Authority Jurisdictions Resources Nomenclature Annex 1: Required and Recommended Supporting Information for IUCN Red List Assessments Annex 2: Schematic Illustration of the IUCN Red List Assessment Process Annex 3: Details of the Steps Involved in the IUCN Red List Process Annex 4: IUCN Red List Assessment Resources Annex 5: Procedure for Handling of Petitions against Current Listings on the IUCN Red List of Threatened SpeciesTM Annex 6: Policy on Use of Pre-Publication IUCN Red List Data Annex 7: Sensitive Data Access Restrictions Policy for the IUCN Red List 1 A. The IUCN Red List Assessment Process The IUCN Red List of Threatened Species™ is produced and managed by the IUCN Species Survival Commission (SSC), the IUCN Global Species Programme and the Red List Partnership. In order to maintain the credibility of the IUCN Red List, the process by which species can be included on the Red List has been formalized. In particular, this process includes the designation of Red List Authorities (RLAs) and Red List Authority Coordinators, under the auspices of the SSC, the responsibilities of which (and whom) are outlined in this document. -
State of Nature Report
STATE OF NATURE Foreword by Sir David Attenborough he islands that make up the The causes are varied, but most are (ButterflyHelen Atkinson Conservation) United Kingdom are home to a ultimately due to the way we are using Twonderful range of wildlife that our land and seas and their natural is dear to us all. From the hill-walker resources, often with little regard for marvelling at an eagle soaring overhead, the wildlife with which we share them. to a child enthralled by a ladybird on The impact on plants and animals has their fingertip, we can all wonder at been profound. the variety of life around us. Although this report highlights what However, even the most casual of we have lost, and what we are still observers may have noticed that all is losing, it also gives examples of how not well. They may have noticed the we – as individuals, organisations, loss of butterflies from a favourite governments – can work together walk, the disappearance of sparrows to stop this loss, and bring back nature from their garden, or the absence of where it has been lost. These examples the colourful wildflower meadows of should give us hope and inspiration. their youth. To gain a true picture of the balance of our nature, we require We should also take encouragement a broad and objective assessment of from the report itself; it is heartening the best available evidence, and that is to see so many organisations what we have in this groundbreaking coming together to provide a single State of Nature report. -
(International Trade Restrictions) on Endangered Species Populations
An Econometric Analysis of the CITES (International Trade Restrictions) on Endangered Species Populations Leah Martindill The College of New Jersey Economics Department Advisor: Dr. Subarna Samanta January 2015 Abstract: The Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) restricts the trade of endangered specimens to ensure international trade does not threaten the survival of the species. This international agreement has been around for 40 years and yet there has been no analysis of the effects these trade restrictions actually have on endangered animal populations. This is a preliminary study on the relationship between CITES and the trend of endangered species populations. The purpose of this paper is to start a conversation about ensuring that our animal conservation methods do not just sound good, but produce their intended results. As the World continues to become more global, the need for conservation methods that work becomes more critical. In order to ensure the efficacy of such methods, a definitive way to measure their effects must be established. This study attempts to draw initial conclusions about the success of the CITES convention. Contents Introduction 3 Review of Literature 6 Data & Methodology 7 Econometric Results 10 Conclusion 12 Bibliography 14 Appendix 15 2 Introduction In the last five hundred years, over eight hundred species of plant and animal have been forced into extinction due to human activity.1 As more of the World develops, so do concerns for the environment. For the past several decades conservation has been given international attention. Global World-leaders and scientists have made issues of environmental conservation and protection priorities. -
Threatened Species PROGRAMME Threatened Species: a Guide to Red Lists and Their Use in Conservation LIST of ABBREVIATIONS
Threatened Species PROGRAMME Threatened Species: A guide to Red Lists and their use in conservation LIST OF ABBREVIATIONS AOO Area of Occupancy BMP Biodiversity Management Plan CBD Convention on Biological Diversity CITES Convention on International Trade in Endangered Species DAFF Department of Agriculture, Forestry and Fisheries EIA Environmental Impact Assessment EOO Extent of Occurrence IUCN International Union for Conservation of Nature NEMA National Environmental Management Act NEMBA National Environmental Management Biodiversity Act NGO Non-governmental Organization NSBA National Spatial Biodiversity Assessment PVA Population Viability Analysis SANBI South African National Biodiversity Institute SANSA South African National Survey of Arachnida SIBIS SANBI's Integrated Biodiversity Information System SRLI Sampled Red List Index SSC Species Survival Commission TSP Threatened Species Programme Threatened Species: A guide to Red Lists and their use in conservation OVERVIEW The International Union for Conservation of Nature (IUCN)’s Red List is a world standard for evaluating the conservation status of plant and animal species. The IUCN Red List, which determines the risks of extinction to species, plays an important role in guiding conservation activities of governments, NGOs and scientific institutions, and is recognized worldwide for its objective approach. In order to produce the IUCN Red List of Threatened Species™, the IUCN Species Programme, working together with the IUCN Species Survival Commission (SSC) and members of IUCN, draw on and mobilize a network of partner organizations and scientists worldwide. One such partner organization is the South African National Biodiversity Institute (SANBI), who, through the Threatened Species Programme (TSP), contributes information on the conservation status and biology of threatened species in southern Africa. -
Predator-Prey Interactions Between Hellbenders
PREDATOR-PREY INTERACTIONS BETWEEN HELLBENDERS (CRYPTOBRANCHUS ALLEGANIENSIS ALLEGANIENSIS AND C. A. BISHOPI) AND NATIVE AND NONNATIVE FISHES A Thesis Presented to The Graduate College of Missouri State University In Partial Fulfillment Of the Requirements for the Degree Master of Science, Biology By Brian G. Gall August 2008 PREDATOR-PREY INTERACTIONS BETWEEN HELLBENDERS (CRYPTOBRANCHUS ALLEGANIENSIS ALLEGANIENSIS AND C. A. BISHOPI) AND NATIVE AND NONNATIVE FISHES Department of Biology Missouri State University, August 2008 Masters of Science Brian G. Gall ABSTRACT The introduction of nonnative fishes often results in the local extinction of native amphibians due to a lack of evolutionary history and therefore, minimally-adapted antipredator behaviors toward the introduced fishes. Populations of hellbenders (Cryptobranchus alleganiensis) in Missouri have declined considerably since the 1980’s, coinciding with a rapid increase in trout introductions for recreational angling. I examined hellbender and fish predator-prey interactions by: (1) examining the foraging behavior of predatory fishes in response to a hellbender secretion; (2) comparing the number of secretion and control-soaked food pellets consumed by trout; and (3) comparing the response of larval hellbenders to chemical stimuli from introduced (trout) and native fish predators. Brown trout, walleye and large banded sculpin respond to hellbender secretions with increased activity while small banded sculpin responded by decreasing activity. In addition, brown trout ingested more hellbender secretion-soaked food pellets than control pellets, while rainbow trout expelled secretion-soaked food pellets. Finally, larval hellbenders exhibited weak fright behavior in response to chemical stimuli from nonnative trout relative to their responses to native predatory fish stimuli. These combinations of responses indicate that predation by nonnative fishes may be a plausible hypothesis for the decline of hellbender populations in Missouri.