MICROBATS of the Young District
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Bat Conservation 2021
Bat Conservation Global evidence for the effects of interventions 2021 Edition Anna Berthinussen, Olivia C. Richardson & John D. Altringham Conservation Evidence Series Synopses 2 © 2021 William J. Sutherland This document should be cited as: Berthinussen, A., Richardson O.C. and Altringham J.D. (2021) Bat Conservation: Global Evidence for the Effects of Interventions. Conservation Evidence Series Synopses. University of Cambridge, Cambridge, UK. Cover image: Leucistic lesser horseshoe bat Rhinolophus hipposideros hibernating in a former water mill, Wales, UK. Credit: Thomas Kitching Digital material and resources associated with this synopsis are available at https://www.conservationevidence.com/ 3 Contents Advisory Board.................................................................................... 11 About the authors ............................................................................... 12 Acknowledgements ............................................................................. 13 1. About this book ........................................................... 14 1.1 The Conservation Evidence project ................................................................................. 14 1.2 The purpose of Conservation Evidence synopses ............................................................ 14 1.3 Who this synopsis is for ................................................................................................... 15 1.4 Background ..................................................................................................................... -
Bat Echolocation Research a Handbook for Planning and Conducting Acoustic Studies Second Edition
Bat Echolocation Research A handbook for planning and conducting acoustic studies Second Edition Erin E. Fraser, Alexander Silvis, R. Mark Brigham, and Zenon J. Czenze EDITORS Bat Echolocation Research A handbook for planning and conducting acoustic studies Second Edition Editors Erin E. Fraser, Alexander Silvis, R. Mark Brigham, and Zenon J. Czenze Citation Fraser et al., eds. 2020. Bat Echolocation Research: A handbook for planning and conducting acoustic studies. Second Edition. Bat Conservation International. Austin, Texas, USA. Tucson, Arizona 2020 This work is licensed under a Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 International License ii Table of Contents Table of Figures ....................................................................................................................................................................... vi Table of Tables ........................................................................................................................................................................ vii Contributing Authors .......................................................................................................................................................... viii Dedication…… .......................................................................................................................................................................... xi Foreword…….. .......................................................................................................................................................................... -
A Survey of the Bat Fauna
__________________________________________________________________________________ Assessment of risk to Large Forest Bat on Lord Howe Isand from proposed wind turbines. An assessment of the risk to the Large Forest Bat Vespadelus darlingtoni from proposed wind turbines on Lord Howe Island, New South Wales. A report to Lord Howe Island Board G.A. Hoye Fly By Night Bat Surveys Pty Ltd ABN 48 068 562 005 PO Box 271 BELMONT NSW 2280 Tel 4947 7794 Fax 4947 7537 January 2016 January 2016 Fly By Night Bat Surveys Pty Ltd __________________________________________________________________________________ 1 __________________________________________________________________________________ Assessment of risk to Large Forest Bat on Lord Howe Isand from proposed wind turbines. 1 INTRODUCTION Fly By Night Bat Surveys PL was requested by the Lord Howe Island Board to assess potential impacts to the Large Forest Bat from two proposed wind turbines to be sited in pasture on the southern flank of Transit Hill. This species is currently the only native mammal known to breed on the island. Previous survey has confirmed the presence of this species in the lower elevated parts of the island including the area where the two turbines are proposed (Fly By Night Bat Surveys 2010). A population of approximately 500 breeding females exists north of the airstrip, with a second smaller population centred around Mount Gower and Mount Lidgebird (Fly By Night Bat Surveys 2010-2014). Significant mortality of microchiropteran bats has occurred at utility wind farms in North America and Europe (eg Kunz 2007b). In eastern North America mortality from turbine strike along forested ridge tops varies from 15.3 to 41.1 bats per megawatt (MW) of installed capacity per year Kunz (2007b). -
Summer Indiana Bat Ecology in the Southern Appalachians
SUMMER INDIANA BAT ECOLOGY IN THE SOUTHERN APPALACHIANS: AN INVESTIGATION OF THERMOREGULATION STRATEGIES AND LANDSCAPE SCALE ROOST SELECTION _______________________ A thesis Presented to The College of Graduate and Professional Studies Department of Biology Indiana State University Terre Haute, Indiana ______________________ In Partial Fulfillment of the Requirements for the Degree Master’s in Biology _______________________ by Kristina Hammond August 2013 Kristina Hammond 2013 Keywords: Myotis sodalis, Indiana bat, thermoregulation, MaxENT, landscape, roosting ecology ii COMMITTEE MEMBERS Committee Chair: Joy O’Keefe, PhD Assistant Professor of Biology Indiana State University Committee Member: George Bakken, PhD Professor of Biology Indiana State University Committee Member: Stephen Aldrich, PhD Assistant Professor of Geography Indiana State University Committee Member: Susan Loeb, PhD Research Ecologist USDA Forest Service, Southern Research Station & Clemson University iii ABSTRACT In the southern Appalachians there are few data on the roost ecology of the federally endangered Indiana bat (Myotis sodalis). During 2008-2012, we investigated roosting ecology of the Indiana bat in ~280,000 ha in the Great Smoky Mountains National Park, Cherokee National Forest, and Nantahala National Forest in the southern Appalachians Mountains of Tennessee and North Carolina. We investigated 2 aspects of the Indiana bat’s roosting ecology: thermoregulation and the extrinsic factors that influence body temperature, and landscape-scale roost selection. To investigate thermoregulation of bats at roost, we used data gathered in 2012 from 6 female Indiana bats (5 adults and 1 juvenile) to examine how reproductive condition, group size, roost characteristics, air temperature, and barometric pressure related to body temperature of roosting bats. We found that air temperature was the primary factor correlated with bats’ body temperatures while at roost (P < 0.01), with few differences detected among reproductive classes in terms of thermoregulatory strategies. -
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. -
Nest Boxes: Creating Homes for Urban Wildlife
Nest Boxes: Creating homes for urban wildlife Importance of Hollows Australia is home to over 350 species of land animals that depend on the hollows that form in old growth eucalyptus trees for shelter or reproduction. Hollows are formed through loss of limb, insect activity (like termites), decay and weathering. Suitable hollows taken a minimum of 80- 100 years and for larger animals it could be 150-250 years for a suitable hollow to form. Some of the many animals in Australia that rely on tree hollows include parrots, owls, kingfishers, ducks, possums, gliders, micro bats and even many reptiles, frogs and invertebrates. Within urban areas hollow bearing trees are found on public land (national parks, water ways, beach foreshore and streets) and on private land (front and back yards). Many hollow dependent species are in decline due to the widespread loss of hollow bearing trees. In urban areas hollows are removed for urban development (new houses, roads and factories) and for public safety reasons. Even if these trees are replanted, up to 100 years or more may pass before they begin to form hollows suitable for use by wildlife. If hollow dependent species are to continue to survive in urban and rural areas, urgent action is required to protect hollow bearing trees wherever possible. Nest boxes are needed in areas where hollows have already been lost. What are Nest Boxes? Nest boxes act as an artificial hollow that provide opportunities for hollow dependent fauna to survive in areas where their natural breeding habitat has been destroyed. Nest boxes are most useful in areas where hollows are lacking and other aspects of habitat are sufficient, such as food and water supply. -
Brigalow Belt Bioregion – a Biodiversity Jewel
Brigalow Belt bioregion – a biodiversity jewel Brigalow habitat © Craig Eddie What is brigalow? including eucalypt and cypress pine forests and The term ‘brigalow’ is used simultaneously to refer to; woodlands, grasslands and other Acacia dominated the tree Acacia harpophylla; an ecological community ecosystems. dominated by this tree and often found in conjunction with other species such as belah, wilga and false Along the eastern boundary of the Brigalow Belt are sandalwood; and a broader region where this species scattered patches of semi-evergreen vine thickets with and ecological community are present. bright green canopy species that are highly visible among the more silvery brigalow communities. These The Brigalow Belt bioregion patches are a dry adapted form of rainforest, relics of a much wetter past. The Brigalow Belt bioregion is a large and complex area covering 36,400 000ha. The region is thus recognised What are the issues? by the Australian Government as a biodiversity hotspot. Nature conservation in the region has received increasing attention because of the rapid and extensive This hotspot contains some of the most threatened loss of habitat that has occurred. Since World War wildlife in the world, including populations of the II the Brigalow Belt bioregion has become a major endangered bridled nail-tail wallaby and the only agricultural and pastoral area. Broad-scale clearing for remaining wild population of the endangered northern agriculture and unsustainable grazing has fragmented hairy-nosed wombat. The area contains important the original vegetation in the past, particularly on habitat for rare and threatened species including the, lowland areas. glossy black-cockatoo, bulloak jewel butterfl y, brigalow scaly-foot, red goshawk, little pied bat, golden-tailed geckos and threatened community of semi evergreen Biodiversity hotspots are areas that support vine thickets. -
ABLV Bat Stats June 2016
ABLV BAT STATS Australian Bat Lyssavirus Report - June 2016 Cases of ABLV infection - January to June 2016 Nine cases of Australian bat lyssavirus (ABLV) Table 1: ABLV infection in Australian bats as confirmed by infection were reported in bats in Australia between FAT, PCR, IHC and/or virus isolation^ January and June 2016, from Queensland, New South Wales and Victoria (Table 1). YEAR NSW NT QLD VIC WA SA Total Queensland 1995 0 0 1# 0 0 0 1 Two black flying-foxes (Pteropus alecto), two little red 1996 1 0 9 1 0 0 11 flying-foxes (P. scapulatus) and one spectacled flying-fox (P. conspicillatus) from Queensland were found to be 1997 7 1 27+ 0 0 0 35 infected with ABLV to June 2016. In three bats, behaviour 1998 1 0 26+ 0 0 0 27 changes and neurological signs were reported such as hanging low in a tree, agitation, being subdued and easy 1999 0 0 6 0 0 0 6 to handle, twitching, nystagmus, paresis and inability to hang. Increased respiratory rate and effort were 2000 1 0 14 0 0 0 15 additionally reported in one bat. One bat was submitted 2001 0 0 9 1 4 0 14 because a person was bitten when picking the bat up, and the other due to contact with a pet dog. 2002 4 0 10 2 1 0 17 Histopathological findings included mild to severe non- 2003 6 0 3 2 0 0 11 suppurative meningoencephalitis, ganglioneuritis, subacute aspiration pneumonia and mild sialoadenitis. In 2004 5 0 6 1 0 0 12 one bat the urinary bladder was markedly distended with 2005 6 0 5 0 0 0 11 urine and the bladder wall was haemorrhagic. -
Bat Community Structure and Habitat Use Across Disturbance Regimes
Bat community structure and habitat use across logging regimes in jarrah eucalypt forests of south-western Australia Paul W. Webala School of Biological Sciences Faculty of Sustainability, Environment and Life Sciences Murdoch University, Perth, Western Australia Submitted in fulfilment of the requirements for the degree of Doctor of Philosophy August 2010 i Abstract In many parts of the world, the increasing demand for timber and other forest products has led to loss, fragmentation, degradation or modification of natural forest habitats. The consequences of such habitat changes have been well studied for some animal groups, however not much is known of their effects on bats. In Australia, logging of native forests is a major threat to the continent‘s biodiversity and while logging practices have undergone great changes in the past three decades to selective logging (including ecologically sustainable forest management), which is more sympathetic to wildlife, there is still concern about the effects of logging on the habitat of many forest-dwelling animals. The goal of this thesis was to investigate the effects of logging on the bat species assemblages at both community and individual species levels in terms of their foraging and roosting ecology in jarrah forests of south-western Australia. This information is necessary to strengthen the scientific basis for ecologically sustainable forest management in production forests. The outcome of this research may help in the formulation of policy and management decisions to ensure the long-term maintenance and survival of viable populations of forest-dwelling bats in these altered environments. Bats were selected because they comprise more than 25% of Australia‘s mammal species and constitute a major component of Australia‘s biodiversity. -
Fitz-Stirling 2007-2017 Ten-Year Evaluation Review
Fitz-Stirling 2007-2017 Ten-year Evaluation Review Feb / 2018 P a g e | 1 Acknowledgements: This report has benefited greatly from the discussion and guidance on content, presentation and editing by Annette Stewart, Clair Dougherty and Simon Smale. Their expert assistance is greatly appreciated. Volunteers have played a major and vital role in the monitoring and survey program over the past 5 years and I thank all of those involved. Special thanks go to Dr Sandra Gilfillan for her continuing dedication to the wallaby monitoring and research program. Volunteers Aaron Gove, who provided the bird data analysis and Richard Thomas, who provided the bat data analysis, have made a large contribution to this report and I thank them. I sincerely thank Bill and Jane Thompson who have regularly carried out all the pool monitoring for several years. Thanks also to Barry Heydenrych, Greening Australia, who provided restoration data. Funding to assist the monitoring program and UAV surveys during 2015 was gratefully received from South Coast NRM as part of the Australian Government funded ‘Restoring Gondwana’ program. Funding vital for wallaby monitoring and research was provided by the Diversicon Foundation. Citation: Sanders, A. (2018). Fitz-Stirling 2007-2017 ten-year evaluation review. Unpublished report for Bush Heritage Australia. P a g e | 2 Contents Overview of Fitz-Stirling Project ........................................................................................................ 6 This report evaluates our conservation impact ................................................................................. -
České Vernakulární Jmenosloví Netopýrů. I. Návrh Úplného Jmenosloví
Vespertilio 13–14: 263–308, 2010 ISSN 1213-6123 České vernakulární jmenosloví netopýrů. I. Návrh úplného jmenosloví Petr Benda zoologické oddělení PM, Národní museum, Václavské nám. 68, CZ–115 79 Praha 1, Česko; katedra zoologie, PřF University Karlovy, Viničná 7, CZ–128 44 Praha 2, Česko; [email protected] Czech vernacular nomenclature of bats. I. Proposal of complete nomenclature. The first and also the last complete Czech vernacular nomenclature of bats was proposed by Presl (1834), who created names for three suborders (families), 31 genera and 110 species of bats (along with names for all other then known mammals). However, his nomenclature is almost forgotten and is not in common use any more. Although more or less representative Czech nomenclatures of bats were later proposed several times, they were never complete. The most comprehensive nomenclature was proposed by Anděra (1999), who gave names for all supra-generic taxa (mostly homonymial) and for 284 species within the order Chiroptera (ca. 31% of species names compiled by Koopman 1993). A new proposal of a complete Czech nomenclature of bats is given in the Appendix. The review of bat taxonomy by Simmons (2005) was adopted and complemented by several new taxa proposed in the last years (altogether ca. 1200 names). For all taxa, a Czech name (in binomial structure for species following the scientific zoological nomenclature) was adopted from previous vernacular nomenclatures or created as a new name, with an idea to give distinct original Czech generic names to representatives of all families, in cases of species- -rich families also of subfamilies or tribes. -
Appendix a Fauna Survey Effort and Results
APPENDIX A FAUNA SURVEY EFFORT AND RESULTS October 2016 Prepared by Anderson Environment and Planning The Fauna Survey Effort (FSE) for the Biobanking Assessment Report has been guided by the following: The predict threatened species from within the Biobanking Credit Calculator; The Threatened Species Survey and Assessment Guidelines for developments and activities (working draft), NSW Department of Environment and Conservation (2004); The NSW Threatened Species Profile Database; and Previous fauna survey results from the site. The following Ecosystem Credit species have been recorded on the site during past or current survey work: Eastern Bentwing-bat (Miniopterus schreibersii oceanensis); Eastern False Pipistrelle (Falsistrellus tasmaniensis); Eastern Freetail-bat (Mormopterus norfolkensis); Greater Broad-nosed Bat (Scoteanax rueppellii); Grey-headed Flying-fox (Pteropus poliocephalus); Little Bentwing-bat (Miniopterus australis); Little Lorikeet (Glossopsitta pusilla); Long-nosed Potoroo (Potorous tridactylus); Powerful Owl (Ninox strenua); Squirrel Glider (Petaurus norfolcensis); Varied Sittella (Daphoenositta chrysoptera); Yellow-bellied Glider (Petaurus australis); Yellow-bellied Sheathtail-bat (Saccolaimus flaviventris). The following Species Credit species have been recorded on the site or surrounds during past survey work: Koala (Phascolarctos cinereus); Wallum Froglet (Crinia tinnula). Prepared by Anderson Environment and Planning Contents 1.0 Introduction ..............................................................................................................................................