Tasmanian Bat Ecology: Conservation of Native Fauna
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Bat Calls of New South Wales
Bat calls of New South Wales Region based guide to the echolocation calls of microchiropteran bats Michael Pennay1 , Brad Law2 & Linda Reinhold3 1 New South Wales Department of Environment and Conservation 2 State Forests of New South Wales 3 Queensland Department of Natural Resources and Mines Bat calls of New South Wales Bat calls of New South Wales Published by the NSW Department of Environment and Conservation May 2004 Copyright © NSW Department of Environment and Conservation ISBN 0 7313 6786 3 This guide is the result of a co-operative project between NSW National Parks and Wildlife Service, now the NSW Department of Environment and Conservation (DEC) and State Forests of NSW (SFNSW). DEC provided project funding, management, staff, reference calls, preparation and printing. SFNSW provided part funding and granted support of staff time and expertise, reference calls and editing. Research was conducted under NPWS scientific licence number A2753 and SFNSW special purpose permit for research number 05466. Material presented in this publication may be copied for personal use or republished for non-commercial purposes provided that NSW Department of Environment and Conservation is fully acknowledged as the copyright owner. Apart from these purposes or for private study, research, criticism or review, as permitted under the Australian Copyright Act, no part of this publication may be reproduced by any process without written permission from NSW Department of Environment and Conservation. Inquiries should be addressed to the NSW Department of Environment and Conservation. This publication should be cited as follows: Pennay, M., Law, B., Reinhold, L. (2004). Bat calls of New South Wales: Region based guide to the echolocation calls of Microchiropteran bats. -
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 ..................................................................................................................... -
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). -
Nine Species of Bats, Each Relying on Specific Summer and Winter Habitats
Species Guide to Vermont Bats • Vermont has nine species of bats, each relying on specific summer and winter habitats. • Six species hibernate in caves and mines during the winter (cave bats). • During the summer, two species primarily roost in structures (house bats), • And four roost in trees and rocky outcrops (forest bats). • Three species migrate south to warmer climates for the winter and roost in trees during the summer (migratory bats). • This guide is designed to help familiarize you with the physical characteristics of each species. • Bats should only be handled by trained professionals with gloves. • For more information, contact a bat biologist at the Vermont Fish and Wildlife Department or go to www.vtfishandwildlife.com Vermont’s Nine Species of Bats Cave Bats Migratory Tree Bats Eastern small-footed bat Silver-haired bat State Threatened Big brown bat Northern long-eared bat Indiana bat Federally Threatened State Endangered J Chenger Federally and State J Kiser Endangered J Kiser Hoary bat Little brown bat Tri-colored bat Eastern red bat State State Endangered Endangered Bat Anatomy Dr. J. Scott Altenbach http://jhupressblog.com House Bats Big brown bat Little brown bat These are the two bat species that are most commonly found in Vermont buildings. The little brown bat is state endangered, so care must be used to safely exclude unwanted bats from buildings. Follow the best management practices found at www.vtfishandwildlife.com/wildlife_bats.cfm House Bats Big brown bat, Eptesicus fuscus Big thick muzzle Weight 13-25 g Total Length (with Tail) 106 – 127 mm Long silky Wingspan 32 – 35 cm fur Forearm 45 – 48 mm Description • Long, glossy brown fur • Belly paler than back • Black wings • Big thick muzzle • Keeled calcar Similar Species Little brown bat is much Commonly found in houses smaller & lacks keeled calcar. -
Insights Into Australian Bat Lyssavirus in Insectivorous Bats of Western Australia
Tropical Medicine and Infectious Disease Article Insights into Australian Bat Lyssavirus in Insectivorous Bats of Western Australia Diana Prada 1,*, Victoria Boyd 2, Michelle Baker 2, Bethany Jackson 1,† and Mark O’Dea 1,† 1 School of Veterinary Medicine, Murdoch University, Perth, WA 6150, Australia; [email protected] (B.J.); [email protected] (M.O.) 2 Australian Animal Health Laboratory, CSIRO, Geelong, VIC 3220, Australia; [email protected] (V.B.); [email protected] (M.B.) * Correspondence: [email protected]; Tel.: +61-893607418 † These authors contributed equally. Received: 21 February 2019; Accepted: 7 March 2019; Published: 11 March 2019 Abstract: Australian bat lyssavirus (ABLV) is a known causative agent of neurological disease in bats, humans and horses. It has been isolated from four species of pteropid bats and a single microbat species (Saccolaimus flaviventris). To date, ABLV surveillance has primarily been passive, with active surveillance concentrating on eastern and northern Australian bat populations. As a result, there is scant regional ABLV information for large areas of the country. To better inform the local public health risks associated with human-bat interactions, this study describes the lyssavirus prevalence in microbat communities in the South West Botanical Province of Western Australia. We used targeted real-time PCR assays to detect viral RNA shedding in 839 oral swabs representing 12 species of microbats, which were sampled over two consecutive summers spanning 2016–2018. Additionally, we tested 649 serum samples via Luminex® assay for reactivity to lyssavirus antigens. Active lyssavirus infection was not detected in any of the samples. -
Corynorhinus Townsendii): a Technical Conservation Assessment
Townsend’s Big-eared Bat (Corynorhinus townsendii): A Technical Conservation Assessment Prepared for the USDA Forest Service, Rocky Mountain Region, Species Conservation Project October 25, 2006 Jeffery C. Gruver1 and Douglas A. Keinath2 with life cycle model by Dave McDonald3 and Takeshi Ise3 1Department of Biological Sciences, University of Calgary, Calgary, Alberta, Canada 2Wyoming Natural Diversity Database, Old Biochemistry Bldg, University of Wyoming, Laramie, WY 82070 3Department of Zoology and Physiology, University of Wyoming, P.O. Box 3166, Laramie, WY 82071 Peer Review Administered by Society for Conservation Biology Gruver, J.C. and D.A. Keinath (2006, October 25). Townsend’s Big-eared Bat (Corynorhinus townsendii): a technical conservation assessment. [Online]. USDA Forest Service, Rocky Mountain Region. Available: http:// www.fs.fed.us/r2/projects/scp/assessments/townsendsbigearedbat.pdf [date of access]. ACKNOWLEDGMENTS The authors would like to acknowledge the modeling expertise of Dr. Dave McDonald and Takeshi Ise, who constructed the life-cycle analysis. Additional thanks are extended to the staff of the Wyoming Natural Diversity Database for technical assistance with GIS and general support. Finally, we extend sincere thanks to Gary Patton for his editorial guidance and patience. AUTHORS’ BIOGRAPHIES Jeff Gruver, formerly with the Wyoming Natural Diversity Database, is currently a Ph.D. candidate in the Biological Sciences program at the University of Calgary where he is investigating the physiological ecology of bats in northern arid climates. He has been involved in bat research for over 8 years in the Pacific Northwest, the Rocky Mountains, and the Badlands of southern Alberta. He earned a B.S. in Economics (1993) from Penn State University and an M.S. -
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. -
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. -
Overview Bat Species Around the World Face a Myriad of Threats, from Climate Change and Habitat Loss to Infectious Disease
Fact sheet for the 12th Meeting of the Conference of the Parties (CoP12) to the Convention on Migratory Species (CMS) Hoary bat Lasiurus cinereus Southern red bat Lasiurus blossevillii Eastern red bat Lasiurus borealis Southern yellow bat Lasiurus ega Proposed action: Inclusion on CMS Appendix II Proponents: Peru M. BROCK FENTON HOARY BAT / Overview Bat species around the world face a myriad of threats, from climate change and habitat loss to infectious disease. Recently, a new threat to migratory bat species has emerged: wind energy production. Although a critical source of renewable energy, research from the last decade has shown that, in just the United States and Canada, over half a million bats are killed each year by wind turbines. New research indicates that mortality at wind turbines has the potential to cause dramatic population-level declines in hoary bats, the species most frequently killed at wind turbines. Technological solutions are in development and operational changes at turbines can be immediately adopted, but most bat species killed by wind turbines do not have any formalized protection, so there is little incentive for wind energy facilities to adopt potentially costly measures that can drastically reduce bat fatalities. CMS Appendix II listing can catalyze protection for these species and encourage research into these migratory bat species and how best to protect them. Fact sheet for the 12th Meeting of the Conference of the Parties (CoP12) to the Convention on Migratory Species (CMS) Biology and Distribution yellow bats are also killed by wind turbines, but most of the records These four species of migratory bats predominantly roost in trees, are from a limited portion of their range. -
Washington, D.C. Bat Species List
Washington, D.C. Bat Species List Washington D.C.’s bats are divided into two main groups based on their roosting habits- “cave bats” and “tree bats.” “Cave bats” hibernate in caves during the winter and usually form colonies to roost and raise their pups during the summer. These colonies can be found in tree cavities, buildings, or other human-made structures. “Tree bats” tend to be solitary and roost under pieces of bark or in small groups. Tree bats often forage in the upper forest canopy and migrate long distances during the spring and fall. Washington, D.C.’s Cave Bats Big Brown Bat (Eptesicus fuscus) Big brown bats are ubiquitous throughout the United States and are found in both cities and rural environments. They usually form maternity colonies under loose bark and within small tree cavities. Other maternity roosts are commonly found in buildings and barns and under bridges. Big brown bats are a highly adaptable bat species that can relocate to human-made structures in response to increasing levels of habitat loss. They can also tolerate cooler (Photo Credit: Paul and Joyce Berquist) temperatures than other bat species, allowing them to roost in less insulated structures. Big brown bats are insectivorous and are specialized to prey upon beetles, but they will also consume other insects such as moths, ants, wasps, and flies. In Washington, D.C., big brown bats are one of the more likely species to form a colony inside of a home and are commonly observed foraging at dusk. Little Brown Bat (Myotis lucifugus) White-Nose Syndrome has decimated populations of little brown bats in Washington, D.C., and they are expected to become extirpated within the next few decades. -
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.