MICROBATS of the Young District

Total Page:16

File Type:pdf, Size:1020Kb

MICROBATS of the Young District MICROBATS of the Young District Major Players in Healthy Productive Landscapes and Waterways INTRODUCTION Welcome to the ‘Microbats of the Young District’ Project – a three-year program co-ordinated by Young District Landcare to familiarise the human residents of the Young district with a group of tiny mammals seldom seen or CONTENTS heard, but of greater importance to our economy and environmental health than most people appreciate. The Project has been made possible through funding by Riverina Local Land Services community grants. Introducing Microbats 3 In April 2014 the project was launched with a Bat Night Microbat body plan 3 presentation ‘Microbats - Fascinating Creatures of the Habitat 4 Night’, followed by school and community group talks, newspaper articles and radio interviews. The fact sheet Roosting 4 ‘Wildlife in the Young District – Microbats’ rounded out the initial education campaign. Foraging 5 Next came activities designed to enhance and protect Identification 6 microbat habitat “so that we can continue to reap the White-striped Freetail Bat 7 benefits of their presence into the future” (Mikla Lewis (Austronomas australis) OAM - YDL Co-ordinator). Inland Freetail Bat (Ozimops petersi) 7 One hundred and forty microbat boxes have been South-eastern Freetail (Little Mastiff) Bat 8 manufactured and installed with information signs in various locations around the Young district. Volunteers (Ozimops planiceps) have planted local ‘bat friendly’ native plants, with many Gould’s Wattled Bat (Chalinolobus gouldii) 8 also given away to encourage private plantings for Chocolate Wattled Bat (Chalinolobus morio) 9 future habitat. Large-footed (Southern) Myotis (Myotis At community workshops, primary producers have learnt macropus) 9 about ecosystem services provided by microbats. Lesser Long-eared Bat This booklet (designed to be read as a companion to (Nyctophilus geoffroyi) 10 the 2014 fact sheet), introduces the microbat species Gould’s Long-eared Bat recorded in the Young district, their habitat preferences, and the ecosystem services they provide for us in (Nyctophilus gouldi) 10 residential and rural environments (broadacre, orchards, Inland Broad-nosed Bat vineyards) and around waterways. (Scotorepens balstoni) 11 An Education Package incorporating this booklet, the fact Inland Forest Bat (Vespadelus baverstocki) 11 sheet, a poster, PowerPoint Presentation and Microbat Southern Forest Bat (Vespadelus regulus) 12 Project Manual completes the current project. It is Little Forest Bat (Vespadelus vulturnus) 12 anticipated that the Package will be presented to and used by local schools, community, and agricultural groups. Ecosystem Services – It will also be available for use by other Landcare groups. How Microbats can help us 13 Young District Landcare has purchased AnaBat Detectors Threats to Microbats – How we give (which record echolocation calls) to monitor microbat presence and identify the different species in selected Microbats a locations, with special attention given to installed hard time 14 microbat boxes. The monitoring will help determine future action needed to preserve and enhance the habitat An Action Plan – How we can help Microbats 14 of these environmentally-friendly ‘insect More Information and Acknowledgements 16 pest terminators’. 2 Microbats of the Young District INTRODUCING MICROBATS Microbats are small, nocturnal, flying mammals which Due to a lack of local research, it is not known which eat insects. They make up almost 25% of Australia’s species are common, uncommon, or rare and in urgent CONTENTS native mammals, with 18 of the 33 or so New South need of help in our region. Wales species having been found in and around the Young district. Microbats have longer life spans than other mammals the same size (eg mice), and together with a low All microbat species are PROTECTED, meaning that it reproductive rate (1 or 2 young per year), they are is illegal to kill, injure or disturb them or their habitat, more likely to suffer population decline. Many live for and some species are also VULNERABLE, meaning that 10 years, with some individuals known to be at least 30 they are facing a high risk of extinction in NSW in the years old. medium-term future if their habitat is not maintained. Diagram: © Mid Murray LAP MICROBAT BODY PLAN The smallest microbat in the Young district has a head/body length ranging from 34.7mm to 48mm (Little Forest Bat), whilst the body of the largest can measure up to 86.5mm (White-striped Freetail Bat). Their tail and wing membranes are fragile and prone to damage but heal remarkably quickly. Future research may present opportunities for the development of new wound treatments if we can determine how the bats achieve this feat. Microbats of the Young District 3 HABITAT A healthy habitat must provide both roosting and Fortunately many microbat species have survived these foraging sites with an ample insect food supply. It ideally disruptions because they are more mobile and adaptable contains a variety of local native vegetation (especially than some other native animals. However, their overall old hollow-bearing trees) to ensure the survival of numbers and diversity have probably been reduced. the microbats. Caves, where they occur, also provide As well as larger areas of remaining native woodland and essential habitat for some species. forest (eg Dananbilla Range), microbats can be found Different species have different habitat needs, and where roosting and feeding in fragmented remnants of native the preferred habitat of native vegetation is scarce or vegetation along roadsides and watercourses. Recent not available, some species use parks and home gardens, research has highlighted just how important these buildings, culverts, bridges and abandoned mines for remnants are in maintaining the number of microbats we roosting and foraging. still have in our agricultural areas. Large, isolated farm paddock trees, both dead and living, provide especially Native vegetation in the Young district has been important foraging areas. substantially reduced and modified by clearing since European settlement, with only small areas and isolated Dams and creeks with open water provide areas for fragments left. Agriculture, mining and towns have drinking and feeding because of the many insects they changed the landscape by introducing new plant and attract, while breeding colonies may be found where animal species. Waterways have been modified and suitable vegetation is within flying distance. sometimes polluted, and new structures, including dams, have been added. Young Arboretum has bat boxes for Paddock trees are important for foraging. Bridge for roosting and regrowth for foraging. r o o s ti n g . P h o t o : © M i k l a L e w i s Photo: © Mikla Lewis Photo: © Mikla Lewis ROOSTING Microbats roost singly, in small groups or in colonies and require sites for three different purposes: • shelter from predators and extreme day-time temperatures; • shelter during torpor (a short form of hibernation lasting from hours to several days) or hibernation when food is scarce and winter temperatures are low. * Torpid bats should not be disturbed. Waking up uses fat reserves they cannot replace when there is little food around and they may die. • shelter for breeding, preferably near water or in humid areas. All locally occurring microbat species give birth to single or twin young each year, mostly during early summer when food is abundant. Young are suckled until able to fly and forage for themselves at 3-6 months of age. 4 Microbats of the Young District Loose bark, crevices and hollows in both dead and living trees are preferred sites for most of our local species, but they FORAGING will use suitable human-made structures (eg sheds, roof cavities and bat boxes) where suitable natural roosts are not available. Some microbats will roost in bird nests. Skull of the Southern Forest Bat (actual length 12.7 mm), showing the sharp, pointy teeth used to crunch its insect prey. Photo: © Australian Museum Microbats navigate and forage using echolocation, a sophisticated form of sonar. They emit ultra-high frequencies from their nose or mouth, then use their ears to detect the pulses which bounce back from their surroundings. Most species can be identified by their echolocation call as recorded then analysed using an AnaBat Detector. Except for the call of the White-striped Freetail Bat, the echolocation calls of the 12 microbats in the Young district cannot be heard by humans, although we can hear some of their ‘chatter’ as they Fairy Martin nests can double as bat roosts. Photo: © Mikla Lewis communicate with each other. Each microbat species has its own foraging, or combination of, foraging techniques: • Some fly quickly, high above trees; • Some fly and manoeuvre within or below trees; • Some fly over water or open shrublands and grasslands; • Many will pick insects off leaves and branches (gleaning); • Some even land on the ground where they chase and catch their prey. Chocolate Wattled Bat colony in roof cavity. Insects can be caught in the mouth, or in the tail and wing Photo: © Australian Museum membranes then transferred to the mouth. Native vegetation and waterways provide the best foraging areas, but anywhere insects are plentiful is a potential feeding area. A rescued Inland Broad-nosed Bat being fed a meal worm by a WIRES carer. Hollows and crevices in dead trees provide Photo: © Anne Lemon roosts. Photo: © Anne Lemon Microbats of the Young District 5 IDENTIFICATION Microbats found in the Young district belong to the The main identifying physical feature of a microbat is families Molossidae (Freetail Bats) and Vespertilionidae its tail and tail membrane (see diagrams below from (Evening Bats), with a good chance that the family Sue Churchill’s book Australian Bats). The Sheathtail Emballonuridae (Sheathtail Bats) is represented by the Bat tail protrudes through the upper surface of the tail Yellow-bellied Sheath-tail Bat, which has been found in membrane, which then forms a sheath over the rest of surrounding districts.
Recommended publications
  • 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 .....................................................................................................................
    [Show full text]
  • 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…….. ..........................................................................................................................................................................
    [Show full text]
  • 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).
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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 .................................................................................
    [Show full text]
  • 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.
    [Show full text]
  • 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 ..............................................................................................................................................
    [Show full text]