Do We Need to Use Bats As Bioindicators?
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On the Distribution, Taxonomy and Karyology of the Genus Plecotus
TurkJZool 27(2003)293-300 ©TÜB‹TAK OntheDistribution,TaxonomyandKaryologyoftheGenus Plecotus (Chiroptera:Vespertilionidae)inTurkey AhmetKARATAfi DepartmentofBiology,FacultyofScience-Art,Ni¤deUniversity,Ni¤de–TURKEY NuriY‹⁄‹T,ErcümentÇOLAK,TolgaKANKILIÇ DepartmentofBiology,FacultyofScience,AnkaraUniversity,Ankara-TURKEY Received:12.04.2002 Abstract: Plecotusauritus andPlecotusaustriacus wererecordedfrom8and3localitiesintheAsiaticpartofTurkey,respectively. Itwasdeterminedthatthelengthofthefirstpremolar,theshapeofthezygomaticarchesandbaculumdistinguishthesetaxaf rom eachother.Apartfromthesemorphologicalcharacteristics,thetibialengthof P.austriacus wasfoundtobesignificantlygreater thanthatof P.austriacus (P<0.05).Thediploidchromosomenumberswereidenticalinbothtaxa(2n=32).Thenumberof chromosomalarms(FN=54)andthenumberofautosomalchromosomalarms(FNa=50)werethesameasinpreviouslypublished papersonP.austriacus. KeyWords: Plecotusauritus,Plecotusaustriacus,Karyology,Turkey Türkiye’deYay›l›flGösterenPlecotus (Chiroptera:Vespertilionidae)CinsininYay›l›fl›, TaksonomisiveKaryolojisiÜzerineBirÇal›flma Özet: Plecotusauritus sekizvePlecotusaustriacus üçlokalitedenolmaküzereAnadolu’dankaydedildi.‹lkpremolarlar›nuzunlu¤u, zygomatikyay›nvebakulumunfleklininbutaksonlar›birbirindenay›rd›¤›saptand›.Bumorfolojikkarakterlerdenbaflka, P. autriacus’untibiauzunlu¤ununP.austriacus’tanistatistikiolarakdahabüyükoldu¤ubelirlendi(P<0.05).Diploidkromozomsay›s› herikitaksondabenzerbirflekilde2n=32dir. P.austriacus’unkromozomkolsay›lar›n›n(FN=54)veotosomalkromozomkol say›lar›n›n(FNa=50)literatüreuygunoldu¤ubulundu. -
Appendix G Final SCR Panther Grove 05152020
LWEG Tiers 1 and 2 Site Characterization Report Panther Grove Wind Energy Project Woodford County, Illinois May 15, 2020 Prepared for: Panther Grove Wind, LLC 17300 N. Dallas Parkway, Ste. 2020 Dallas Texas 75248 Prepared by: Stantec Consulting Services Inc. 2300 Swan Lake Blvd., Suite 202 Independence, IA 50644 Phone: (319) 334-3755 Fax: (319) 334-3780 Project #193706902 Table of Contents 1.0 INTRODUCTION ............................................................................................................ 1 1.1 PROJECT DESCRIPTION ............................................................................................. 1 1.2 REGULATORY BACKGROUND .................................................................................... 1 1.3 PURPOSE AND OBJECTIVES ...................................................................................... 2 2.0 METHODS ..................................................................................................................... 4 2.1 PRELIMINARY SITE EVALUATION (TIER 1) ................................................................. 4 2.1.1 Land Cover and Use ...................................................................................... 4 2.1.2 Wetlands and Waterways ............................................................................... 4 2.1.3 Migratory Birds ...............................................................................................4 2.1.4 Eagles and Other Raptors ............................................................................. -
BAT FIELD TECH WORKSHOP.Pmd
Gathering evidence of the utility of bats: Training in Field Techniques for Ecological Studies of Chiroptera C. Srinivasulu* and Sally Walker** The Chiroptera Conservation and Information Network of South Asia (CCINSA) and the IUCN SSC Chiroptera Threatened bats of India Specialist Group joined with the College of Forestry, Kerala Agricultural University, Thrissur to conduct its second field Fruit bats (Megachiroptera) -- total 5 techniques training workshop, from 28 July – 1 August 2003 Latidens salimalii Thonglongya, 1972 -- EN sponsored by Chester Zoo and Marwell Zoo, U.K at Thrissur. Pteropus faunulus Miller, 1902 -- EN Pteropus hypomelanus Temminck, 1853 -- EN The first such workshop was conducted at Madurai Pteropus melanotus Blyth, 1863 -- VU Kamaraj University, School of Biological Sciences almost Pteropus vampyrus (Linnaeus, 1758) -- EN two years ago, ably led by Dr. Paul Bates from U.K. and author of the definitive book on bats of this region Bats of Insectivorous bats (Microchiroptera) -- total 24 the Indian Subcontinent, (1997). He was assisted by Dr. M. Hipposideros diadema (E. Geoffroy, 1813) -- VU S. Pradhan and Dr. Y. P. Sinha from the Zoological Survey of Hipposideros durgadasi Khajuria, 1970 -- EN India. This workshop focused on general field techniques Hipposideros hypophyllus Kock & Bhat, 1994 -- EN and taxonomy with a day spent on the IUCN Red List Ia io Thomas, 1902 -- EN Criteria and Categories and the C.A.M.P. Workshop Process Miniopterus pusillus Dobson, 1876 -- VU in order to prepare CCINSA members for the impending Murina grisea Peters, 1872 -- CR Chiroptera C.A.M.P. which was held last year in January. Myotis annectans (Dobson, 1871) -- VU Myotis blythii (Tomes, 1857) -- VU The South Asian Chiroptera C.A.M.P. -
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. -
Listeria Monocytogenes Infection of Bat Pipistrellus Nathusii Epithelial Cells Depends on the Invasion Factors Inla and Inlb
pathogens Article Listeria monocytogenes Infection of Bat Pipistrellus nathusii Epithelial Cells Depends on the Invasion Factors InlA and InlB Olga Povolyaeva 1, Yaroslava Chalenko 2,3,* , Egor Kalinin 3, Olga Kolbasova 1, Elena Pivova 1, Denis Kolbasov 1 , Sergey Yurkov 1 and Svetlana Ermolaeva 2,3 1 Federal Research Center for Virology and Microbiology (FRCVM), 601125 Volginsky, Russia; [email protected] (O.P.); [email protected] (O.K.); [email protected] (E.P.); [email protected] (D.K.); [email protected] (S.Y.) 2 Federal Research Center for Virology and Microbiology (FRCVM), Nizhny Novgorod Research Veterinary Institute Branch, Laboratory of Molecular Microbiology, 603022 Nizhny Novgorod, Russia; [email protected] 3 Gamaleya Research Center of Epidemiology and Microbiology, Laboratory of Ecology of Pathogenic Bacteria, 123098 Moscow, Russia; [email protected] * Correspondence: [email protected]; Tel.: +7-92-5936-7317 Received: 13 September 2020; Accepted: 21 October 2020; Published: 22 October 2020 Abstract: L. monocytogenes is a widespread facultative intracellular pathogen. The range of natural hosts that supporting L. monocytogenes persistence in the environment has not been fully established yet. In this study, we were interested in the potential of L. monocytogenes to infect cells of bats, which are being increasingly recognized as a reservoir for microorganisms that are pathogenic to humans and domestic animals. A stable epithelial cell line was developed from the kidneys of Pipistrellus nathusii, a small bat widely distributed across Europe. The wild-type L. monocytogenes strain EGDe infected this cell line with an invasion efficiency of 0.0078 0.0009%. Once it entered bat cells, L. -
Bioindicator
Bioindicator INTRODUCTION A bioindicator is any species (an indicator species) or group of species whose function, population, or status can reveal the qualitative status of the environment. For example, copepods and other small water crustaceans that are present in many water bodies can be monitored for changes (biochemical, physiological, or behavioural) that may indicate a problem within their ecosystem. Bioindicators can tell us about the cumulative effects of different pollutants in the ecosystem and about how long a problem may have been present, which physical and chemical testing cannot. A biological monitor or biomonitor is an organism that provides quantitative information on the quality of the environment around it. Therefore, a good biomonitor will indicate the presence of the pollutant and can also be used in an attempt to provide additional information about the amount and intensity of the exposure. A biological indicator is also the name given to a process for assessing the sterility of an environment through the use of resistant microorganism strains (eg. Bacillus or Geobacillus). Biological indicators can be described as the introduction of a highly resistant microorganisms to a given environment before sterilization, tests are conducted to measure the effectiveness of the sterilization processes. As biological indicators use highly resistant microorganisms, any sterilization process that renders them inactive will have also killed off more common, weaker pathogens. The advantages associated with using Bioindicators are as follows: (a) Biological impacts can be determined. (b) To monitor synergetic and antagonistic impacts of various pollutants on a creature. (c) Early stage diagnosis as well as harmful effects of toxins to plants, as well as human beings, can be monitored. -
The Amphipod <I>Orchomenella Pinguis</I>
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Valery Forbes Publications Papers in the Biological Sciences 2009 The amphipod Orchomenella pinguis — A potential bioindicator for contamination in the Arctic Lis Bach Aarhus University, [email protected] Valery E. Forbes University of Nebraska-Lincoln, [email protected] Ingela Dahllöf Aarhus University Follow this and additional works at: https://digitalcommons.unl.edu/biosciforbes Part of the Aquaculture and Fisheries Commons, Other Pharmacology, Toxicology and Environmental Health Commons, Terrestrial and Aquatic Ecology Commons, and the Toxicology Commons Bach, Lis; Forbes, Valery E.; and Dahllöf, Ingela, "The amphipod Orchomenella pinguis — A potential bioindicator for contamination in the Arctic" (2009). Valery Forbes Publications. 47. https://digitalcommons.unl.edu/biosciforbes/47 This Article is brought to you for free and open access by the Papers in the Biological Sciences at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Valery Forbes Publications by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. Published in Marine Pollution Bulletin 58:11 (November 2009), pp. 1664–1670; doi: 10.1016/j.marpolbul.2009.07.001 Copyright © 2009 Elsevier Ltd. Used by permission. The amphipod Orchomenella pinguis — A potential bioindicator for contamination in the Arctic Lis Bach,1,2 Valery E. Forbes,2 and Ingela Dahllöf 1 1. Department of Marine Ecology, National Environmental Research Institute, Aarhus University, Frederiksborgvej 399, DK-4000 Roskilde, Denmark 2. Department of Environmental, Social and Spatial Change, Roskilde University, Universitetsvej 1, DK-4000 Roskilde, Denmark Corresponding author — L. Bach, email [email protected] , [email protected] Abstract Indigenous organisms can be used as bioindicators for effects of contaminants, but no such bioindicator has been estab- lished for Arctic areas. -
Per-Species Spatial-Block Cross-Validation
Ecography ECOG-03149 El-Gabbas, A. and Dormann, C. F. 2017. Improved species-occurrence predictions in data-poor regions: using large-scale data and bias correction with down- weighted Poisson regression and Maxent. – Ecography doi: 10.1111/ecog.03149 Supplementary material Appendix 1: Supplementary figures and tables Table A1: The estimated optimum combination of Maxent’s feature classes (FC) and Regularization Multiplier (RM) for each species and bias model type. Combinations with highest mean testing-AUC on 5-folds spatial-block cross-validation were selected. All the analyses were performed using modified code from the ENMeval package in R (Muscarella et al., 2014). See main text for more information. Environment-only Accessibility Effort Species FC a RM b FC RM FC RM 1 Asellia tridens LQ 0.5 LQ 3 LQHPT 3 2 Barbastella leucomelas LQ 0.5 LQ 0.5 LQHPT 3.5 3 Eptesicus bottae LQ 0.5 LQHP 2 LQHP 4 4 Hypsugo ariel LQHPT 2 LQHP 2 L 1 5 Nycteris thebaica LQ 4 LQ 3.5 LQ 4 6 Nycticeinops schlieffeni LQ 1 LQ 0.5 LQ 1.5 7 Otonycteris hemprichii LQ 0.5 LQ 1 LQHPT 0.5 8 Pipistrellus deserti L 2.5 LQ 0.5 L 3 9 Pipistrellus kuhlii LQ 0.5 LQ 0.5 LQ 0.5 10 Pipistrellus rueppellii LQ 4 LQ 0.5 LQ 4 11 Plecotus christii LQ 0.5 LQHPT 0.5 LQHPT 0.5 12 Rhinolophus clivosus LQHP 2.5 LQHPT 2 LQHPT 2.5 13 Rhinolophus hipposideros LQ 0.5 LQ 0.5 LQ 0.5 14 Rhinolophus mehelyi LQ 0.5 LQ 0.5 LQ 2.5 15 Rhinopoma cystops LQ 1 LQ 1.5 LQHPT 1 16 Rhinopoma microphyllum LQ 1.5 LQ 2 LQHPT 4 17 Rousettus aegyptiacus LQHPT 2.5 LQ 3 LQ 4 18 Tadarida aegyptiaca LQ 3 LQ 4 LQ 3 19 Tadarida teniotis LQ 0.5 LQ 0.5 LQ 0.5 20 Taphozous nudiventris LQ 1 L 2 LQHPT 2.5 21 Taphozous perforatus LQ 1.5 LQ 1 LQ 1.5 a Feature classes (FC): L linear; Q quadratic; H hinge; P product; and T threshold. -
Ozone Bioindicator Plants (Combined), Version 5.1 October, 2011
Phase 3 Field Guide – Ozone Bioindicator Plants (combined), Version 5.1 October, 2011 Section 20. Ozone Bioindicator Plants 20.1 Overview .............................................................................................................................................. 3 20.1.1 Scope and Application ................................................................................................................ 3 20.1.2 Summary of Method .................................................................................................................... 4 20.1.3 Summary of PDR Screens and Tally Procedures ....................................................................... 4 20.1.4 Equipment And Supplies ............................................................................................................. 4 20.1.5 Training and Quality Assurance .................................................................................................. 5 20.1.6 Voucher Specimens .................................................................................................................... 5 20.1.7 Communications ......................................................................................................................... 5 20.2 Ozone Biomonitoring Procedures ..................................................................................................... 7 20.2.1 Evaluation Window ...................................................................................................................... 7 20.2.2 -
Use of Leaves As Bioindicator to Assess Air Pollution Based on Composite Proxy Measure (APTI), Dust Amount and Elemental Concentration of Metals
plants Article Use of Leaves as Bioindicator to Assess Air Pollution Based on Composite Proxy Measure (APTI), Dust Amount and Elemental Concentration of Metals Vanda Éva Molnár 1 ,Dávid T˝ozsér 2, Szilárd Szabó 1 ,Béla Tóthmérész 3 and Edina Simon 2,* 1 Department of Physical Geography and Geoinformatics, University of Debrecen, H-4032 Debrecen, Hungary; [email protected] (V.É.M.); [email protected] (S.S.) 2 Department of Ecology, University of Debrecen, H-4032 Debrecen, Hungary; [email protected] 3 MTA-DE Biodiversity and Ecosystem Services Research Group, H-4032 Debrecen, Hungary; [email protected] * Correspondence: [email protected] Received: 15 October 2020; Accepted: 7 December 2020; Published: 9 December 2020 Abstract: Monitoring air pollution and environmental health are crucial to ensure viable cities. We assessed the usefulness of the Air Pollution Tolerance Index (APTI) as a composite index of environmental health. Fine and coarse dust amount and elemental concentrations of Celtis occidentalis and Tilia europaea leaves were measured in June and September at three sampling sites (urban, × industrial, and rural) in Debrecen city (Hungary) to assess the usefulness of APTI. The correlation between APTI values and dust amount and elemental concentrations was also studied. Fine dust, total chlorophyll, and elemental concentrations were the most sensitive indicators of pollution. Based on the high chlorophyll and low elemental concentration of tree leaves, the rural site was the least disturbed by anthropogenic activities, as expected. We demonstrated that fine and coarse dust amount and elemental concentrations of urban tree leaves are especially useful for urban air quality monitoring. -
Bat Community Structure, Foraging Activity, and Evening Bat Roost
BAT COMMUNITY STRUCTURE, FORAGING ACTIVITY, AND EVENING BAT ROOST SITE SELECTION IN LOBLOLLY PINE AND LONGLEAF PINE FORESTS OF GEORGIA by ADAM CARL MILES (Under the Direction of Steven Castleberry) ABSTRACT During summers 2002 and 2003, I used mist nets, bat detectors, and radio-telemetry to investigate bat community structure, activity, and the day-roost selection of evening bats (Nycticeius humeralis) on mature longleaf and managed loblolly study sites in southwestern Georgia. The Seminole bat (Lasiurus seminolus), red bat (L. borealis), and evening bat were captured most frequently on each site. Bat activity was greater in mature pine than other habitats on the longleaf site, and activity was lesser in the hardwood habitat type on the managed site. Evening bats on the longleaf pine landscape selected roosts based on tree, plot, and landscape scale characteristics, while bats on the managed landscape selected roosts based on only the tree and plot characteristics. I hypothesized that the greater availability of roosting structures (abundant large trees and snags) on the longleaf site allowed evening bats to select roost sites that had more favorable landscape characteristics (i.e. closer to water and foraging sites). INDEX WORDS: Anabat, bat activity, bat community, bat detector, evening bat, habitat use, Nycticeius humeralis, radiotelemetry, roost selection, Southeast BAT COMMUNITY STRUCTURE, FORAGING ACTIVITY, AND EVENING BAT ROOST SITE SELECTION IN LOBLOLLY PINE AND LONGLEAF PINE FORESTS OF GEORGIA by ADAM C MILES B.S. Wildlife, Humboldt State University, 2001 A Thesis Submitted to the Graduate Faculty of The University of Georgia in Partial Fulfillment of the Requirements for the Degree MASTER OF SCIENCE ATHENS, GEORGIA 2005 © 2005 ADAM CARL MILES All Rights Reserved BAT COMMUNITY STRUCTURE, FORAGING ACTIVITY, AND EVENING BAT ROOST SITE SELECTION IN LOBLOLLY PINE AND LONGLEAF PINE FORESTS OF GEORGIA by ADAM CARL MILES Major Professor: Steven B. -
Random Sampling of the Central European Bat Fauna Reveals the Existence of Numerous Hitherto Unknown Adenoviruses+
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Repository of the Academy's Library Acta Veterinaria Hungarica 63 (4), pp. 508–525 (2015) DOI: 10.1556/004.2015.047 RANDOM SAMPLING OF THE CENTRAL EUROPEAN BAT FAUNA REVEALS THE EXISTENCE OF NUMEROUS + HITHERTO UNKNOWN ADENOVIRUSES 1* 2 3 1,4 Márton Z. VIDOVSZKY , Claudia KOHL , Sándor BOLDOGH , Tamás GÖRFÖL , 5 2 1 Gudrun WIBBELT , Andreas KURTH and Balázs HARRACH 1Institute for Veterinary Medical Research, Centre for Agricultural Research, Hungarian Academy of Sciences, Hungária krt. 21, H-1143 Budapest, Hungary; 2Robert Koch Institute, Centre for Biological Threats and Special Pathogens, Berlin, Germany; 3Aggtelek National Park Directorate, Jósvafő, Hungary; 4Department of Zoology, Hungarian Natural History Museum, Budapest, Hungary; 5Leibniz Institute for Zoo and Wildlife Research, Berlin, Germany (Received 16 September 2015; accepted 28 October 2015) From over 1250 extant species of the order Chiroptera, 25 and 28 are known to occur in Germany and Hungary, respectively. Close to 350 samples originating from 28 bat species (17 from Germany, 27 from Hungary) were screened for the presence of adenoviruses (AdVs) using a nested PCR that targets the DNA polymerase gene of AdVs. An additional PCR was designed and applied to amplify a fragment from the gene encoding the IVa2 protein of mastadenovi- ruses. All German samples originated from organs of bats found moribund or dead. The Hungarian samples were excrements collected from colonies of known bat species, throat or rectal swab samples, taken from live individuals that had been captured for faunistic surveys and migration studies, as well as internal or- gans of dead specimens.