Recommendations for Using the Subdermal Stitch Method to Attach External Transmitters on Snakes
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Species Diversity of Snakes in Pachmarhi Biosphere Reserve
& Herpeto gy lo lo gy o : h C it u n r r r e O Fellows, Entomol Ornithol Herpetol 2014, 4:1 n , t y R g e o l s o e Entomology, Ornithology & Herpetology: DOI: 10.4172/2161-0983.1000136 a m r o c t h n E ISSN: 2161-0983 Current Research ResearchCase Report Article OpenOpen Access Access Species Diversity of Snakes in Pachmarhi Biosphere Reserve Sandeep Fellows* Asst Conservator of forest, Madhya Pradesh Forest Department (Information Technology Wing), Satpura Bhawan, Bhopal (M.P) Abstract Madhya Pradesh (MP), the central Indian state is well-renowned for reptile fauna. In particular, Pachmarhi Biosphere Reserve (PBR) regions (Districts Hoshangabad, Betul and Chindwara) of MP comprises a vast range of reptiles, especially herpetofauna yet unexplored from the conservation point of view. Earlier inventory herpetofaunal study conducted in 2005 at MP and Chhattisgarh (CG) reported 6 snake families included 39 species. After this preliminary report, no literature existing regarding snake diversity of this region. This situation incited us to update the snake diversity of PBR regions. From 2010 to 2012, we conducted a detailed field study and recorded 31 species of 6 snake families (Boidae, Colubridae, Elapidae, Typhlopidea, Uropeltidae, and Viperidae) in Hoshanagbad District (Satpura Tiger Reserve) and PBR regions. Besides, we found the occurrence of Boiga forsteni and Coelognatus helena monticollaris (Colubridae), which was not previously reported in PBR region. Among the recorded, 9 species were Lower Risk – least concerned (LR-lc), 20 were of Lower Risk – near threatened (LR-nt), 1 is Endangered (EN) and 1 is vulnerable (VU) according to International Union for Conservation of Nature (IUCN) status. -
Behavioural And.Pdf
Published by Associazione Teriologica Italiana Volume 29 (2): 211–215, 2018 Hystrix, the Italian Journal of Mammalogy Available online at: http://www.italian-journal-of-mammalogy.it doi:10.4404/hystrix–00119-2018 Research Article Behavioural and population responses of ground-dwelling rodents to forest edges Maria Vittoria Mazzamuto∗, Lucas A. Wauters, Damiano G. Preatoni, Adriano Martinoli Environment Analysis and Management Unit, Guido Tosi Research Group, Department of Theoretical and Applied Sciences, University of Insubria, via J.-H. Dunant 3, 21100 Varese, Italy Keywords: Abstract bank vole wood mouse Forest edges can affect the behaviour, physiology and demography of small mammals. We tested survival whether there was a response in abundance, distribution, personality selection or foraging behaviour seed predation of ground-dwelling rodents to a forest–meadow edge in two study areas in Northern Italy over a 1- personality year period. We used capture-mark-recapture to evaluate species distribution, abundance, survival GUD and personality, while Giving-up Density was used to test their foraging behaviour and the cost associated to it. All tests were carried out on the forest edge and at 50 and 100 m from the edge along Article history: three parallel transects 90 m long. We detected two species in both areas: Apodemus sylvaticus Received: 8/06/2018 and Myodes glareolus. We found a neutral effect of the edge on species number, survival and on Accepted: 3/12/2018 individual’s personality (activity/exploration tendency). Bank voles occurred more along the edge and both taxa took more seeds from trays along the edge. The hypothesis of edge avoidance was not Acknowledgements confirmed in any of the variables examined. -
Herpetofaunistic Diversity of the Cres-Lošinj Archipelago (Croatian Adriatic)
University of Sopron Roth Gyula Doctoral School of Forestry and Wildlife Management Sciences Ph.D. thesis Herpetofaunistic diversity of the Cres-Lošinj Archipelago (Croatian Adriatic) Tamás Tóth Sopron 2018 Roth Gyula Doctoral School of Forestry and Wildlife Management Sciences Nature Conservation Program Supervisors: Prof. Dr. Faragó Sándor Dr. Gál János Introduction In recent years the Croatian islands, especially those of the Cres-Lošinj Archipelago became the focus of research of herpetologists. However, in spite of a long interest encompassing more than a hundred years, numerous gaps remain in our herpetological knowledge. For this reason, the author wished to contribute to a better understanding by performing studies outlined below. Aims The first task was to map the distribution of amphibians and reptiles inhabiting the archipelago as data were lacking for several of the smaller islands and also the fauna of the bigger islands was insufficiently known. Subsequently, the faunistic information derived from the scientific literature and field surveys conducted by the author as well as available geological and paleogeological data were compared and analysed from a zoogeographic point of view. The author wished to identify regions of the islands boasting the greatest herpetofaunal diversity by creating dot maps based on collecting localities. To answer the question which snake species and which individuals are going to be a victim of the traffic snake roadkill and literature survey were used. The author also identified where are the areas where the most snakes are hit by a vehicle on Cres. By gathering road-killed snakes and comparing their locality data with published occurrences the author seeked to identify species most vulnerable to vehicular traffic and road sections posing the greatest threat to snakes on Cres Island. -
6. Terrestrial Fauna
Moura Link - Aldoga Rail Project Queensland Rail Environmental Impact Statement Terrestrial fauna 6. Terrestrial fauna This section describes the existing environment, potential impacts and mitigation measures for the Project in terms of the terrestrial fauna values. The assessment has been based on a review of existing information and the outcomes of supporting field investigations. It should be noted that the information regarding legislation is current at the time of writing this section but may be subject to change in the future. Legislation requirements covered in the EIS have been cited from: • Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act) • Nature Conservation Act 1992 (NC Act) • Nature Conservation (Wildlife) Regulation 2006 (NC Regulation) • Vegetation Management Act 1999 (VM Act) • Land Protection (Pest and Stock Route Management) Act 2002 • Land Protection (Pest and Stock Route Management) Regulation 2003 The currency of such information will be checked during the detailed design phase of the Project and prior to commencement of construction activities within the project area. Currently the designation of threatened species under the NC Act and NC Regulation is being reviewed to conform with international classification and as such species listed as rare will be reassessed and classified as either least concern, vulnerable, near threatened, endangered or critically endangered. 6.1 Existing environment 6.1.1 Methodology In March 2007, Connell Hatch prepared a desktop ecological assessment to support the development of an Initial Advice Statement, EPBC Referral for determination of the Project’s controlled action status under the EPBC Act and ultimately assist in the EIS process. The Project was deemed a not controlled action under Section 75 of the EPBC Act. -
Charles Darwin University Death Adder Envenoming Causes
Charles Darwin University Death Adder Envenoming Causes Neurotoxicity Not Reversed by Antivenom - Australian Snakebite Project (ASP-16) Johnston, Christopher; O'Leary, Margaret; Brown, Simon; Currie, Bart; Halkidis, Lambros; Whitaker, Richard; Close, Benjamin; Isbister, Geof Published in: PLoS Neglected Tropical Diseases DOI: 10.1371/journal.pntd.0001841 Published: 01/01/2012 Document Version Publisher's PDF, also known as Version of record Link to publication Citation for published version (APA): Johnston, C., O'Leary, M., Brown, S., Currie, B., Halkidis, L., Whitaker, R., Close, B., & Isbister, G. (2012). Death Adder Envenoming Causes Neurotoxicity Not Reversed by Antivenom - Australian Snakebite Project (ASP-16). PLoS Neglected Tropical Diseases, 6(9), 1-8. https://doi.org/10.1371/journal.pntd.0001841 General rights Copyright and moral rights for the publications made accessible in the public portal are retained by the authors and/or other copyright owners and it is a condition of accessing publications that users recognise and abide by the legal requirements associated with these rights. • Users may download and print one copy of any publication from the public portal for the purpose of private study or research. • You may not further distribute the material or use it for any profit-making activity or commercial gain • You may freely distribute the URL identifying the publication in the public portal Take down policy If you believe that this document breaches copyright please contact us providing details, and we will remove access to the work immediately and investigate your claim. Download date: 03. Oct. 2021 Death Adder Envenoming Causes Neurotoxicity Not Reversed by Antivenom - Australian Snakebite Project (ASP-16) Christopher I. -
Indigenous Reptiles
Reptiles Sylvain Ursenbacher info fauna & NLU, Universität Basel pdf can be found: www.ursenbacher.com/teaching/Reptilien_UNIBE_2020.pdf Reptilia: Crocodiles Reptilia: Tuataras Reptilia: turtles Rep2lia: Squamata: snakes Rep2lia: Squamata: amphisbaenians Rep2lia: Squamata: lizards Phylogeny Tetrapoda Synapsida Amniota Lepidosauria Squamata Sauropsida Anapsida Archosauria H4 Phylogeny H5 Chiari et al. BMC Biology 2012, 10:65 Amphibians – reptiles - differences Amphibians Reptiles numerous glands, generally wet, without or with limited number skin without scales of glands, dry, with scales most of them in water, no links with water, reproduction larval stage without a larval stage most of them in water, packed in not in water, hard shell eggs tranparent jelly (leathery or with calk) passive transmission of venom, some species with active venom venom toxic skin as passive protection injection Generally in humide and shady Generally dry and warm habitats areas, nearby or directly in habitats, away from aquatic aquatic habitats habitats no or limited seasonal large seasonal movements migration movements, limited traffic inducing big traffic problems problems H6 First reptiles • first reptiles: about 320-310 millions years ago • embryo is protected against dehydration • ≈ 305 millions years ago: a dryer period ➜ new habitats for reptiles • Mesozoic (252-66 mya): “Age of Reptiles” • large disparition of species: ≈ 252 and 65 millions years ago H7 Mesozoic Quick systematic overview total species CH species (oct 2017) Order Crocodylia (crocodiles) -
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. -
Death Adder (Deaf Adder)
Death Adder (Deaf Adder) There are three major death adder species that occur in Australia, some more species have been described and named in Australia and are awaiting official acceptances; whatever that might mean. Death adders are found in all states of Australia excepting Victoria and Tasmania. In the early days of European settlement they were probably in Northern Victoria though perhaps no longer. Death adders also occur in New Guinea and some adjacent islands. The Common Death Adder (Acanthophis antarcticus) The Northern Death Adder (Acanthophis praelongus) The Desert Death Adder (Acanthophis pyrrhus) The death adder is not a true adder; it belongs to the family of snakes called the elapids (elapidae). Elapids are snakes that are usually described as having short, front fixed (not hinged) fangs. Death Adders are live bearers or viviparous (not egg layers). They never grow very long; a death adder of one meter in length would be classed as a monster. Their venom is primarily neurotoxic (effecting mostly the nervous system). The only antivenom to be used is specific Death Adder antivenom and in emergencies only would you use polyvalent antivenom (Australian universal antivenom). It is possible that the name Death Adder is a corruption of the term Deaf Adder. This snake was in days gone by, called also by this name. Most snakes in the world are totally deaf. The name given by the inhabitants of the Island of Crete to a snake is kouphos’, which means deaf in Greek, (kouphos’ is pronounced with the accent or emphasis on the last vowel). In Greek proper, a snake is called phidi and the plural is phidia. -
Black Rat Eradication on Italian Islands: Planning Forward by Looking Backward Black Rat Eradication on Italian Islands: Planning Forward by Looking Backward
D. Capizzi, P. Sposimo, G. Sozio, F. Petrassi, C. Gotti, E. Raganella Pelliccioni and N. Baccetti Capizzi, D.; P. Sposimo, G. Sozio, F. Petrassi, C. Gotti, E. Raganella Pelliccioni and N. Baccetti. Black rat eradication on Italian islands: planning forward by looking backward Black rat eradication on Italian islands: planning forward by looking backward D. Capizzi1, P. Sposimo2, G. Sozio1, F. Petrassi1, C. Gotti3, E. Raganella Pelliccioni3 and N. Baccetti3 1Regione Lazio, Direzione Capitale Naturale, parchi e Aree Protette, via del Pescaccio 96 - 00166 Rome, Italy. <[email protected]>. 2NEMO s.r.l., Piazza D’Azeglio 11 – 50121 Florence, Italy. 3Istituto Superiore per la Protezione e la Ricerca Ambientale, via Ca’ Fornacetta 9 – 40064 Ozzano dell’Emilia (BO), Italy. Abstract Since 1999, the black rat (Rattus rattus) has been eradicated from 14 Italian islands, and eradication is ongoing on a further five islands. Most projects were funded by the European Union (EU) Life Programme. Over the years, eradication techniques have been improved and adapted to different situations, including aerial bait distribution on islands with large inaccessible areas, which otherwise would have relied on a manual bait distribution. A priority list of eradications on islands, which was compiled ten years ago, has been met to a large extent, as rats have been successfully eradicated from many islands of great importance to breeding seabirds. Despite some cases of re-invasion occurring in early projects, advances in biosecurity measures have allowed for eradications on islands where this was previously considered unfeasible due to a high risk of re-invasion. This paper reports on black rat eradication work performed on Italian Mediterranean islands with small villages. -
The Contribution to Wildlife Conservation of an Italian Recovery
Nature Conservation 44: 1–20 (2021) A peer-reviewed open-access journal doi: 10.3897/natureconservation.44.65528 RESEARCH ARTICLE https://natureconservation.pensoft.net Launched to accelerate biodiversity conservation The contribution to wildlife conservation of an Italian Recovery Centre Gabriele Dessalvi1, Enrico Borgo2, Loris Galli1 1 Department of Earth, Environmental and Life Sciences (DISTAV), Genoa University, Corso Europa 26, 16132, Genoa, Italy 2 Museum of Natural History “Giacomo Doria”, Via Brigata Liguria, 9, 16121, Genoa, Italy Corresponding author: Loris Galli ([email protected]) Academic editor: Christoph Knogge | Received 5 March 2021 | Accepted 20 April 2021 | Published 10 May 2021 http://zoobank.org/F5D4BBF2-A839-4435-A1BA-83EAF4BA94A9 Citation: Dessalvi G, Borgo E, Galli L (2021) The contribution to wildlife conservation of an Italian Recovery Centre. Nature Conservation 44: 1–20. https://doi.org/10.3897/natureconservation.44.65528 Abstract Wildlife recovery centres are widespread worldwide and their goal is the rehabilitation of wildlife and the subsequent release of healthy animals to appropriate habitats in the wild. The activity of the Genoese Wild- life Recovery Centre (CRAS) from 2015 to 2020 was analysed to assess its contribution to the conservation of biodiversity and to determine the main factors affecting the survival rate of the most abundant species. In particular, the analyses focused upon the cause, provenance and species of hospitalised animals, the sea- sonal distribution of recoveries and the outcomes of hospitalisation in the different species. In addition, an in-depth analysis of the anthropogenic causes was conducted, with a particular focus on attempts of preda- tion by domestic animals, especially cats. -
Snake Venom Potency and Yield Are Associated with Prey-Evolution, Predator Metabolism and Habitat Structure
Snake venom potency and yield are associated with prey-evolution, predator metabolism and habitat structure Kevin Healy a, b, c, *, Chris Carbone d and Andrew L. Jackson a. a Department of Zoology, School of Natural Sciences, Trinity College Dublin, Dublin 2, Ireland. b School of Biology, University of St Andrews, St Andrews KY16 9TH, UK. c School of Natural Sciences, National University of Ireland Galway, Galway, Republic of Ireland. d Institute of Zoology, Zoological Society of London, London, UK * Corresponding author: [email protected], School of Biology, University of St Andrews, St Andrews KY16 9TH, UK. Short running title Macroecological factors drive venom evolution Article type: Letters Number of words in abstract: 150 Number of words in main text: 4984 Number of references: 73 Number of Figures: 4 Statement of authorship KH collated the dataset and conducted the analysis. All authors contributed to the analysis, design, discussion and interpretation of the results, and writing of the manuscript. Data accessibility statement Data available from the Figshare Digital Repository https://doi.org/10.6084/m9.figshare.7128566.v1 Keywords Venom, Body size, Comparative analysis, Scaling, trophic ecology, Macroecology, LD50, Phylogenetic analysis, Snake, Abstract Snake venom is well known for its ability to incapacitate and kill prey. Yet, potency and the amount of venom available varies greatly across species, ranging from the seemingly harmless to those capable of killing vast numbers of potential prey. This variation is poorly understood, with comparative approaches confounded by the use of atypical prey species as models to measure venom potency. Here, we account for such confounding issues by incorporating the phylogenetic similarity between a snake’s diet and the species used to measure its potency. -
Hierophis Viridiflavus
Hierophis viridiflavus Region: 3 Taxonomic Authority: (Lacépède, 1789) Synonyms: Common Names: Hierophis gyarosensis (Mertens, 1968) Western Whip Snake English Green Whip Snake English Gelbgrüne Zornnatter German Culebra Verdiamarilla Spanish biacco Italian Order: Ophidia Family: Colubridae Notes on taxonomy: This species was formerly included in the genus Coluber, but is included here in Hierophis following Schätti and Utiger (2001) and Nagy et al. (2004). Nagy et al. (2002) showed that the subspecies H. viridiflavus carbonarius is probably a different evolutionary unit from H.v. viridiflavus. The synonym Hierophis gyarosensis (known only from the island of Gyaros (Greece)) is actually a translocation of H.v. carbonarius (Schätti, in press). General Information Biome Terrestrial Freshwater Marine Geographic Range of species: Habitat and Ecology Information: This species ranges from northeastern Spain; western, southern, It is found in dry, open, well vegetated habitats. It occurs in scrubland, eastern and northeastern France; and southern Switzerland, through macchia, open woodland (deciduous and mixed), heathland, cultivated most of Italy, to southwestern Slovenia and northern Croatia. It is areas, dry river beds, rural gardens, roads, stone walls and ruins. The present on the Mediterranean islands of Corsica (France), Sardinia, species lays four to 15 eggs. Sicily and most other Italian islands, Krk (Croatia), and Malta. The species may occur in Luxembourg, but this requires verification. The species is absent from Austria. It has also been translocated to the island of Gyaros (Greece) in the Aegean Sea where it was described as a new species but it is now considered to be a synonym. It ranges from sea level up to 2,000m asl.