Annotated Checklist of the Recent and Extinct Pythons (Serpentes, Pythonidae), with Notes on Nomenclature, Taxonomy, and Distribution
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Koolan Island Quoll Demographics & Genetics
Running head: Conservation status of the Olive Python Final report GENETIC SURVEY OF THE PILBARA OLIVE PYTHON (Liasis olivaceaus barroni) David Pearson1, Peter Spencer2 Mia Hillyer2 and Ric A. How3 1Science Division, Department of Parks and Wildlife PO Box 51, Wannerooo, WA 6946 2School of Veterinary and Life Sciences, Murdoch University 90 South St, Murdoch, WA 6150 3Department of Terrestrial Zoology (Vertebrates), Western Australian Museum, 49 Kew St, Welshpool, WA 6986 September, 2013 Olive python – final report 1 Running head: Conservation status of the Olive Python Summary • The study used genetic information to investigate differences between and within populations of olive pythons in the Pilbara. This information was compared with genetic profiles from olive pythons form the Kimberley and carpet pythons. • Genetic variation was examined at eight nuclear genes (microsatellite) from 47 individual olive pythons. • Genetic analyses of nuclear markers show that the Pilbara olive python contains low levels of diversity, compared with its Kimberley counterpart. • The Pilbara population also had a low effective population size, but showed no signatures of a genetic bottleneck as a result of a population crash. • Nuclear DNA markers identified two distinct olive python populations. One in the Pilbara and the other in the Kimberley. • Mitochondrial analysis at three diagnostic regions showed two distinct clades representing Pilbara and Kimberley olive pythons, exclusively, consistent with results from nuclear markers. • Overall olive pythons appear to have two Evolutionary Significant Units. The Pilbara unit appear to be less genetically diverse than Kimberley one and shows little phylogeographic structure within the Pilbara. • There is sufficient evidence from the data that the taxonomy of the two groups should be subject to a re-appraisal, the Kimberley and Pilbara Olive pythons sufficiently different to be considered as different species. -
Flora and Fauna Survey June 2018
Burrup Peninsula Interconnector Pipeline Flora and Fauna Survey June 2018 Prepared for DDG Operations Pty Ltd Report Reference: 21244-18-BISR-1Rev0_180803 This page has been left blank intentionally. Burrup Peninsula Interconnector Pipeline Flora and Fauna Survey Prepared for DDG Operations Pty Ltd Job Number: 21244-18 Reference: 21244-18-BISR-1Rev0_180803 Revision Status Rev Date Description Author(s) Reviewer B. Jeanes A 20/07/2018 Draft Issued for Client Review H. Warrener J. Atkinson J. Johnston B. Jeanes 0 03/08/2018 Final Issued for Information H. Warrener J. Atkinson J. Johnston Approval Rev Date Issued to Authorised by Name Signature A 20/07/2018 M. Goodwin R. Archibald 0 03/08/2018 M. Goodwin S. Pearse © Copyright 2018 Astron Environmental Services Pty Ltd. All rights reserved. This document and information contained in it has been prepared by Astron Environmental Services under the terms and conditions of its contract with its client. The report is for the clients use only and may not be used, exploited, copied, duplicated or reproduced in any form or medium whatsoever without the prior written permission of Astron Environmental Services or its client. DDG Operations Pty Ltd Burrup Peninsula Interconnector Pipeline – Flora and Fauna Survey, June 2018 Abbreviations Abbreviation Definition Astron Astron Environmental Services BAM Biosecurity and Agriculture Management Act 2007 DBNGP Dampier Bunbury Natural Gas Pipeline DBCA Department of Biodiversity, Conservation and Attractions DEC Department of Environment and Conservation -
Investigations Into the Presence of Nidoviruses in Pythons Silvia Blahak1, Maria Jenckel2,3, Dirk Höper2, Martin Beer2, Bernd Hoffmann2 and Kore Schlottau2*
Blahak et al. Virology Journal (2020) 17:6 https://doi.org/10.1186/s12985-020-1279-5 RESEARCH Open Access Investigations into the presence of nidoviruses in pythons Silvia Blahak1, Maria Jenckel2,3, Dirk Höper2, Martin Beer2, Bernd Hoffmann2 and Kore Schlottau2* Abstract Background: Pneumonia and stomatitis represent severe and often fatal diseases in different captive snakes. Apart from bacterial infections, paramyxo-, adeno-, reo- and arenaviruses cause these diseases. In 2014, new viruses emerged as the cause of pneumonia in pythons. In a few publications, nidoviruses have been reported in association with pneumonia in ball pythons and a tiger python. The viruses were found using new sequencing methods from the organ tissue of dead animals. Methods: Severe pneumonia and stomatitis resulted in a high mortality rate in a captive breeding collection of green tree pythons. Unbiased deep sequencing lead to the detection of nidoviral sequences. A developed RT-qPCR was used to confirm the metagenome results and to determine the importance of this virus. A total of 1554 different boid snakes, including animals suffering from respiratory diseases as well as healthy controls, were screened for nidoviruses. Furthermore, in addition to two full-length sequences, partial sequences were generated from different snake species. Results: The assembled full-length snake nidovirus genomes share only an overall genome sequence identity of less than 66.9% to other published snake nidoviruses and new partial sequences vary between 99.89 and 79.4%. Highest viral loads were detected in lung samples. The snake nidovirus was not only present in diseased animals, but also in snakes showing no typical clinical signs. -
Aspidites Melanocephalus) in the Wild
Northern Territory Naturalist (2019) 29: 37-39 Short Note An observation of excavating behaviour by a Black-headed Python (Aspidites melanocephalus) in the wild Gerry Swan1 and Christy Harvey2 12 Acron Road, St Ives, NSW 2075, Australia Email: [email protected] 216 Fleetwood Cres, Frankston South, VIC 3199, Australia Abstract The Black-headed Python (Aspidites melanocephalus) and the Woma (Aspidites ramsayi) have both been reported as carrying out burrowing or excavating behaviour. These reports have been based mainly on observations of captive individuals, with the only observations of specimens in the wild being those of Bruton (2013) on Womas. Here we report on a Black-headed Python scooping out sand with its head and fore-body to create a depression in the wild. The pythonid genus Aspidites has been reported as exhibiting burrowing behaviour (Ross & Marzec 1990; Ehmann 1993; Barker & Barker 1994), based mainly on the report by Murphy, Lamoreaux & Barker (1981) that four captive Black-headed Pythons (A. melanocephalus) excavated gravel by using their head and neck to scoop loose material and create a cavity. O’Brien & Naylor (1987) reported that a young specimen that had been recently removed from the wild and was being held pending release, was observed digging beneath rocks and logs, ultimately creating a cavity in which it concealed itself. Fyfe & Harvey (1981) recorded similar behaviour by six captive Womas (Aspidites ramsayi). The floor of the vivaria in which they were housed was covered with 5–15 cm of sand and the pythons scooped this out in large quantities until they reached the base of the vivarium. -
Pest Risk Assessment
PEST RISK ASSESSMENT Antaresia spp. (Children‟s Pythons) Antaresia childreni (Children's Python) Antaresia stimsoni (Stimson's Python) Antaresia maculosa (Spotted Python) Photo: Scarlet23. Image from Wikimedia Commons under a GNU Free Documentation License, Version 1.2) December 2011 Department of Primary Industries, Parks, Water and Environment Resource Management and Conservation Division Department of Primary Industries, Parks, Water and Environment 2011 Information in this publication may be reproduced provided that any extracts are acknowledged. This publication should be cited as: DPIPWE (2011) Pest Risk Assessment: Children’s Pythons (Antaresia childreni, A. stimsoni, A. maculosa). Department of Primary Industries, Parks, Water and Environment. Hobart, Tasmania. About this Pest Risk Assessment This pest risk assessment is developed in accordance with the Policy and Procedures for the Import, Movement and Keeping of Vertebrate Wildlife in Tasmania (DPIPWE 2011). The policy and procedures set out conditions and restrictions for the importation of controlled animals pursuant to S32 of the Nature Conservation Act 2002. This pest risk assessment is prepared by DPIPWE for use within the Department. For more information about this Pest Risk Assessment, please contact: Wildlife Management Branch Department of Primary Industries, Parks, Water and Environment Address: GPO Box 44, Hobart, TAS. 7001, Australia. Phone: 1300 386 550 Email: [email protected] Visit: www.dpipwe.tas.gov.au Disclaimer The information provided in this Pest Risk Assessment is provided in good faith. The Crown, its officers, employees and agents do not accept liability however arising, including liability for negligence, for any loss resulting from the use of or reliance upon the information in this Pest Risk Assessment and/or reliance on its availability at any time. -
Israel's System for Risk Assessment of Imported Wildlife for the Pet Trade
Israel ’s System for Risk Assessment of Imported Wildlife for the Pet Trade Dr. Simon Nemtzov Israel Nature and Parks Authority Jerusalem, Israel [email protected] 1 Univ. Notre Dame – April 2008 Israel is especially susceptible to invasive species because of its rich diversity of habitats and ecosystems. Why does Israel have such a high level of biodiversity? Species per m 2 in Mediterranean countries Eurostat 2008 2 1 EUROPE ASIA AFRICA 3 Biogeography of Israel Northern Israel: – Mediterranean ecosystem – Up to 1000 mm rainfall Central Israel Iraq – Dense urban population Israel Southern Israel: – Sudanese desert ecosystem – < 100 mm rainfall – Relatively low human impact Saudi Arabia 40 miles / 60 km 4 2 Israel ’s geographic factors Small area: ~21,700 km 2 (~ 8,400 sq mi) – (about the size of New Jersey) Intersection of 3 continents: – Asia, Africa and Europe – 4 biogeographical regions: Rich diversity of ecotones and biota Sea of Galilee - Lake Kinneret 5 Wildlife biodiversity in Israel 16 species of Carnivores: Striped hyena (Hyena hyena ) 5 species of canids: wolf (Canis lupus ), 3 foxes, golden jackal (C. aureus ) 5 sp. of mustelids : 2 badgers, beech marten, marbled polecat, otter (Lutra lutra ) Egyptian mongoose (Herpestes ichneumon ) 4 species of felids 6 3 Wildlife biodiversity in Israel 4 species of felids: Caracal (Felis caracal ) Leopard (Panthera pardus ) Wild cat (Felis silvestris ) Jungle cat (Felis chaus ) (Sand cat (Felis margarita) ) 7 Risk Assessment Procedure Simplified system based on Australia ’s system (Bomford 1991, 2003) Importer requests an import permit from INPA No application fee! INPA ecologist collects biological data (answers “The Questions ”), prepares opinion, and assigns initial risk category (H / M / L) 3 ecologist referees → Consensus category Coypu 8 4 The risk assessment questions 1. -
A Rapid Survey of Online Trade in Live Birds and Reptiles in The
S H O R T R E P O R T 0ൾඍඁඈൽඌ A rapid online survey was undertaken EHWZHHQDQG)HEUXDU\ GD\V DSSUR[LPDWHO\KRXUVVXUYH\GD\ RQ pre-selected Facebook groups specializing in the trade of live pets. Ten groups each for reptiles and birds were selected based on trading activities in the previous six months. The survey was carried out during ZHHN GD\V 0RQGD\ WR )ULGD\ E\ JRLQJ through each advertisement posted in A rapid survey of online trade in the groups. Information, including that live birds and reptiles in the Philippines relating to species, quantity, and asking HYDROSAURUS PUSTULATUS WWF / URS WOY WOY WWF / URS PUSTULATUS HYDROSAURUS SULFH ZDV QRWHG 6SHFLHV ZHUH LGHQWL¿HG Report by Cristine P. Canlas, Emerson Y. Sy, to the lowest taxonomic level whenever and Serene Chng possible. Taxonomy follows Gill and 'RQVNHU IRU ELUGV DQG 8HW] et al. IRUUHSWLOHV7KHDXWKRUVFDOFXODWHG ,ඇඍඋඈൽඎർඍංඈඇ WKH WRWDO SRWHQWLDO YDOXH R൵HUHG IRU ELUGV and reptiles based on prices indicated he Philippines is the second largest archipelago in the world by traders. Advertisements that did not comprising 7641 islands and is both a mega-biodiverse specify prices were assigned the lowest country for harbouring wildlife species found nowhere known price for each taxon. Valuations in else in the world, and one of eight biodiversity hotspots this report were based on a conversion rate having a disproportionate number of species threatened with RI86' 3+3 $QRQ ,WLV ,//8675$7,213+,/,33,1(6$,/),1/,=$5' TH[WLQFWLRQIXUWKHULWKDVVRPHRIWKHKLJKHVWUDWHVRIHQGHPLFLW\LQWKH not always possible during online surveys world (Myers et al 7KHLOOHJDOZLOGOLIHWUDGHLVRQHRIWKHPDLQ WRYHULI\WKDWDOOR൵HUVDUHJHQXLQH UHDVRQVEHKLQGVLJQL¿FDQWGHFOLQHVRIVRPHZLOGOLIHSRSXODWLRQVLQ$VLD LQFOXGLQJWKH3KLOLSSLQHV $QRQ6RGKLet al1LMPDQDQG 5ൾඌඎඅඍඌ 6KHSKHUG'LHVPRVet al5DRet al 7KHWildlife Act of 2001 (Republic Act No. -
AC27 Inf. 17 (Rev.1) (English Only / Únicamente En Inglés / Seulement En Anglais)
AC27 Inf. 17 (Rev.1) (English only / únicamente en inglés / seulement en anglais) CONVENTION ON INTERNATIONAL TRADE IN ENDANGERED SPECIES OF WILD FAUNA AND FLORA ____________ Twenty-seventh meeting of the Animals Committee Veracruz (Mexico), 28 April – 3 May 2014 INSPECTION MANUAL FOR USE IN COMMERCIAL REPTILE BREEDING FACILITIES IN SOUTHEAST ASIA 1. The attached information document has been submitted by the Secretariat and has been prepared by TRAFFIC* in relation to agenda item 9. * The geographical designations employed in this document do not imply the expression of any opinion whatsoever on the part of the CITES Secretariat or the United Nations Environment Programme concerning the legal status of any country, territory, or area, or concerning the delimitation of its frontiers or boundaries. The responsibility for the contents of the document rests exclusively with its author. AC27 Doc. 17 (Rev.1) – p. 1 Inspection Manual for use in Commercial Reptile Breeding Facilities in Southeast Asia EU- CITES Capacity - building project N o . S - 408 2013 CITES Secretariat About the EU-CITES Capacity-building project The project Strengthening CITES implementation capacity of developing countries to ensure sustainable wildlife management and non-detrimental trade was approved for funding by the European Union in 2009. A major challenge for many countries is the difficulty in meeting the requirements for trade in CITES-listed species, ranging from legal sourcing and sustainability requirements, to the effective control of legal trade and deterrence of illegal trade. Mechanisms exist in CITES and in both exporting and importing countries that promote and facilitate compliance – although Parties are often hampered by a lack of capacity or a lack of current biological or trade information with respect to certain species. -
The Discovery of XY Sex Chromosomes in a Boa and Python
Current Biology, Volume 27 Supplemental Information The Discovery of XY Sex Chromosomes in a Boa and Python Tony Gamble, Todd A. Castoe, Stuart V. Nielsen, Jaison L. Banks, Daren C. Card, Drew R. Schield, Gordon W. Schuett, and Warren Booth Figure S1. PCR validation of male-specific RAD markers in boa and python. Related to Figure 1. A. Male-biased amplification of RAD marker TCBoa_2918 in eleven male and eleven female Boa imperator. Individual specimen ID numbers are listed below the gel image. B. Male-biased amplification of RAD marker TCBoa_2918 in an additional eight male and eleven female Boa imperator. Individual specimen ID numbers are listed below the gel image. C. Photograph of South American Boa (Boa constrictor) from Goiás, Brazil. D. Male-biased amplification of RAD marker TCBoa_2918 in three male and three female Boa constrictor. Individual specimen ID numbers are listed below the gel image. E. Male-biased amplification of RAD marker M3 in twelve male and twelve female Python bivittatus. Individual specimen ID numbers are listed below the gel image in panel F. F. Male-specific restriction digest of PCR amplicon (PCR-RFLP) from RAD marker M10 in twelve male and twelve female Python bivittatus. Individual specimen ID numbers are listed below the gel image. G. Cartoon illustrating PCR amplicons from the python RAD marker M10. The X and Y alleles are illustrated including the approximate position of the Y chromosome-specific SpeI restriction site. H. Gel image of python RAD marker M10 showing difference between digested and undigested PCR amplicons from a male Python bivittatus. -
Aspidites Melanocephalus
Husbandry Manual For Black Headed Python Aspidites melanocephalus (Reptilia: Boidae) Compiler: Chris Mann Date of Preparation: Western Sydney Institute of TAFE, Richmond Course Name and Number: Lecturer: Graeme Phipps/Andrew Titmuss/Jacki Salkeld TABLE OF CONTENTS 1 INTRODUCTION............................................................................................................................... 5 2 TAXONOMY ...................................................................................................................................... 6 2.1 NOMENCLATURE .......................................................................................................................... 6 2.2 SUBSPECIES .................................................................................................................................. 6 2.3 RECENT SYNONYMS ..................................................................................................................... 6 2.4 OTHER COMMON NAMES ............................................................................................................. 6 3 NATURAL HISTORY ....................................................................................................................... 7 3.1 MORPHOMETRICS ......................................................................................................................... 7 3.1.1 Mass And Basic Body Measurements ..................................................................................... 7 3.1.2 Sexual Dimorphism ................................................................................................................ -
Inclusion Body Disease in Australian Snakes Jun 2013
Inclusion body disease in Australian snakes Fact sheet Introductory statement Inclusion body disease (IBD) is an important disease of snakes because of its 100% mortality rate and lack of definite knowledge regarding epidemiology, diagnosis, treatment and prevention. While IBD appears to be present in captive Australian snakes its diagnosis is still extremely problematic. Until recently diagnosis was purely histological, determined by the presence of inclusion bodies. However, inclusion bodies are not specific to IBD and are found in many viral infections. It seems entirely plausible that at least some of the snakes diagnosed with IBD were infected with a different virus. Recently arenavirus has been identified in snakes with IBD. A diagnostic test is now available in Australia. The effect of IBD on wild Australian snake populations is unknown as the IBD status of Australia’s snakes, captive and free living, is also unknown. Aetiology Previously it was thought that IBD may be caused by a virus of the family Retroviridae (Schumacher et al. 1994). Although retroviruses have been isolated from affected snakes it has not been shown definitely that they were the cause of the disease (Jacobson et al. 2001). More recently researchers have found arenaviruses in six out of eight snakes diagnosed with IBD in the USA and eight IBD positive snakes examined in The Netherlands. These findings led the authors to speculate that arenavirus may be the causative agent of IBD (Stenglein et al. 2012; Bodewes et al. 2013). Natural hosts IBD is mainly a disease of the family Boidae (boas and pythons) but cases have also been described in an eastern kingsnake (Lampropeltis getulus), and a collection of palm vipers (Bothriechis marchi) (Raymond et al. -
Woma Python and Inland Taipan
Government of South Australia South Australian Arid Lands Natural Resources Management Board STUDENT WOMA PYTHON FACT SHEET Aspidites Ramsayi The Woma Python is a nocturnal snake that is Australia have come from sandy areas in the usually quiet and shy, mostly seen at dusk or north-east of the state, predominantly along the during warmer nights. It is rarely seen and has a Birdsville and Strzelecki Tracks. patchy distribution in South Australia, mostly in the north-east of the state. It eats lizards, snakes, Marla birds and small mammals (including dingo pups Oodnadatta and young rabbits). Woma Pythons wiggle their tail to distract initially cautious prey and then attract it to within striking distance. The python then coils around the prey, constricting it until it finally dies. Ceduna Port Augusta IDENTIFICATION The Woma Python can grow to 2.7 metres in Distribution Distribution total length and weigh up to 5.8kg. The body is ADELAIDE a yellowish brown to yellowish white with many wavy brownish bands that join along the back. Juveniles are more prominently patterned and POTENTIAL THREATS TO coloured than older animals. WOMA PYTHONS Land clearance and introduced predators have Woma Pythons can be confused with the Mulga resulted in significant declines of the Woma (King Brown) Snake or Western Brown Snakes. Python in central northern New South Wales Woma Pythons can be distinguished by the shape and the south east of Queensland, and is near of the head, which is rounded near the eyes but extinction in southwestern Western Australia. narrower at the snout. Woma Pythons compete with cats and foxes and DISTRIBUTION AND HABITAT may also be eaten by these species, particularly Woma Pythons are found in desert dunefields and when the snakes are still young and small.