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Conserviing Fiordland's Biodiversity 1987-2015 Part 3
Ecosystem response to pest control Flora and plant communities • Recognition and documentation of the flora, vegetation and wider ecological values of the Since 1987, considerable effort – both planned and Fiordland / Te Anau Basin area. opportunistic – has gone into surveying threatened • Identification of national strongholds for heart-leaved flora (plant species) and vegetation in general (plant kōhūhū, the shrub Melicytus flexuosus, the tree daisy communities) in Fiordland. This region is not only Olearia lineata and small-leaved coprosma in Back floristically significant nationally, but is also an important Valley. stronghold for several threatened species. • Recognition that the lakeshore turfs found around 11 Around 1000 vascular plant taxa are thought to occur Lakes Manapouri and Te Anau are among the in Fiordland, which makes the region much richer, most significant plant habitats in Fiordland (these ecologically, than previously understood. The Fiord communities are a national stronghold for several Ecological Region contains 11 species classified (under plant species). the New Zealand Threat Classification System) as • Protection of the Dale bog pine area as Dale Threatened, 96 as At Risk, 2 as Vagrant and 5 as Data Conservation Area. Deficient – and several of these have their national stronghold within Fiordland. Nationally important • Retirement of the Mavora Lakes and Eglinton Valley populations of some species classified as Naturally from grazing. Uncommon also occur. Fiordland is also known to be an • Working with community groups to restore and important region for endemism, with 24 taxa endemic manage important ecological values (notably to Fiordland, 11 near-endemic and a further 13 restricted Pomona Island Charitable Trust, Te Puka-Hereka/ to southern New Zealand. -
Literature Cited in Lizards Natural History Database
Literature Cited in Lizards Natural History database Abdala, C. S., A. S. Quinteros, and R. E. Espinoza. 2008. Two new species of Liolaemus (Iguania: Liolaemidae) from the puna of northwestern Argentina. Herpetologica 64:458-471. Abdala, C. S., D. Baldo, R. A. Juárez, and R. E. Espinoza. 2016. The first parthenogenetic pleurodont Iguanian: a new all-female Liolaemus (Squamata: Liolaemidae) from western Argentina. Copeia 104:487-497. Abdala, C. S., J. C. Acosta, M. R. Cabrera, H. J. Villaviciencio, and J. Marinero. 2009. A new Andean Liolaemus of the L. montanus series (Squamata: Iguania: Liolaemidae) from western Argentina. South American Journal of Herpetology 4:91-102. Abdala, C. S., J. L. Acosta, J. C. Acosta, B. B. Alvarez, F. Arias, L. J. Avila, . S. M. Zalba. 2012. Categorización del estado de conservación de las lagartijas y anfisbenas de la República Argentina. Cuadernos de Herpetologia 26 (Suppl. 1):215-248. Abell, A. J. 1999. Male-female spacing patterns in the lizard, Sceloporus virgatus. Amphibia-Reptilia 20:185-194. Abts, M. L. 1987. Environment and variation in life history traits of the Chuckwalla, Sauromalus obesus. Ecological Monographs 57:215-232. Achaval, F., and A. Olmos. 2003. Anfibios y reptiles del Uruguay. Montevideo, Uruguay: Facultad de Ciencias. Achaval, F., and A. Olmos. 2007. Anfibio y reptiles del Uruguay, 3rd edn. Montevideo, Uruguay: Serie Fauna 1. Ackermann, T. 2006. Schreibers Glatkopfleguan Leiocephalus schreibersii. Munich, Germany: Natur und Tier. Ackley, J. W., P. J. Muelleman, R. E. Carter, R. W. Henderson, and R. Powell. 2009. A rapid assessment of herpetofaunal diversity in variously altered habitats on Dominica. -
Oligosoma Ornatum; Reptilia: Scincidae) Species Complex from Northern New Zealand
Zootaxa 3736 (1): 054–068 ISSN 1175-5326 (print edition) www.mapress.com/zootaxa/ Article ZOOTAXA Copyright © 2013 Magnolia Press ISSN 1175-5334 (online edition) http://dx.doi.org/10.11646/zootaxa.3736.1.2 http://zoobank.org/urn:lsid:zoobank.org:pub:B7D72CD9-BE5D-4603-8BC0-C9FA557C7BEE Taxonomic revision of the ornate skink (Oligosoma ornatum; Reptilia: Scincidae) species complex from northern New Zealand GEOFF B. PATTERSON1,5, ROD A. HITCHMOUGH2 & DAVID G. CHAPPLE3,4 1149 Mairangi Road, Wilton, Wellington, New Zealand 2Department of Conservation, Terrestrial Conservation Unit, PO Box 10-420, Wellington 6143, New Zealand 3School of Biological Sciences, Monash University, Clayton Victoria 3800, Australia 4Allan Wilson Centre for Molecular Ecology and Evolution, School of Biological Sciences, Victoria University of Wellington, P.O. Box 600, Wellington 6140, New Zealand 5Corresponding author. E-mail: [email protected] Abstract Although the New Zealand skink fauna is known to be highly diverse, a substantial proportion of the recognised species remain undescribed. We completed a taxonomic revision of the ornate skink (Oligosoma ornatum (Gray, 1843)) as a pre- vious molecular study indicated that it represented a species complex. As part of this work we have resolved some nomen- clatural issues involving this species and a similar species, O. aeneum (Girard, 1857). A new skink species, Oligosoma roimata sp. nov., is described from the Poor Knights Islands, off the northeast coast of the North Island of New Zealand. This species is diagnosed by a range of morphological characters and genetic differentiation from O. ornatum. The con- servation status of the new taxon appears to be of concern as it is endemic to the Poor Knights Islands and has rarely been seen over the past two decades. -
Whakamana Te Waituna Biodiversity Plan
WHAKAMANA TE WAITUNA BIODIVERSITY PLAN R4701 WHAKAMANA TE WAITUNA BIODIVERSITY PLAN Wire rush rushland amongst mānuka shrubland, near Waituna Lagoon Road. Contract Report No. 4701 February 2019 Project Team: Kelvin Lloyd - Project management Nick Goldwater - Report author Carey Knox - Report author Helen McCaughan - Report author Steve Rate - Report author Fiona Wilcox - Report author Prepared for: Whakamana te Waituna Charitable Trust DUNEDIN OFFICE: 764 CUMBERLAND STREET, DUNEDIN 9016 Ph 03-477-2096, 03-477-2095 HEAD OFFICE: 99 SALA STREET, P.O. BOX 7137, TE NGAE, ROTORUA Ph 07-343-9017; Fax 07-343-9018, email [email protected], www.wildlands.co.nz CONTENTS 1. INTRODUCTION 1 2. PROJECT OBJECTIVE 3 3. PROJECT SCOPE 3 4. METHODS 3 5. CULTURAL CONTEXT 4 6. ECOLOGICAL CONTEXT 5 6.1 Waituna Ecological District 5 6.2 Waterways 5 6.3 Protected Natural Areas 7 6.4 Unprotected natural areas 8 6.5 Threatened land environments 8 6.6 Vegetation and habitats 10 6.7 Overview 10 6.8 Wetland vegetation 10 6.9 Terrestrial vegetation 12 6.10 Other vegetation/habitat types 12 6.11 Naturally uncommon ecosystem types 15 7. FLORA 16 7.1 Indigenous species 16 8. FAUNA 18 8.1 Overview 18 8.2 Birds 18 8.3 Lizards 20 8.4 Aquatic fauna 23 8.5 Terrestrial invertebrates 26 9. THREATS TO ECOLOGICAL VALUES 27 9.1 Overview 27 9.2 Land-based activities 27 9.2.1 Excessive catchment inputs of sediment, nutrients, and pathogens 27 9.2.2 Indigenous vegetation clearance 27 9.2.3 Hydrological modification 27 9.2.4 Stock 28 9.2.5 Other adverse activities 28 9.3 Natural phenomena 28 9.3.1 Fire 28 9.3.2 Sea level rise 29 9.4 Effects at landscape scale 29 9.5 Pest animals and plants 29 9.5.1 Pest animals 29 9.5.2 Pest plants 30 © 2019 Contract Report No. -
ASH Newsletter 47 E.Pub
THE AUSTRALIAN SOCIETY OF HERPETOLOGISTS INCORPORATED NEWSLETTER 47 2 History of Office Bearers Formation Committee (April 1964):- MJ Littlejohn (Convenor); State Reps IR Straughan (Qld), FJ Mitch- ell (SA), HG Cogger (NSW), G Storr (WA), RE Barwick (ACT), JW Warren (Vic), AK Lee (Editor). First AGM (23 August 1965):- President MJ Littlejohn, Vice-President NG Stephenson, Secretary- Treasurer AA Martin, Asst Secretary-Treasurer KJ Wilson, Ordinary Members FJ Mitchell and IR Strau- ghan, Editor AK Lee. PRESIDENT:- MJ Littlejohn (1965-69); AK Lee (1969-70); HG Cogger (1971-73); J de Bavay (1974); H Heatwole (1975-76); GC Grigg (1976-77); MJ Tyler (1978-79); GF Watson (1979-81); AA Martin (1981- 82); RS Seymour (1982-83); R Shine (1983-84); GC Grigg (1984-86); J Coventry (1986-87); RE Barwick (1987-88); J Covacevich (1988-91); M Davies (1991-92); R Shine (1992-94); A Georges (1994-6); D Roberts (1996-98); M Bull (1998-9); R Swain (1999-2001); S Downes (2001-03); J Melville (2004-2005); J -M Hero (2005-2007); P Doherty (2007-2008); M Thompson (2008-2009); M Hutchinson (2009-2010); L Schwarzkopf (2010-2011); F Lemckert (2011-) VICE-PRESIDENT:- NG Stephenson (1965-67); RE Barwick (1967-69); HG Cogger (1969-70); MJ Lit- tlejohn (1971-72); MJ Tyler (1973); HG Cogger (1974); J de Bavay (1975-76); H Heatwole (1976-77); GC Grigg (1977-79); MJ Tyler (1979-80); GF Watson (1981-82); AA Martin (1982-83); RS Seymour (1983- 84); R Shine (1984-86); GC Grigg (1986-87); J Coventry (1987-88); RE Barwick (1988-91); J Covacevich (1991-92); M Davies (1992-94); R Shine (1994-6); A Georges (1996-98); D Roberts (1998-99); M Bull (1999-2001); R Swain (2001-2003); S Downes (2004-5); J Melville (2005-2007); J-M Hero (2007-2008); P Doherty (2008-2009); M Thompson (2009-2010); M Hutchinson (2010-); L Schwarzkopf (2010-2011) SECRETARY/TREASURER:- AA Martin (1965-67); GF Watson (1967-72); LA Moffatt (1973-75); J Caughley (19375-76); RWG Jenkins (1976-77); M Davies (1978-83); G Courtice (1983-87); J Wombey (1987-99); S Keogh (1999-2003); N Mitchell (2004-5); E. -
Stoats (Mustela Erminea) Are Primary Predators, Which Are Likely to Be Impacting Significantly on Population Viability
DOI:O’Donnell 10.20417/nzjecol.41.18 et al.: Mammalian predators and alpine fauna 1 REVIEW Impacts of introduced mammalian predators on New Zealand’s alpine fauna Colin F. J. O’Donnell1, Kerry A. Weston1* and Joanne M. Monks2 1Science and Policy Group, Department of Conservation, Private Bag 4715, Christchurch Mail Centre, Christchurch 8140, New Zealand 2Science and Policy Group, Department of Conservation, PO Box 5244, Dunedin 9058, New Zealand *Author for correspondence (Email: [email protected]) Published online: 9 December 2016 Abstract: Alpine zones are threatened globally by invasive species, hunting, and habitat loss caused by fire, anthropogenic development and climate change. These global threats are pertinent in New Zealand, with the least understood pressure being the potential impacts of introduced mammalian predators, the focus of this review. In New Zealand, alpine zones include an extensive suite of cold climate ecosystems covering c. 11% of the land mass. They support rich communities of indigenous invertebrates, lizards, fish, and birds. Many taxa are obligate alpine dwellers, though there is uncertainty about the extent to which distributions of some species are relicts of wider historical ranges. The impacts of introduced mammalian predators are well described in many New Zealand ecosystems, though little is known about the impacts of these predators on alpine fauna. Here we review the importance of alpine habitats for indigenous fauna and the impacts of introduced mammalian predators; and develop a conceptual model explaining threat interactions. Most evidence for predation is anecdotal or comes from studies of species with wider ranges and at lower altitudes. Nevertheless, at least ten introduced predator species have been confirmed as frequent predators of native alpine species, particularly among birds and invertebrates. -
New Zealand Threat Classification System (NZTCS)
NEW ZEALAND THREAT CLASSIFICATION SERIES 17 Conservation status of New Zealand reptiles, 2015 Rod Hitchmough, Ben Barr, Marieke Lettink, Jo Monks, James Reardon, Mandy Tocher, Dylan van Winkel and Jeremy Rolfe Each NZTCS report forms part of a 5-yearly cycle of assessments, with most groups assessed once per cycle. This report is the first of the 2015–2020 cycle. Cover: Cobble skink, Oligosoma aff.infrapunctatum “cobble”. Photo: Tony Jewell. New Zealand Threat Classification Series is a scientific monograph series presenting publications related to the New Zealand Threat Classification System (NZTCS). Most will be lists providing NZTCS status of members of a plant or animal group (e.g. algae, birds, spiders). There are currently 23 groups, each assessed once every 3 years. After each three-year cycle there will be a report analysing and summarising trends across all groups for that listing cycle. From time to time the manual that defines the categories, criteria and process for the NZTCS will be reviewed. Publications in this series are considered part of the formal international scientific literature. This report is available from the departmental website in pdf form. Titles are listed in our catalogue on the website, refer www.doc.govt.nz under Publications, then Series. © Copyright December 2016, New Zealand Department of Conservation ISSN 2324–1713 (web PDF) ISBN 978–1–98–851400–0 (web PDF) This report was prepared for publication by the Publishing Team; editing and layout by Lynette Clelland. Publication was approved by the Director, Terrestrial Ecosystems Unit, Department of Conservation, Wellington, New Zealand. Published by Publishing Team, Department of Conservation, PO Box 10420, The Terrace, Wellington 6143, New Zealand. -
Modelling Reinvasion of the Common Brushtail Possum (Trichosurus Vulpecula) Within a New Zealand Urban Centre
Predicting Possums: Modelling reinvasion of the common brushtail possum (Trichosurus vulpecula) within a New Zealand urban centre Charlotte Ruby Patterson A thesis submitted in partial fulfilment of the requirements for the degree of Master of Science, Ecology University of Otago, Dunedin, New Zealand March 2020 In memory of Gary Oldcorn and Faye Patterson For the love of learning Abstract Invasive mammalian pests threaten biodiversity globally across a diverse range of habitats. Recent interest in urban biodiversity enhancement has increased the need for effective urban pest control, however efforts are hampered by a lack of understanding of the unique ecological processes occurring in cities. Projects seeking to eradicate mammals from mainland urban sites face the ongoing threat of reinvasion, and as such, often represent a significant long-term investment. There is a need for fundamental research of the invasive mammals that occupy urban habitats, and for this research to be integrated into evidence-based management. The introduced common brushtail possum (Trichosurus vulpecula) has invaded the majority of New Zealand landscapes, and is a nationally significant pest species. Decades of control and research in New Zealand have been focused on non-urban habitats, but the lens has shifted with the initiation of a national pest control initiative, which aims to eradicate T. vulpecula and several other mammalian pest species from the whole of New Zealand by 2050. New urban- based control projects have arisen in response, creating a need for urban-based research of possums. The overall aim of this thesis was to inform the management of possums in a New Zealand city, Ōtepoti/ Dunedin, by assessing the density of possums across urban habitat types, and applying this information to a spatially explicit, individual-based model of possum reinvasion. -
Alpine Lizard Research in Fiordland National Park
4.1.2 Geckos The two geckos found at Barrier Knob were Cascades geckos (H. aff. granulatus), as might be expected from the earlier findings of M. Judge and B. Judge in 2005 and Bell & Patterson (2006). This is a rock-dwelling, thigmothermic species that is sympatric with the skinks on Barrier Knob, sharing the same crevices or snow tussock vegetation. Some animals were captured while sunbasking, but we have no evidence whether this is a diurnal or nocturnal species. 4.2 Sinbad GullY 4.2.1 Skinks One adult male Sinbad skink was captured at 1200 m a.s.l. in Sinbad Gully on 10 March 2007. This specimen was medium to large, but slender (reaching up to 82 mm SVL, 188 mm TL, with a weight of 10 g; Fig. 5). The male was brightly coloured, with large green dorsal speckles against a black dorsal base colour, a black dorso-lateral band with large salmon-pink lateral speckles, pale grey chin and a belly flushed with vivid orange. It had a shiny, glossy appearance, and was characterised by long toes and a long tail. Genetic analysis by D. Chapple (pers. comm. 2007) on both the original animal captured by T. Jewell (RE 5315) and this adult, placed this species in the Fiordland skink group, which includes the Barrier skink. A distinctive looking skink was found only 10 m away from the capture site of the Sinbad skink. This skink was a small male (59 mm SVL, 121 mm TL, weight 3 g; Fig. 6). It was a deep and dark mahogany colour, with large eyes, a flat, wedge-shaped head and long toes. -
Sampling Skinks and Geckos in Artificial Cover Objects in a Dry Mixed Grassland–Shrubland with Mammalian Predator Control
WILSONAvailable on-line ET AL.: at: SAMPLING http://www.newzealandecology.org/nzje/ SKINKS AND GECKOS 169 Sampling skinks and geckos in artificial cover objects in a dry mixed grassland–shrubland with mammalian predator control Deborah J. Wilson1*, Robin L. Mulvey1,2 and Ryan D. Clark3 1 Landcare Research, Private Bag 1930, Dunedin 9054, New Zealand 2 Department of Botany and Plant Pathology, Cordley Hall 2082, Oregon State University, Corvallis, Oregon 97331-2902 3 Department of Zoology, University of Otago, PO Box 56, Dunedin 9054, New Zealand * Author for correspondence (Email: [email protected]) Published on-line: 3 December 2007 ___________________________________________________________________________________________________________________________________ Abstract: Introduced mammalian predators threaten populations of endemic New Zealand lizards but their effects on lizard populations have not been quantified on the mainland. We trialled the use of artificial cover objects (ACOs) for sampling small terrestrial lizards (the skinks Oligosoma maccanni, O. nigriplantare polychroma and O. inconspicuum, and gecko Hoplodactylus maculatus) in three experimental mammal-management treatments: a mammal-proof fence, two sites in an intensive mammal-removal area, and an experimental control site with no mammal removal. These predator control regimes were established in 2005–2006 to protect endangered grand skinks (O. grande) and Otago skinks (O. otagense) at Macraes Flat, North Otago. We (1) counted skinks and geckos found under ACOs on a single day and compared these counts between treatments, and (2) estimated lizard population sizes (N) based on capture-mark-recapture (CMR) of lizards under ACOs in daily and weekly sampling sessions. Our results provide baseline data of the abundance of the small lizard species shortly after implementation of predator management. -
Mamaku Point Conservation Reserve Restoration Plan June 2019
Mamaku Point Conservation Reserve Restoration Plan June 2019 Prepared by Kathleen Lalor [email protected] This report has been submitted in partial fulfilment of WILM501 Wildlife Management Research Placement 1 2 Table of Contents Summary assessment 4 Introduction 4 Mamaku Point Conservation Reserve Biological History of Stewart Island History of the Reserve Restoration Vision 6 Vision Statement Trust Objectives Conservation Outcomes Restoring Mamaku Point’s Birdlife 8 Current Birdlife Seabirds Habitat suitability for reintroducing missing birds Restoring Mamaku Point’s Other Fauna 13 Reptiles Bats Fish Amphibians Invertebrates Erosion 18 Measuring Conservation Outcomes – Initial Ideas 20 Restoration Policies 22 Ecotourism, School group, and Volunteer Access Plan 24 Concluding statement 27 Acknowledgements 27 Appendix I – Survey Methods 28 Questions Habitat Survey Bird Survey Skink Survey Appendix II – Survey Results 32 Habitat Survey Bird Survey Skink Survey Appendix III – Vascular plants of the Mamaku Point Conservation Reserve 36 Appendix IV – Bird Scavenger Hunt 38 Appendix V – Coordinates from surveys 40 Habitat Survey coordinates Bird Survey coordinates Skink Survey coordinates References 44 3 Summary assessment Mamaku Point Conservation Reserve is a biosecure nature reserve on Stewart Island, 4km north-west of the central township of Oban. It is an undisturbed, largely predator-free, forest sanctuary, fit for native birds, lizards, and invertebrates. The objectives of the Mamaku Point Conservation Trust are to: maintain and enhance biodiversity; offer an opportunity for education, learning, and research, and to create a financially and environmentally sustainable Reserve. It is my opinion that the Trust is achieving these objectives. The Reserve’s predator control programme is working well and is continuing to improve. -
An Investigation Into Declining Skink Populations and Their Behavioural Responses to Introduced Mammalian Predators
An investigation into declining skink populations and their behavioural responses to introduced mammalian predators Christina Terra Dumont Masters of Science in Ecology School of Biological Sciences, University of Canterbury Te Whare Wānanga o Waitaha 2015 Table of Contents Acknowledgments ......................................................................................................................... 1 Abstract .......................................................................................................................................... 2 Chapter 1: General Introduction ................................................................................................ 4 Effects of invasive predators on reptiles ..................................................................................... 4 The effect of introduced mammalian predators on New Zealand reptiles .................................. 7 Study species ............................................................................................................................. 10 Northern grass skink .............................................................................................................. 10 Speckled skink ....................................................................................................................... 10 Spotted skink ......................................................................................................................... 11 Glossy brown skink ..............................................................................................................