A Dilemma for New Zealand Herpetologists
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On Ulva Island
Abundance and dispersal of translocated common skink (Oligosoma polychroma) on Ulva Island Helen Sharpe A report submitted in partial fulfilment of the Post-graduate Diploma in Wildlife Management University of Otago 2011 University of Otago Department of Zoology P.O. Box 56, Dunedin New Zealand WLM Report Number: 250 Abundance and dispersal of translocated common skink (Oligosoma polychroma) on Ulva Island A report prepared for the Department of Conservation in association with Otago University’s Diploma of Wildlife Management. Helen Sharpe July 2011 2 Abundance and dispersal of translocated common skink (Oligosoma polychroma) on Ulva Island Contents Summary 2 Introduction 3 Methods 4 Results 8 Discussion 9 Recommendations 13 Acknowledgements 15 References 16 Figures and tables 18 3 Abundance and dispersal of translocated common skink (Oligosoma polychroma) on Ulva Island Summary This report describes a monitoring study carried out in 2011 to investigate the abundance and distribution of common skink (Oligosoma polychroma) on Ulva Island, Southland, New Zealand. Common skinks were introduced to Ulva in 2005 and 2006 for ecosystem restoration, and to investigate effects of weka (Gallirallus australis scotti) predation. Skinks were monitored over 3 non-consecutive days using artificial cover objects. Where possible skinks were caught, weighed, measured and photographed. A total of 18 sightings were made which indicates a substantial drop in both populations but especially at West End Beach. A combination of insufficient habitat and predation/competition by weka are the probable causes. However some uncertainties with monitoring are acknowledged, with regard to sub-optimal weather conditions and ‘settling’ time for new ACOS. Skinks appear not to have dispersed more than 20-30 metres from their release site. -
Reptiles and Amphibians of Otago
Society for Research on Amphibians and Reptiles in New Zealand (SRARNZ) presents Reptiles and Amphibians of Otago Otago is a large (31,251 km2) and lightly populated region of the southern South Island of Aotearoa New Zealand, stretching from the eastern coastline west to the Southern Alps. The earliest humans, of East Polynesian origin, arrived about 700 years ago. The largest settlement today is the coastal city of Dunedin (pop. >127,000), which grew from a Scottish influx in the 1800s. The Otago Regional Council administers the region, and tribal authority (mana whenua) rests with the iwi of Ngāi Tahu. Climates in the Otago region (roughly 45°– leiopelmatid frogs survive elsewhere in 47°S) range from changeable, cool- New Zealand. Two species of introduced temperate conditions near the coast to frogs are present, but there are no the near-continental climates (baking hot crocodilians, salamanders, terrestrial summers, freezing winters) of the interior. snakes or turtles. Marine turtles (mainly The region provides varied habitats for leatherback turtles, Dermochelys coriacea) herp species, including sand-dunes, visit the coastal waters of Otago but do grasslands, shrublands, wetlands, forests, not nest here. rock structures and scree slopes, some occupied to at least 1900 m above sea level. Today’s herpetofauna is dominated by lizards (solely geckos and skinks), including about 10 described species. A further 12 or more undescribed taxa are recognised Otago by tag names for conservation purposes, and we follow that approach here. All lizards in Otago are viviparous and long- lived, and remain vulnerable to ongoing habitat loss and predation by introduced mammals. -
Ecology of Scree Skinks (Oligosoma Waimatense) in O Tu Wharekai Wetland, Mid-Canterbury High Country, New Zealand
Lettink,New Zealand Monks: Journal Scree ofskink Ecology ecology (2019) 43(1): 3354 © 2018 New Zealand Ecological Society. RESEARCH Ecology of scree skinks (Oligosoma waimatense) in O Tu Wharekai Wetland, mid-Canterbury high country, New Zealand Marieke Lettink1* and Joanne M. Monks2 1Fauna Finders, 45 Park Terrace, Corsair Bay, Christchurch 8082 2Department of Conservation, Ōtepoti/Dunedin Office, PO Box 5244, Dunedin 9058 *Author for correspondence (Email: [email protected]) Published online: 17 October 2018 Abstract: Many of New Zealand’s 104 lizard taxa are restricted to the country’s main islands where they are vulnerable to a range of threats. Information on population trends and basic ecological data are lacking for most species, hampering conservation efforts. We monitored a population of scree skinks (Oligosoma waimatense; conservation status: Nationally Vulnerable) in an alluvial stream bed in O Tu Wharekai Wetland in the mid- Canterbury high country over 10 years (2008−2018) to understand aspects of the population’s ecology, and to clarify potential threats and options for management. Although there was no linear trend in scree skink capture numbers over this time, an 84% decline was observed following severe and unseasonal flooding in May 2009. Capture numbers recovered over c. 8.5 years in the absence of any species management. Skinks ranged in size from 60−114 mm (snout-to-vent length). Home range size estimates varied from 39.5 to 950 m2 (100% Minimum Convex Polygons) and their mean size was smaller than those reported for closely-related species. Photo-identification was not sufficiently accurate for long-term individual identification. -
Surveys for Hoplodactylus Aff. Granulatus, Roys Peak and Mt Alpha, Wanaka
Surveys for Hoplodactylus aff. granulatus, Roys Peak and Mt Alpha, Wanaka Mandy D Tocher Science & Research Unit Department of Conservation PO Box 5244 Dunedin Leigh J Marshall c/o Zoology Department University of Otago PO Box 56 Dunedin Published by Department of Conservation Head Office, PO Box 10-420 Wellington, New Zealand This report was commissioned by Otago Conservancy. ISSN 1171-9834 © 2001 Department of Conservation Reference to material in this report should be cited thus: Tocher, M.D.; Marshall, LJ, 2001. Surveys for Hoplodactylus aff. granulatus, Roys Peak and Mt Alpha, Wanaka. Conservation Advisory Science Notes 344, Department of Conservation, Wellington. Keywords: forest geckos, Hoplodactylus sp., search, Roys Peak, Wanaka Ecological District. 1. Introduction and background Recent evidence shows the forest gecko Hoplodactylus granulatus (sensu Thomas 1981) comprises at least two species (Hitchmough 1997). Based on allozyme data, Hitchmough (1997) has reinstated the cloudy gecko H. nebulosus from synonymy with H. granulatus. Furthermore, Hitchmough (1997) suggests there may be further undescribed species within the H. granulatus complex, but the small number of samples available for analyses prevents further subdivision. In particular, forest geckos from the North Is- land differ genetically from forest geckos of the South Island West Coast. In addition, forest geckos from Nelson/Marlborough are genetically similar to forest geckos from the South Island West Coast, but their life history traits are more similar to forest geckos from the North Island. Hitchmough (1997) also refers to other geckos that are likely to represent fur- ther undescribed species of H. granulatus type geckos. A small juvenile gecko from the Esperance Valley in Fiordland superficially resembles Hoplodactylus rakiurae, although it is thought to be morphologically quite distinct. -
Assessment of Lizards for a Proposed Expansion of the Kiwi Point Quarry, Ngauranga Gorge, Wellington
ASSESSMENT OF LIZARDS FOR A PROPOSED EXPANSION OF THE KIWI POINT QUARRY, NGAURANGA GORGE, WELLINGTON Barking gecko (Naultinus punctatus), one of the lizard species potentially present within the proposed quarry footprint. Contract Report No. 4378b December 2017 Project Team: Carey Knox - Field work, report author Astrid van Meeuwen-Dijkgraaf - Field work Prepared for: Wellington City Council PO Box 2199 Wellington 6140 WELLINGTON OFFICE: 22 RAIHA STREET, ELSDON, P.O. BOX 50-539, PORIRUA Ph 04-237-7341; Fax 04-237-7496 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. DESKTOP ASSESSMENT OF WELLINGTON LIZARD TAXA 1 3. SURVEY METHODS 2 3.1 Overview 2 3.2 Survey methods used 4 3.3 Information collected during the survey 6 4. SURVEY RESULTS 6 4.1 Likelihood of species presence 8 5. SURVEY LIMITATIONS 11 6. POTENTIAL ADVERSE EFFECTS 11 7. POSSIBLE MITIGATION FOR CLEARANCE OF LIZARD HABITAT 11 8. PERMIT REQUIREMENTS 12 9. CONCLUSIONS 13 ACKNOWLEDGMENTS 13 REFERENCES 13 Reviewed and approved for release by: _______________________ W.B. Shaw Director/Principal Ecologist Wildland Consultants Ltd Wildland Consultants Ltd 2017 This report has been produced by Wildland Consultants Ltd for Wellington City Council. All copyright in this report is the property of Wildland Consultants Ltd and any unauthorised publication, reproduction, or adaptation of this report is a breach of that copyright. © 2017 Contract Report No. 4378b 1. INTRODUCTION Kiwi Point Quarry has been operating on Wellington City Council (WCC)-owned land in the Ngauranga Gorge since the 1920s. -
Report Format WITHOUT PHOTOS
LIZARD MANAGEMENT PLAN WAKANUI CREEK REALIGNMENT 28 FEBRUARY 2018 LIZARD MANAGEMENT PLAN WAKANUI CREEK REALIGNMENT PREPARED BY: DYLAN VAN WINKEL BIORESEARCHES GROUP LTD 68 BEACH ROAD, AUCKLAND [email protected] FOR: AECOM NEW ZEALAND LIMITED PO BOX 4241 SHORTLAND ST AUCKLAND 1140 DATE: 28 FEBRUARY 2018 REFERENCE: BIORESEARCHES (2017). LIZARD MANAGEMENT PLAN: WAKANUI CREEK REALIGNMENT COVER ILLUSTRATION: OLIGOSOMA AFF. POLYCHROMA Level 4, 68 Beach Road, Auckland 1010; PO Box 2727, Shortland Street, Auckland 1140. T: (09) 379-9417; www.bioresearches.co.nz CONTENTS Page 1 INTRODUCTION ................................................................................................................ 1 2 LIZARD MANAGEMENT PLAN ........................................................................................... 2 2.1 Context of the lizard management plan .............................................................. 2 2.2 Project area and area of affected habitat ........................................................... 2 2.3 Local lizard populations ....................................................................................... 5 2.4 Management of resident lizards .......................................................................... 5 3 LIZARD SALVAGE AND RELOCATION ................................................................................. 6 3.1 Lizard capture ...................................................................................................... 6 3.1.1 Active Searches ....................................................................................... -
The Spatial Distribution of Pā in Tōtaranui/Queen Charlotte Sound, New Zealand
The spatial distribution of pā in Tōtaranui/Queen Charlotte Sound, New Zealand A thesis submitted for the degree of Master of Arts, University of Otago, Dunedin, New Zealand Tristan Wadsworth i Abstract The distribution of pā sites in the central New Zealand region of Tōtaranui/Queen Charlotte Sound is investigated to determine the relationship between pā and other Māori archaeological sites, and the influence of maritime and introduced terrestrial resources. Particular aims of research are to investigate the role of visibility as a measure of defensibility in the distribution of Tōtaranui pā, and whether this distribution is influenced by the distribution of garden sites and karaka stands, two important introduced resources often considered to influence pā distribution at national levels. Additionally, evidence for gardening activity is ambiguous in Tōtaranui, for which there is a number of archaeologically recorded garden sites but a noted absence of gardening activity in the earliest historical records. Investigation into the distribution of pā is done by comparing proximity and intervisibility of pā sites to a range of Māori archaeological site types (garden sites, karaka stands, midden sites, oven sites, other pā sites, pit sites, and terrace sites). Proximity of pā to other archaeological sites is quantitatively measured by way of cost distance analysis, and intervisibility of sites measured by way of viewshed analysis within Geographical Information Systems (GIS). Cost distances and frequency of intervisibility of pā to other archaeological sites is recorded and compared against a dataset of random points. Based on the methodology used in the analysis, neither maritime nor introduced terrestrial resources had a significant influence on the distribution of Tōtaranui pā. -
Maori Occupation of Arapawa Island Archaeological Evidence 4; Evidence of Maori Settlement 4
LIST OF CONTENTS Chapter 1: Introduction The claim 1; The Location 2 Chapter 2: Maori Occupation of Arapawa Island Archaeological evidence 4; Evidence of Maori Settlement 4 Chapter 3: The Purchase of Land - The New Zealand Company 7; The Waipounamu purchases 8 (, (, Chapter 4: The Watering Place Resewe 14 The Queen's Chain 14; Sounds Foreshore Reserve 18; The Department of Conservation's regime 24 Chapter 5: The Oamaru Native Resewe 28 The Native Land Court 29; The Queen's Chain 32; Sounds Foreshore Reserve 33; The Law of Foreshore Ownership 42 Chapter 6: Umukuri Bay urupa 46 Chapter 7: Conclusion 5 1 ( The Watering Place Reserve 51; Sounds Foreshore Reserve 52; The Umukuri Bay Urupa 53 Bibliography 54 Chapter 1 Introduction This report summarises the alienation of Maori land on Arapawa Island, and, in particular, part of Oamaru Native Reserve. The Claim \ The claim (Wai 124) relates to Arapawa Island and was received on 22 February 1990. It was submitted by Neville Karira Watson Tahuaroa for himself and on behalf of the descendants of Rihari Tahuaroa. The claim concerns the Sounds Foreshore Reserve fronting Oamaru 2A3, which is an urupa, and Oamaru part 1B1, both part of the Oamaru Native Reserve on Arapawa Island. It also concerns a reserve adjoining the Oamaru Native Reserve, known as the Watering Place Reserve. The claimant states that he and the descendants of Rihati Tahuaroa are prejudicially affected by: a the Department of Conservation's failure to protect the urupa against erosion; a proposal by DOC to exchange the Watering Place Reserve with land adjacent to the reserve; the need for him to pay rental for the foreshore reserve fronting his property at part 1B1. -
Assessment of Microbranding As an Alternative Marking Technique for Long-Term Identification of New Zealand Lizards
AvailableHitchmough on-line et al.: at: Microbranding http://www.newzealandecology.org/nzje/ as an alternative marking technique for New Zealand Lizards 151 Assessment of microbranding as an alternative marking technique for long-term identification of New Zealand lizards Rod Hitchmough1*, Keri Neilson1,5, Kara Goddard2, Mike Goold2, Brett Gartrell3, Stu Cockburn1 and Nicholas Ling4 1Research & Development Group, Department of Conservation, PO Box 10 420, Wellington 6143, New Zealand 2Hamilton Zoo, Hamilton City Council, Private Bag 3010, Hamilton 3240, New Zealand 3New Zealand Wildlife Health Centre, Institute of Veterinary, Animal and Biomedical Sciences, Massey University Manawatu, Private Bag 11 222, Palmerston North 4442, New Zealand 4Department of Biological Sciences, University of Waikato, Private Bag 3105, Hamilton 3240, New Zealand 5Present address: Lake Management Officer, River & Catchment Services, Environment Waikato Regional Council, PO Box 4010, Hamilton East 2032, New Zealand * Author for correspondence (Email: [email protected]) Published on-line: 1 May 2012 Abstract: ‘Microbranding’, a system for individually identifying reptiles and amphibians based on a numbered code of spot brands applied to the body and limbs, was tested on New Zealand skinks and geckos. Common geckos (Woodworthia maculata) and copper skinks (Oligosoma aeneum) were used as test animals. Brands applied in autumn took 3 months or more to heal. There was no evidence of brand-related mortality or increased parasite loads in branded animals. However, after healing the brands faded very rapidly in the skinks to become totally unreadable in all surviving branded skinks after 2.5 years and not accurately readable in most geckos after 3 years. We therefore consider the technique unsuitable as a standard marking procedure for New Zealand lizards. -
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. -
DOCDM-1023668 Herpetofauna: Photo-Identification V1.0 2
Herpetofauna: photo-identification Version 1.0 This specification was prepared by Marieke Lettink in 2012. Contents Synopsis .......................................................................................................................................... 2 Assumptions .................................................................................................................................... 5 Advantages ...................................................................................................................................... 5 Disadvantages ................................................................................................................................. 6 Suitability for inventory ..................................................................................................................... 6 Suitability for monitoring ................................................................................................................... 6 Skills ................................................................................................................................................ 7 Resources ....................................................................................................................................... 7 Minimum attributes .......................................................................................................................... 7 Data storage ................................................................................................................................... -
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.