Identifying Geckos in Otago’) Print-Outs from DOC’S ‘Herpetofauna’ Database
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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. -
Table 7: Species Changing IUCN Red List Status (2018-2019)
IUCN Red List version 2019-3: Table 7 Last Updated: 10 December 2019 Table 7: Species changing IUCN Red List Status (2018-2019) Published listings of a species' status may change for a variety of reasons (genuine improvement or deterioration in status; new information being available that was not known at the time of the previous assessment; taxonomic changes; corrections to mistakes made in previous assessments, etc. To help Red List users interpret the changes between the Red List updates, a summary of species that have changed category between 2018 (IUCN Red List version 2018-2) and 2019 (IUCN Red List version 2019-3) and the reasons for these changes is provided in the table below. IUCN Red List Categories: EX - Extinct, EW - Extinct in the Wild, CR - Critically Endangered [CR(PE) - Critically Endangered (Possibly Extinct), CR(PEW) - Critically Endangered (Possibly Extinct in the Wild)], EN - Endangered, VU - Vulnerable, LR/cd - Lower Risk/conservation dependent, NT - Near Threatened (includes LR/nt - Lower Risk/near threatened), DD - Data Deficient, LC - Least Concern (includes LR/lc - Lower Risk, least concern). Reasons for change: G - Genuine status change (genuine improvement or deterioration in the species' status); N - Non-genuine status change (i.e., status changes due to new information, improved knowledge of the criteria, incorrect data used previously, taxonomic revision, etc.); E - Previous listing was an Error. IUCN Red List IUCN Red Reason for Red List Scientific name Common name (2018) List (2019) change version Category -
Lake Rotokare Scenic Reserve Invertebrate Ecological Restoration Proposal
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Lincoln University Research Archive Bio-Protection & Ecology Division Lake Rotokare Scenic Reserve Invertebrate Ecological Restoration Proposal Mike Bowie Lincoln University Wildlife Management Report No. 47 ISSN: 1177‐6242 ISBN: 978‐0‐86476‐222‐1 Lincoln University Wildlife Management Report No. 47 Lake Rotokare Scenic Reserve Invertebrate Ecological Restoration Proposal Mike Bowie Bio‐Protection and Ecology Division P.O. Box 84 Lincoln University [email protected] Prepared for: Lake Rotokare Scenic Reserve Trust October 2008 Lake Rotokare Scenic Reserve Invertebrate Ecological Restoration Proposal 1. Introduction Rotokare Scenic Reserve is situated 12 km east of Eltham, South Taranaki, and is a popular recreation area for boating, walking and enjoying the scenery. The reserve consists of 230 ha of forested hill country, including a 17.8 ha lake and extensive wetland. Lake Rotokare is within the tribal area of the Ngati Ruanui and Ngati Tupaea people who used the area to collect food. Mature forested areas provide habitat for many birds including the fern bird (Sphenoeacus fulvus) and spotless crake (Porzana tabuensis), while the banded kokopu (Galaxias fasciatus) and eels (Anguilla australis schmidtii and Anguilla dieffenbachii) are found in streams and the lake, and the gold‐striped gecko (Hoplodactylus chrysosireticus) in the flax margins. In 2004 a broad group of users of the reserve established the Lake Rotokare Scenic Reserve Trust with the following mission statements: “To achieve the highest possible standard of pest control/eradication with or without a pest‐proof fence and to achieve a mainland island” “To have due regard for recreational users of Lake Rotokare Scenic Reserve” The Trust has raised funds and erected a predator exclusion fence around the 8.4 km reserve perimeter. -
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 ................................................................................................................................... -
Oceania Species ID Sheets
Species Identification Sheets for Protected Wildlife in Trade - Oceania - 3 Mark O’Shea 1 Mike McCoy © Phil Bender 5 Tony Whitaker © 2 4 Tony Whitaker © 6 WILDLIFE ENFORCEMENT GROUP (AGRICULTURE & FORESTRY · CONSERVATION · N. Z. CUSTOMS SERVICE) Numbered images above Crown Copyright: Department of Conservation Te Papa Atawhai. Photographers:1) Dick Veitch 1981, 2) Rod Morris 1984, 3) Gareth Rapley 2009, 4) Andrew Townsend 2000, 5) Paul Schilov 2001, 6) Dick Veitch 1979 Introduction Purpose of this resource: - Additional species that should be included in this booklet Wildlife trafficking is a large-scale multi-billion dollar industry worldwide. The illegal trade of - Sources of information, such as identification guides or reports, related to these wildlife has reached such prominence that it has the potential to devastate source populations species of wildlife, impacting on the integrity and productivity of ecosystems in providing food and - Domestic legislation regarding the regulation of trade in wildlife - Sources of photographs for identification purposes resources to the local economy. In order to protect these resources, legislation has been put in place to control the trade of wildlife in almost every country worldwide. Those assigned with - Details of wildlife seizures, including the smuggling methods enforcing these laws have the monumental task of identifying the exact species that are being traded, either as whole living plants or animals, as parts that are dried, fried or preserved, or as Any feedback can be provided directly to the Wildlife Enforcement Group: derivatives contained within commercial products. Stuart Williamson Senior Investigator, Wildlife Enforcement Group This booklet “Species Identification Sheets for Protected Species in Trade – Oceania” has been Customhouse, Level 6, 50 Anzac Avenue, Auckland, New Zealand developed to address the lack of resources, identified by customs agencies within Oceania, for Ph: +64 9 3596676, Fax: +64 9 3772534 identification of wildlife species in trade. -
Survey of the Lizard Fauna of Janet Stewart and Styx Mill Conservation Reserves, Christchurch
Prepared for Styx Living Laboratory Trust 2010. Survey of the Lizard Fauna of Janet Stewart and Styx Mill Conservation Reserves, Christchurch Christine McClure – Lincoln University Contents Pg 1. Abstract 3 2. Introduction 3 3. Methods 5 3.1 Study Areas 5 3.1.1 Styx Mill Conservation Reserve 5 3.1.2 Janet Stewart Reserve: Pá Harakeke 6 3.2 Predation 7 3.3 Sites and Sampling 9 3.4 Site descriptions 10 3.6 Pitfall Traps (PF) 12 3.7 Artificial Cover Object (ACO) 14 3.8 Physical variables measured 15 4. Results 16 4.1 Species Identified 16 4.2 Site Results 17 5. Discussion 21 5.1 Effects of vegetation change on lizard habitat use 21 5.2 Herbicides 23 5.3 Predators 23 5.3.1 Predation population eruptions 24 5.4 Vandalism 26 5.5 Recommendations 26 5.6 Conclusion 27 5.7 Further Study 27 6. Acknowledgements 28 7. Benefits f the Summer Scholarship 28 Appendix 29 References Cited 31 2 | Page Survey of the Lizard Fauna of Janet Stewart and Styx Mill Conservation Reserves, Christchurch. 1. Abstract A survey was conducted in two Christchurch urban reserves, Janet Stewart and Styx Mill Conservation Reserves to establish which reptile species were present, including species preferred habitat type and health and age structure of populations found. Methods used to assess reptile fauna in the chosen areas were low‐intensity monitoring techniques such as pitfall trapping (PF) and artificial cover objects (ACO), placed at 14 sites throughout the reserves. Results show that there are two species of skink; Oligosoma nigriplantare polychroma (Common skink / mokomoko) and Oligosoma maccanni (McCann’s skink / mokomoko) inhabiting dry grassland habitats at Styx Mill Conservation Reserve. -
Skeletal Variation in Extant Species Enables Systematic Identification of New Zealand's Large, Subfossil Diplodactylids
Scarsbrook et al. BMC Ecol Evo (2021) 21:67 BMC Ecology and Evolution https://doi.org/10.1186/s12862-021-01808-7 RESEARCH Open Access Skeletal variation in extant species enables systematic identifcation of New Zealand’s large, subfossil diplodactylids Lachie Scarsbrook1*, Emma Sherratt2, Rodney A. Hitchmough3 and Nicolas J. Rawlence1 Abstract New Zealand’s diplodactylid geckos exhibit high species-level diversity, largely independent of discernible osteologi- cal changes. Consequently, systematic afnities of isolated skeletal elements (fossils) are primarily determined by comparisons of size, particularly in the identifcation of Hoplodactylus duvaucelii, New Zealand’s largest extant gecko species. Here, three-dimensional geometric morphometrics of maxillae (a common fossilized element) was used to determine whether consistent shape and size diferences exist between genera, and if cryptic extinctions have occurred in subfossil ‘Hoplodactylus cf. duvaucelii’. Sampling included 13 diplodactylid species from fve genera, and 11 Holocene subfossil ‘H. cf. duvaucelii’ individuals. We found phylogenetic history was the most important predictor of maxilla morphology among extant diplodactylid genera. Size comparisons could only diferentiate Hoplodactylus from other genera, with the remaining genera exhibiting variable degrees of overlap. Six subfossils were positively identifed as H. duvaucelii, confrming their proposed Holocene distribution throughout New Zealand. Conversely, fve subfossils showed no clear afnities with any modern diplodactylid genera, implying either increased morphological diversity in mainland ‘H. cf. duvaucelii’ or the presence of at least one extinct, large, broad-toed diplodactylid species. Keywords: Diplodactylidae, Ecomorphology, Geometric morphometrics, Hoplodactylus duvaucelii, Taxonomy Background (e.g. coloration and scalation), with interspecifc skeletal New Zealand’s lizard fauna is characteristic of isolated variation rarely analysed. -
Zootaxa, Reptilia, Pygopodidae, Hoplodactylus
Zootaxa 792: 1–11 (2004) ISSN 1175-5326 (print edition) www.mapress.com/zootaxa/ ZOOTAXA 792 Copyright © 2004 Magnolia Press ISSN 1175-5334 (online edition) A new species of Hoplodactylus (Reptilia: Pygopodidae) from the Takitimu Mountains, South Island, New Zealand TONY R. JEWELL1 & RICHARD A. B. LESCHEN2* 1 216 Ripponvale Road, R.D., Cromwell, New Zealand 2 New Zealand Arthropod Collection, Private Bag 92170, Auckland, New Zealand, [email protected] * Address correspondence to R. Leschen Abstract A gecko from alpine scree in the Takitimu Mountains, South Island, New Zealand, is described as Hoplodactylus cryptozoicus n. sp. Hoplodactylus cryptozoicus is characterized by an orange mouth lining, a short tail, minute body scales, and a distinctive colour pattern which includes bright orange patches. It may be closely related to H. nebulosus (McCann) based on the sharing of grey pigment on the tongue. Hoplodactylus cryptozoicus is known from only a single locality and is one of the few species of Hoplodactylus in New Zealand that inhabits rocks in the alpine zone. Key words: Reptilia; taxonomy; endemism; conservation Introduction The New Zealand gecko fauna presently comprises 18 validly named species placed into two endemic genera of the Diplodactylinae, Hoplodactylus Fitzinger 1843 and Naultinus Gray 1842. Both genera occur throughout the country and remain poorly studied with sev- eral species needing to be described. Most species, in fact, are threatened and/or of con- servation importance (Hitchmough 2002). Even though there are only a handful of species, taxonomic revisions are lacking with the last monograph that of McCann (1955). Since that time five species were described in the 1980’s (Robb 1980; Thomas 1981; Whi- taker 1985), including the mysterious Hoplodactylus delcourti Bauer and Russell, the larg- est species of gecko in the world and known from a single specimen (Bauer and Russell 1986, 1987; Russell and Bauer 1986). -
<I>Hoplodactylus Stephensi</I>
HARE,Available CREE: on-line NATURAL at: http://www.nzes.org.nz/nzje HISTORY OF H. STEPHENSI 137 SHORT COMMUNICATION Natural history of Hoplodactylus stephensi (Reptilia: Gekkonidae) on Stephens Island, Cook Strait, New Zealand Kelly M. Hare1 and Alison Cree2 1School of Biological Sciences, Victoria University of Wellington, P.O. Box 600, Wellington, New Zealand (E-mail: [email protected]) 2Department of Zoology, University of Otago, P.O. Box 56, Dunedin, New Zealand ____________________________________________________________________________________________________________________________________ Abstract: The striped gecko (Hoplodactylus stephensi) is one of the rarest and most elusive of New Zealand’s lizards. It is currently known from just three locations; Stephens Island (Takapourewa) in Cook Strait, Maud Island in Pelorus Sound, and the Coromandel Peninsula. The striped gecko is a relatively poorly studied species with little data available on many aspects of its biology. We report on the first estimate of longevity in H. stephensi (a minimum of 16 years) and provide baseline data on population structure, habitat use, morphometrics and pregnancy rate. Our data show the value of permanently marked populations of reptiles available for long-term study by different researchers. ____________________________________________________________________________________________________________________________________ Keywords: Life history; longevity; striped gecko. Introduction 85 mm snout-vent length), and is nocturnal and arboreal. It -
And Endoparasites of New Zealand Reptiles
An annotated checklist This article lists the internal and external parasites recorded in or on tuataras and lizards in New Zealand of ecto- and endoparasites and includes brief notes about them. of New Zealand reptiles Tuataras and lizards are New Zealand’s only land-based native reptiles. Currently these comprise two species of tuatara, 16 geckos divided into the major groups of Nematoda, Cestoda, Trematoda and 28 skinks although the exact number of lizards is undecided and Protozoa whereas all ectoparasite records are included in the and is likely to increase as more research is done(1). In this article order Acari. In the annotated list, the parasites are not only attempts are made to catalogue all those ecto- and endoparasites identified according to the phylum or order to which they belong, that have been recorded on, or in, these hosts. but also to family level. In the latter list, each parasite record is also The parasite checklist is presented in three parts. The first two parts supported by a reference, but these are omitted in parts one and simply list these records alphabetically by common host name two. While these data are primarily concerned with parasites of according to Gill and Whitaker(1) and by parasite group, respectively. New Zealand’s native reptile fauna, for the sake of completeness, The third comprises an annotated catalogue of the parasites those that have been recorded from two non-naturalised captive arranged alphabetically according to their scientific names. In the lizards in this country (the Indian blood sucker lizard and the former two parts, and as appropriate, the endoparasite groups are bluetongue skink) are included as well. -
Scoping the Potential to Eradicate Rats, Wild Cats and Possums from Stewart Island/Rakiura
Scoping the Potential to Eradicate Rats, Wild Cats and Possums from Stewart Island/Rakiura Scoping the potential to eradicate rats, wild cats and possums from Stewart Island / Rakiura Page 2 of 139 Scoping the potential to eradicate rats, wild cats and possums from Stewart Island / Rakiura Quotes of note Southland mayor Frana Cardno on visiting Sirocco the kakapo on Ulva Island (Southland Times, 2 Sept 2006). “It was a truly magical experience walking through the bush on Ulva Island. The lush undergrowth, the sounds of kiwi and kaka’s call and you can’t help reflect and say a quiet thankyou to the Ulva Island Trust in partnership with DOC, who have eradicated all pests from this beautiful island. The birds and bush are being restored to what we had in the past, what an investment for the future.” Andy Roberts, Southern Islands Area Manager (Campbell Island Eradication Scoping Paper 2000). “We only got to this position by doing what others believed was impossible!” Compiled by: Brent Beaven Department of Conservation Southland Conservancy Invercargill New Zealand June 2008 Contracted by: Stewart Island/ Rakiura Community and Environment Trust PO Box 124 Stewart Island www.sircet.org.nz Page 3 of 139 Page 4 of 139 Summary What is proposed? Stewart Island / Rakiura has exceptionally high conservation values; in part due to the absence of certain pests that are present on mainland New Zealand (notably stoats and mice). However, Norway rats (Rattus norvegicus), ship rats (Rattus rattus), kiore / Pacific rats (Rattus exulans), wild cats (Felis catus) and possums (Trichosurus vulpecula) are established on Stewart Island / Rakiura and these species are causing a steady decline in the Island’s indigenous flora and fauna.