Modelling Reinvasion of the Common Brushtail Possum (Trichosurus Vulpecula) Within a New Zealand Urban Centre
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Foraging Ecology of the World's Only
Copyright is owned by the Author of the thesis. Permission is given for a copy to be downloaded by an individual for the purpose of research and private study only. The thesis may not be reproduced elsewhere without the permission of the Author. FORAGING ECOLOGY OF THE WORLD’S ONLY POPULATION OF THE CRITICALLY ENDANGERED TASMAN PARAKEET (CYANORAMPHUS COOKII), ON NORFOLK ISLAND A thesis presented in partial fulfilment of the requirements for the degree of Master of Science in Conservation Biology at Massey University, Auckland, New Zealand. Amy Waldmann 2016 The Tasman parakeet (Cyanoramphus cookii) Photo: L. Ortiz-Catedral© ii ABSTRACT I studied the foraging ecology of the world’s only population of the critically endangered Tasman parakeet (Cyanoramphus cookii) on Norfolk Island, from July 2013 to March 2015. I characterised, for the first time in nearly 30 years of management, the diversity of foods consumed and seasonal trends in foraging heights and foraging group sizes. In addition to field observations, I also collated available information on the feeding biology of the genus Cyanoramphus, to understand the diversity of species and food types consumed by Tasman parakeets and their closest living relatives as a function of bill morphology. I discuss my findings in the context of the conservation of the Tasman parakeet, specifically the impending translocation of the species to Phillip Island. I demonstrate that Tasman parakeets have a broad and flexible diet that includes seeds, fruits, flowers, pollen, sori, sprout rhizomes and bark of 30 native and introduced plant species found within Norfolk Island National Park. Dry seeds (predominantly Araucaria heterophylla) are consumed most frequently during autumn (81% of diet), over a foraging area of ca. -
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. -
Assessing Pollination and Fruit Dispersal in Fuchsia Excorticata (Onagraceae)
RobertsonNew Zealand et al.—Pollination Journal of Botany, and 2008, dispersal Vol. in46 Fuchsia: 299–314 299 0028–825X/08/4603–0299 © The Royal Society of New Zealand 2008 Assessing pollination and fruit dispersal in Fuchsia excorticata (Onagraceae) ALastaIR W. ROBErtsON cases very frequently by silvereyes, which also oc- Ecology, Institute of Natural Resources casionally rob nectar from flowers. We confirmed Massey University that hermaphrodites account for more than half the Private Bag 11222 plants in all populations, are fully self-compatible, Palmerston North 4474, New Zealand and can autonomously self in the absence of pollina- [email protected] tors (especially in plants with smaller herkogamy). Fruit production in hermaphrodites and (particularly) JENNY J. LADLEY females was frequently pollen-limited (mean Pollen DAVE KELLY Limitation Indices of 0.17 and 0.40, respectively), School of Biological Sciences and was correlated with visual assessments of pol- University of Canterbury len loads on the stigma, a useful index of pollinator Private Bag 4800 service. A comparison of the proportion of ripe or Christchurch 8140, New Zealand overripe fruit on branches exposed to birds versus KatE L. MCNUTT branches enclosed in wire cages showed that un- Ecology, Institute of Natural Resources caged fruit on Kapiti Island is removed almost as Massey University soon as it is ripe but on the mainland it persists for Private Bag 11222 much longer. The proportion of ripe or overripe Palmerston North 4474, New Zealand compared to green fruit is therefore an approximate index of dispersal service. Both indices may be use- PAUL G. PETERSON ful to managers concerned with measuring the level Landcare Research of mutualism service provided by native birds. -
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. -
(Fuchsia Excorticata) and Tree Weta
Austral Ecology (2011) 36, 261–268 Mutualism or opportunism? Tree fuchsia (Fuchsia excorticata) and tree weta (Hemideina) interactionsaec_2146 261..268 TARRYN E. WYMAN,1* STEVE A. TREWICK,1 MARY MORGAN-RICHARDS1 AND ALASDAIR D. L. NOBLE2 1Ecology Group, Institute of Natural Resources, and 2Institute of Fundamental Sciences, Massey University, Private Bag 11–222, Palmerston North 4442, New Zealand Abstract Mutualisms or interspecific interactions involving net mutual benefits, are an important component of ecological theory, although effectively demonstrating mutualism is notoriously difficult. Among two New Zealand endemics, a slightly elevated germination rate of Fuchsia excorticata (Onagraceae) seeds after passage through tree weta (Orthoptera: Anostostomatidae) compared with seeds manually extracted from fruit, led to the proposal that a mutualistic relationship exists between this plant and animal. An improved germination rate, or any other single trait, however, does not alone constitute evidence for mutualism; the relative costs and benefits of numerous components of the interaction need to be accounted for.We considered the costs and benefits to F.excorticata of the putative seed dispersal mutualism with tree weta.Tree weta provided with F.excorticata fruits destroyed 78% of the seeds they consumed, did not move fruit; and faeces containing seeds were deposited near their roost holes (which are naturally in trees). The seeds remaining after fruit consumption and those that are ingested but survive gut passage are unlikely to be deposited in suitable habitat for seedling survival. Plant food preferences of captive tree weta assessed using pairwise leaf choice tests showed that the leaves of F.excorticata were the least preferred of six commonly encountered plants. -
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. -
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66 AvailableNew on-lineZealand at: Journal http://www.newzealandecology.org/nzje/ of Ecology, Vol. 34, No. 1, 2010 special issue: Feathers to Fur The ecological transformation of Aotearoa/New Zealand Mutualisms with the wreckage of an avifauna: the status of bird pollination and fruit- dispersal in New Zealand Dave Kelly1*, Jenny J. Ladley1, Alastair W. Robertson2, Sandra H. Anderson3, Debra M. Wotton1, and Susan K. Wiser4 1School of Biological Sciences, University of Canterbury, Private Bag 4800, Christchurch 8140, New Zealand 2Ecology, Institute of Natural Resources, Massey University, Private Bag 11222, Palmerston North 4474, New Zealand 3School of Environment, University of Auckland, Private Bag 92019, Auckland 1010, New Zealand 4Landcare Research, PO Box 40, Lincoln 7640, New Zealand *Author for correspondence (Email: [email protected]) Published on-line: 9 November 2009 Abstract: Worldwide declines in bird numbers have recently renewed interest in how well bird–plant mutualisms are functioning. In New Zealand, it has been argued that bird pollination was relatively unimportant and bird- pollination failure was unlikely to threaten any New Zealand plants, whereas dispersal mutualisms were widespread and in some cases potentially at risk because of reliance on a single large frugivore, the kereru (Hemiphaga novaeseelandiae). Work since 1989, however, has changed that assessment. Smaller individual fruits of most plant species can be dispersed by mid-sized birds such as tui (Prosthemadera novaezelandiae) because both fruits and birds vary in size within a species. Only one species (Beilschmiedia tarairi) has no individual fruits small enough for this to occur. Germination of 19 fleshy-fruited species, including most species with fruits >8 mm diameter, does not depend on birds removing the fruit pulp. -
Pdf Size: 669 KB Dr Tocher (Herpetology)
Before a joint hearing of the Otago Regional Council RM20.024 Waitaki District Council 201.2019.1454 Under the Resource Management Act 1991 In the matter of applications by Oceana Gold (New Zealand) Limited for resource consents for the Deepdell North Stage III project Statement of evidence of Mandy Tocher for Oceana Gold (New Zealand) Limited 4 August 2019 Qualifications and experience 1 My name is Mandy D. Tocher. 2 I am a Principal Ecologist and Herpetologist for Ryder Environmental Limited. I have held this position since October 2017. I have worked in the field of Herpetology (lizards and frogs) for over 30 years. Prior to taking up my position with Ryder Environmental, I was employed by another ecological consultancy from 2011. From 1996-2011 (16- years) I was employed by the Department of Conservation as a research scientist specialising in management of South Island lizards and frogs, including carrying out 10- years of lizard research at Macraes Flat1. 3 I hold a Ph.D. from the University of Canterbury awarded in 1997, where I researched the effects of forest fragmentation, forest destruction, edge effects, and matrix habitat on herpetofauna using grant money awarded from the Smithsonian Institute in Washington, USA and the WWF. This work culminated in the publication of multiple scientific publications and book chapters2. 4 I also hold a Master of Science (1st class honours), awarded from the University of Canterbury in 1992; for part of this degree I researched the eco-physiology of Otago and Canterbury geckos including their tolerance to cold, and their ability to adapt physiologically to cold conditions3.