The Hopeful Story of the Parrot That Cannot Fly Thousands of Miles
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Eradication of Stoats (Mustela Erminea) from Secretary Island, New Zealand
McMurtrie, P.; K-A. Edge, D. Crouchley, D. Gleeson, M.J. Willans, and A.J. Veale. Eradication of stoats (Mustela erminea) from Secretary Island, New Zealand Eradication of stoats (Mustela erminea) from Secretary Island, New Zealand P. McMurtrie1, K-A. Edge1, D. Crouchley1, D. Gleeson2, M. J. Willans3, and A. J. Veale4 1Department of Conservation, Te Anau Area Office, PO Box 29, Lakefront Drive, Te Anau 0640, New Zealand. <[email protected]>. 2Landcare Research, PB 92170, Auckland, NZ. 3The Wilderness, RD Te Anau-Mossburn Highway, Te Anau, NZ. 4School of Biological Sciences, The University of Auckland, Private Bag 92019, Auckland Mail Centre, Auckland 1142, NZ. Abstract Stoats (Mustelia erminea) are known to be good swimmers. Following their liberation into New Zealand, stoats reached many of the remote coastal islands of Fiordland after six years. Stoats probably reached Secretary Island (8140 ha) in the late 1800s. Red deer (Cervus elaphus) are the only other mammalian pest present on Secretary Island; surprisingly, rodents have never established. The significant ecological values of Secretary Island have made it an ideal target for restoration. The eradication of stoats from Secretary Island commenced in 2005. Nine-hundred-and-forty-five stoat trap tunnels, each containing two kill traps, were laid out along tracks at a density of 1 tunnel per 8.6 ha. Traps were also put in place on the adjacent mainland and stepping-stone islands to reduce the probability of recolonisation. Pre-baiting was undertaken twice, first in June and then in early July 2005. In late July, the traps were baited, set and cleared twice over 10 days. -
Stoat Eradication
Resolution Island Operational Plan Stoat Eradication SOUTHLAND CONSERVANCY 2008 Resolution Island Operational Plan Stoat Eradication Pete Mc Murtrie, Kerri-Anne Edge, Dave Crouchley and Murray Willans 2008 Published by Department of Conservation PO Box 743 Invercargill, New Zealand Publ.info. Cover: Mount Clerke Bivvy, Resolution Island, Fiordland National Park Photo: Pete Kirkman, DOC © Copyright 2008, New Zealand Department of Conservation ISBN 978-0-478-14433-8 (hardcopy) ISBN 978-0-478-14434-5 (web PDF) Te Anau Area Office Internal Report In the interest of forest conservation we support paperless electronic publishing. When printing, recycled paper is used wherever possible. CONTENTS 1.0 Executive Summary 5 2.0 Introduction 2.1 Island description 6 2.2 Threat status 7 2.3 Island classification 7 2.4 Treasury funding for Secretary and Resolution Islands 8 2.5 Key learning points from previous stoat eradication programmes 8 2.6 Programme objectives 9 2.7 Operational objectives 10 3.0 Set-up Phase 11 3.1 Trap lines 11 3.2 Bivvies 14 3.3 Communications 14 3.4 Transportation 14 3.5 Trap design and layout 14 3.5.1 Trap choice 14 3.5.2 Tunnels 15 3.5.3 Tunnel placement 18 4.0 Knockdown Phase 20 4.1 Timing of knockdown 20 4.2 Pre-baiting 20 4.3 Bait type 20 4.4 Trapping 21 4.5 Data collection during knock-down 22 5.0 Maintenance Phase 23 5.1 Managing re-invasion 23 5.2 Timing of trap checks 25 6.0 Monitoring and Programme Evaluation 26 6.1 Result monitoring 26 6.2 Outcome Monitoring 27 7.0 Quarantine Management 28 8.0 Milestones 30 9.0 References 32 10.0 Internal Department of Conservation documents 34 Appendix 1 35 Appendix 2 36 Appendix 3 37 Appendix 4 38 Appendix 5 40 Appendix 6 43 Appendix 7 44 4 Resolution Island Operational Plan: Stoat Eradication 1.0 Executive Summary Resolution Island, including Five Fingers Peninsula, is the largest of the islands on the Fiordland coast, covering 20 860 hectares and rising to 1 069 m and above sea level. -
New Locality Records for Two Species of Protected Weevils, Anagotus Fairburni
Tuhinga 29: 20–34 Copyright © Museum of New Zealand Te Papa Tongarewa (2018) New locality records for two species of protected weevils, Anagotus fairburni (Brookes, 1932) and Hadramphus stilbocarpae Kuschel, 1971 (Coleoptera: Curculionidae), from southern Fiordland, New Zealand Colin M. Miskelly,* Alan J.D. Tennyson** and Colin R. Bishop*** * Museum of New Zealand Te Papa Tongarewa, PO Box 467, Wellington 6140, New Zealand ([email protected]) ** Museum of New Zealand Te Papa Tongarewa, PO Box 467, Wellington 6140, New Zealand *** Department of Conservation, PO Box 29, Te Anau 9600, New Zealand ABSTRACT: The flax weevil Anagotus fairburni (Brookes, 1932) and knobbled weevil Hadramphus stilbocarpae Kuschel, 1971 were among the first New Zealand insects to be granted legal protection. Both are large flightless species with narrow host–plant requirements. Their disjunct distributions are probably the result of predation by introduced rodents, with populations of both having apparently been extirpated by ship rats (Rattus rattus) at one documented site (Taukihepa/Big South Cape Island). Within Fiordland, flax weevils were previously known from a single small island in Breaksea Sound, and knobbled weevils had been reported from five outer islands, from Secretary Island south to Resolution Island. We report the presence of both species in Dusky Sound, and flax weevils in Chalky and Preservation Inlets, based on surveys of 134 islands in 2016 and 2017. Signs of flax weevil feeding were recorded on 56 widely scattered islands, with live or dead animals found on seven of these during the limited search time available. A single knobbled weevil was found at night on a small island in the Seal Islands, southwest of Anchor Island. -
Re-Establishing North Island Kākā (Nestor Meridionalis Septentrionalis
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. Re-establishing North Island kākā (Nestor meridionalis septentrionalis) in New Zealand A thesis presented in fulfilment of the requirements for the degree of Master of Science In Conservation Biology Massey University Auckland, New Zealand Tineke Joustra 2018 ii For Orlando, Aurora and Nayeli “I don’t want my children to follow in my footsteps, I want them to take the path next to me and go further than I could have ever dreamt possible” Anonymous iii iv Abstract Recently there has been a global increase in concern over the unprecedented loss of biodiversity and how the sixth mass extinction event is mainly due to human activities. Countries such as New Zealand have unique ecosystems which led to the evolution of many endemic species. One such New Zealand species is the kākā (Nestor meridionalis). Historically, kākā abundance has been affected by human activities (kākā were an important food source for Māori and Europeans). Today, introduced mammalian predators are one of the main threats to wild kākā populations. Although widespread and common throughout New Zealand until the 1800’s, kākā populations on the mainland now heavily rely on active conservation management. The main methods of kākā management include pest control and re-establishments. This thesis evaluated current and past commitments to New Zealand species restoration, as well as an analysis of global Psittacine re-establishment efforts. -
Scenic & Nature
FIORDLAND DISCOVERY 7-DAY FIORDLAND / TE WAHIPOUNAMU EXPEDITIONS SCENIC & NATURE The massive glaciers that tore the landscape Seals apart 15,000 years ago left 14 fascinating fiords, Fiordland is home to the New Zealand fur seal the northernmost being the famous Milford Sound, (kekeno). Although almost hunted to extinction in with its narrow valley and steep cliffs, and the the 1800s, New Zealand now boasts approximately southernmost being Dusky Sound, and Chalky and 80,000 fur seals, with a large population found in Preservation Inlets. Dusky Sound. Strictly speaking, a “sound” is formed by a river, Dolphins are frequently seen in the sounds and, on rare occasions, pilot, humpback and Southern Right while a “fiord” is a glacier-formed valley. Fiordland’s whales. Orca have been spotted along the coast and southern fiords are much larger than its northern it is always a special privilege to see these incredible fiords, with mountains and hills complementing their animals. islands and coves. The remote islands in particular have been a real opportunity to establish bird Underwater sanctuaries, such as Anchor Island, which is now Fiordland is home to ten marine reserves. Depending home to the likes of the kakapo and saddleback. on the weather, we may use the ROV to view the Five Fingers Peninsula and Wet Jacket Arm reserves Fiordland receives about 6500mm of rainfall each in Dusky Sound and the Long Sound Reserve at the year, the perfect catalyst for beautiful waterfalls head of the Preservation Inlet. and lush podocarp forest, both abundant in Dusky Sound. This rainfall also creates a freshwater layer The extreme amount of rainfall in the fiords results in a freshwater surface layer that can be as deep on top of the fiords, resulting in a unique marine as seven metres. -
Taxon Plan for Northern and Southern Fiordland Tokoeka (Apteryx Australis Australis)
Taxon plan for northern and southern Fiordland tokoeka (Apteryx australis australis) Strategic plan for the recovery of northern and southern Fiordland tokoeka, for the period 2015–2025 and beyond Hannah Edmonds Cover: Fiordland tokoeka, Apteryx australis. Photo: James T. Reardon ISBN 978–0–478–15040–7 (web PDF) © Copyright June 2015, New Zealand Department of Conservation. This report may be cited as: Edmonds, H. 2015: Taxon plan for northern and southern Fiordland tokoeka (Apteryx australis australis): strategic plan for the recovery of northern and southern Fiordland tokoeka, for the period 2015–2025 and beyond. Department of Conservation, Te Anau. 25 p. In the interest of forest conservation, we support paperless electronic publishing. CONTENTS Preface 2 Executive summary 3 1. Introduction 3 2. Plan term and review date 4 3. Context 4 3.1 Taxonomy 4 3.2 Biology and ecology 5 3.3 Past and present distribution, and population trends 5 3.4 Threat status 6 3.5 Agents of decline and current threats 6 3.6 Past and current management 7 3.6.1 Productivity and chick survival 7 3.6.2 Distribution 8 3.6.3 Offshore islands 8 3.7 Cultural importance 9 3.8 Public awareness, key stakeholders and associates 9 3.9 Preferred option for recovery and recovery principles 9 4. Goals 10 4.1 Long-term recovery goal 10 4.2 Goals for the term of this taxon plan 10 4.2.1 Management 10 4.2.2 Community relations and engagement 10 4.2.3 Research and innovation 10 5. Implementation 11 5.1 Management 11 5.1.1 Topic 1: Taxon plans 11 5.1.2 Topic 2: Best practice 12 -
(Strigops Habroptilus) on Maud Island
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Lincoln University Research Archive 143 Seasonal changes in home range size and habitat selection by kakapo (Strigops habroptilus) on Maud Island JULIE WALSH Abstract Seasonal changes in home range size and habitat selection of kakapo Ecology and Entomology Group, P.O. Box 84, (Strigops habroptilus) were investigated on Maud Island. Kakapo were radio-tracked Lincoln University, New Zealand. at night in each of the four seasons between December 2000 and October 2001. [email protected] Home ranges were estimated for four adult males, three juvenile males and two juvenile females in each season and for nine females in summer, each based on KERRY-JAYNE WILSON 20 radio-fixes per season. Home range size varied from 1.8 to 145.0 ha using the Bio-Protection and Ecology Division, P.O. minimum convex polygon method. Home ranges were smallest in winter. Habitat Box 84, Lincoln University, New Zealand selection was determined by overlaying the kakapo locations and home ranges on a vegetation map of the island. For each season selection ratios were calculated GRAEME P. ELLIOTT for each vegetation community. Pine plantation (Pinus radiata) was selected for in Research, Development & Improvement summer, whereas the treeland community dominated by five- fingerPseudopanax ( Division, Department of Conservation, arbereus) was selected for in the autumn. Dense pole stands of manuka Private Bag 5, Nelson, New Zealand (Leptospemum scoparium) and pasture communities were avoided by kakapo. Walsh, J.; Wilson, K-J.; Elliott, G.P. 2006. Seasonal changes in home range size and habitat selection by kakapo (Strigops habroptilus) on Maud Island. -
Abundance and Future Options for Wetapunga on Little Barrier Island
Abundance and future options for wetapunga on Little Barrier Island SCIENCE FOR CONSERVATION: 48 George Gibbs and Mary McIntyre Published by Department of Conservation P.O. Box 10-420 Wellington, New Zealand 1 Science for Conservation presents the results of investigations contracted to science providers outside the Department of Conservation. Reports are subject to peer review within and outside the Department. May 1997, Department of Conservation ISSN 1173-2946 ISBN 0-478-01896-7 This publication originated from work done under Department of Conservation contract 1959 carried out by George Gibbs and Mary McIntyre, School of Biological Sciences, Victoria University, PO Box 600, Wellington. It was approved for publication by the Director, Science and Research Division, Department of Conservation, Wellington. Cataloguing-in-Publication data Gibbs, George W. (George William), 1937– Abundance and future options for wetapunga on Little Barrier Island / George Gibbs and Mary McIntyre. Wellington, N.Z. : Dept. of Conservation, 1997. 1 v. ; 30 cm. (Science for conservation, 1173-2946 ; 48.) Includes bibliographical references. ISBN 0478018967 1. Giant wetas- -New Zealand- -Little Barrier Island. 2. Weta punga. I. McIntyre, M. E. (Mary E.) II. Title. III. Series: Science for conservation (Wellington, N.Z.) ; 48. 595.7260993245 20 zbn97-045241 2 CONTENTS Abstract 5 1. Introduction 5 1.1 Objectives 6 1.2 Visits to Little Barrier Island 6 2. Assessment of numbers 6 2.1 Methods 7 2.2 Results 8 2.3 Discussion of population size 8 3. Habitat use 9 3.1 Use of shelters 10 3.2 Radiotracking study 10 3.3 Discussion of predators and role of shelters 12 4. -
Breeding Petrels of Dusky Sound, Fiordland – Survivors from a Century of Stoat Invasions
136 Notornis, 2017, Vol. 64: 136-153 0029-4470 © The Ornithological Society of New Zealand Inc. Breeding petrels of Dusky Sound, Fiordland – survivors from a century of stoat invasions COLIN M. MISKELLY* ALAN J.D. TENNYSON JEAN-CLAUDE STAHL Museum of New Zealand Te Papa Tongarewa, PO Box 467, Wellington 6140, New Zealand ANDREW F. SMART HANNAH K. EDMONDS PETER G. MCMURTRIE Department of Conservation, PO Box 29, Te Anau 9600, New Zealand Abstract A total of 49 breeding colonies of 3 petrel species was found on 44 of 56 islands surveyed in Dusky Sound, Fiordland National Park, New Zealand, in November 2016. Sooty shearwater (Puffinus griseus) was the most widespread and abundant species, with an estimated 21,400 burrows on 35 islands. Mottled petrels (Pterodroma inexpectata) were breeding on 12 islands (5500 burrows estimated), and broad-billed prions (Pachyptila vittata) on 2 islands (560 burrows estimated). Sooty shearwaters were found breeding among mottled petrels on 4 islands, and among broad-billed prions on 1 island. This is a 5-fold increase in the number of petrel colonies in Dusky Sound identified in published accounts, and the first estimate of the number of burrows on each island. Long-term survival of most or all of these colonies is dependent on ongoing control of stoats (Mustela erminea) in Dusky Sound. However, we suggest that islands too small to support a resident stoat population provided partial refugia for petrels, even if the islands are within stoat swimming range, allowing petrels to persist for multiple generations. In contrast, petrels were apparently rapidly extirpated from islands over 100 ha, where stoats maintained a resident population. -
A Parrot Apart: the Natural History of the Kakapo (Strigops Habroptilus), and the Context of Its Conservation Management
A parrot apart: the natural history of the kakapo (Strigops habroptilus), and the context of its conservation management RALPH G. POWLESLAND Abstract Since the last review of kakapo biology, published 50 years ago, much Research, Development & Improvement has been learnt as a result of the transfer of all known individuals to offshore islands, Division, Department of Conservation, P.O. and their intensive management to increase adult survival and productivity. This Box 10-420, Wellington, New Zealand review summarises information on a diversity of topics, including taxonomy, plumage, [email protected] moult, mass, anatomy, physiology, reasons for decline in distribution, present numbers and status, sex ratio, habitat, home range, foraging activities, diet, voice, DON V. MERTON breeding biology, nesting success, sexual maturity, and adult survival. In addition, Honorary Research Associate, Research, those kakapo attributes that compromise its long-term survival in present-day New Development & Improvement Division, Zealand are discussed, along with management practises developed to overcome Department of Conservation, P.O. Box 10- these problems. 420, Wellington, New Zealand Powlesland, R.G.; Merton, D.V.; Cockrem, J.F. 2006. A parrot apart: the natural JOHN F. COCKREM history of the kakapo (Strigops habroptilus), and the context of its conservation Conservation Endocrinology Research management. Notornis 53 (1): 3 - 26. Group, Institute of Veterinary, Animal & Biomedical Sciences, Massey University, Keywords Kakapo; Strigops habroptilus; Psittacidae; endangered species; review; Private Bag 11-222, Palmerston North, natural history; management practices; predatory mammals New Zealand INTRODUCTION The kakapo (Strigops habroptilus) is a large parrot (males 1.6 – 3.6 kg, females 0.9 – 1.9 kg) (Higgins 1999), with finely barred or mottled yellowish-green plumage. -
Mustela Erminea And) and Managementred Deer ( Cervus Elaphus ) Off Islands in Fiordland
Edge, K-A.; D. Crouchley, P. McMurtrie, M.J. Willans,Island and A. Byrom.invasives: Eradicating eradicationstoats ( Mustela erminea and) and managementred deer ( Cervus elaphus ) off islands in Fiordland Eradicating stoats (Mustela erminea) and red deer (Cervus elaphus) off islands in Fiordland K-A. Edge 1, D. Crouchley 1, P. McMurtrie 1, M.J. Willans 2, and A. Byrom 3 1Department of Conservation, Te Anau Area Offi ce, PO Box 29, Lakefront Drive, Te Anau 9640, New Zealand. <[email protected]>. 2The Wilderness, RD Te Anau-Mossburn Highway, Te Anau, NZ. 3Manaaki Whenua - Landcare Research, PO Box 40, Lincoln 7640, New Zealand. Abstract In 2004, the New Zealand Government allocated NZ$7.1M to eradicate stoats ( Mustela erminea ) and red deer (Cervus elaphus ) from Fiordland’s two largest islands: Secretary Island (8100 ha) and Resolution Island (21,000 ha), in SW New Zealand. Both islands are rugged and within the swimming range of stoats and deer from the mainland. Here we apply the six strategic rules for achieving eradication to the Secretary and Resolution islands programme and use these rules as means of assessing progress fi ve years into the campaign. For these programmes ‘eradication’ has been defi ned as the complete removal of the stoat and deer populations, and the establishment of long-term control to manage reinvasion. While the original eradication objectives are yet to be achieved, the planned conservation outcomes are on track; several threatened species of birds have been successfully reintroduced and the regeneration of palatable plants is apparent. The conservation importance of large islands such as Secretary and Resolution in terms of New Zealand’s commitments to international biodiversity conventions and restoration goals cannot be overstated. -
A History of Kākāpō
A history of kākāpō Pre-human settlement Pre-human settlement Kākāpō are abundant throughout New Māori settlement Zealand. Māori settlers bring kiore (Polynesian rat) and kurī (Polynesian dog). Māori also hunt kākāpō. 1800s Kākāpō are confined to 1800 1894 the central North Island Government’s first and forested areas of the attempt to save the South Island. species. Conservation European settlers bring rats, ranger Richard Henry stoats, cats and extensive habitat loss moved several hundred begins. Kākāpō began to decline rapidly. kākāpō to predator-free Lithograph: J G Keulemans, 1872, London. Resolution Island in Fiordland. Richard Henry, 1900. 1900 Source: Hocken Library, Dunedin Stoats reach Resolution Island and begin the eventual destruction of the entire 1949–1967 kākāpō population 1900 there. More than 60 expeditions to find kākāpō, focusing on Fiordland, with only 6 males caught. Species seems doomed to extinction. 1974–1975 Three Fiordland male kākāpō, including Richard 1970 1973–1977 Henry, are transferred to offshore island sanctuary No females and 18 males are found in Fiordland. Maud Island (Te Pāteka). Only one, Richard Henry, lives to pass on his genes to the current population. 1980 Cats are eradicated from Te Hauturu-o-Toi/Little 1977 Barrier island in the Hauraki Gulf/Tīkapa Moana. Estimate of 200 kākāpō found living on Stewart Island/Rakiura. First female kākāpō is found on Stewart Island/ Rakiura. Use of tracker dogs begins as 1979 cage trapping is found to be First male kākāpō, named Mawson, is captured on too slow. 16 birds are caught Stewart Island/Rakiura. including 3 females. First 2 Stewart Island/Rakiura 1980 birds transfered to Maud 1981–1982 Island (Te Pāteka).