Reintroduction Specialist Group Oceania Newsletter December 2007
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RESEARCH Factors Limiting Kererū (Hemiphaga Novaeseelandiae) Populations Across New Zealand
CarpenterNew Zealand et al.: Journal Limiting of Ecology factors for(2021) kerer 45(2):u 3441 © 2021 New Zealand Ecological Society. 1 RESEARCH Factors limiting kererū (Hemiphaga novaeseelandiae) populations across New Zealand Joanna K. Carpenter1* , Susan Walker1 , Adrian Monks1 , John Innes2 , Rachelle N. Binny3,4 and Ann-Kathrin V. Schlesselmann1 1Manaaki Whenua – Landcare Research, Private Bag 1930, Dunedin, New Zealand 2Manaaki Whenua – Landcare Research, Private Bag 3127, Hamilton, New Zealand 3Manaaki Whenua – Landcare Research, PO Box 69040, Lincoln, New Zealand 4Te Pūnaha Matatini, Centre of Research Excellence, New Zealand *Author for correspondence (Email: [email protected]) Published online: 25 June 2021 Abstract: Kererū declined rapidly following European settlement in New Zealand, and they remain at a reduced density. We assessed three sources of information to test the hypothesis that predation by introduced mammals and abundance of food resources are the two major factors determining kererū abundance across New Zealand. First, we reviewed the literature on factors affecting the vital rates of kererū. This analysis showed that predation is the cause of most nest failures and deaths in kererū. Second, we examined data from a major database of bird sanctuary outcomes across New Zealand to evaluate long-term responses of kererū to intensive pest control at local scales. Kererū detections did not always increase following predator control, which suggests that food supply or forest area may be more important limiting factors at some sanctuaries. Third, to understand the factors underlying temporal and spatial kererū distribution patterns at a national scale, we assessed changes and patterns in kererū local occupancy through time using data from the 1969–1979 and 1999–2004 editions of the Atlas of Bird Distribution in New Zealand. -
Best Practice Techniques for the Translocation of Whiteheads (Popokatea, Mohoua Albicilla)
Best practice techniques for the translocation of whiteheads (popokatea, Mohoua albicilla) Ralph Powlesland and Kevin Parker Cover: Whitehead, Tiritiri Matangi Island. Photo: Martin Sanders. © Copyright April 2014, New Zealand Department of Conservation Published by the Terrestrial Ecosystems Unit, National Office, Science and Capability Group, Department of Conservation, PO Box 10420, The Terrace, Wellington 6143, New Zealand. Editing and design by the Publishing Team, National Office, Department of Conservation, PO Box 10420, The Terrace, Wellington 6143, New Zealand. CONTENTS Abstract 1 1. Introduction 2 2. Animal welfare requirements 3 3. Transfer team 3 4. Time of year for transfer 3 5. Number of transfers 4 6. Composition of transfer group 4 7. Sexing whiteheads 4 7.1 Appearance 4 7.2 Measurements 5 7.3 DNA sexing 6 8. Ageing whiteheads 7 9. Capture 7 10. Transfer to base for ‘processing’ 7 11. Processing the birds 8 12. Temporary housing in aviaries 10 12.1 Capture in the aviary on transfer day 12 13. Feeding 14 14. Whitehead husbandry 15 15. Transfer box design 15 16. Transport 16 17. Release 17 18. Post-release monitoring 17 18.1 Purpose 17 18.2 Recommended monitoring 19 19. Record keeping 19 20. References 21 Appendix 1 Details of report contributors 23 Appendix 2 Feeding protocol for whiteheads being held in temporary aviaries 24 Appendix 3 Recipes for whitehead foods 25 Best practice techniques for the translocation of whiteheads (popokatea, Mohoua albicilla) Ralph Powlesland1 and Kevin Parker2 1 606 Manaroa Road, Manaroa, RD 2, Picton, New Zealand [email protected] 2 Parker Conservation, Auckland, New Zealand parkerconservation.co.nz Abstract This document outlines best practice techniques for the translocation of whiteheads (popokatea, Mohoua albicilla). -
MAUNGATAUTARI ECOLOGICAL ISLAND TRUST Annual General Meeting Unconfirmed Minutes 22 October 2019
MAUNGATAUTARI ECOLOGICAL ISLAND TRUST Annual General Meeting unconfirmed Minutes 22 October 2019 unconfirmed minutes of the Annual General Meeting of the Maungatautari Ecological Island Trust held in Te Manawa o Matariki room at the Don Rowlands Complex, Mighty River Domain at Lake Karāpiro on Tuesday, 22 October 2019 commencing at 6.00m. 1 Opening Karakia – Taiapa Kara; Mihi Whakatau – Johnson Raumati; and MEIT response – Simon Anderson 2 Present Poto Davies (co-Chair), Don Scarlet (Acting co-Chair), Aaron Barnsdall, Graham Parker, Maryanne Sambells Simon Anderson, Steve Cooper, Clare Crickett, Joce Dawkins, Neville Dawkins, Gabrielle Dela Rue, Anne Deulin, George Dingle, Antonia Eames, Ruth Etches, Joyce Fleming, Margaret Gasquoine, Adua Geremia, Ron Guest, Beth Guest, Angela Harris, John Innes, Bryan Jenkin, Nanette Jenkin, Taiapa Kara, Colleen Lecky, Pam Lemming, Helen Lewis, Alan Livingston, Rod Lugton, Rosemary Lugton, Linda McCarter, Nigel McCarter, David Mans, Graham Mayall, Craig Montgomerie, Brent Montgomerie, Robyn Nightingale, Kurarangi Paki, Elaine Parkinson, Annie Perkins, Pat Quin, Johnson Raumati, Clare Ravenscroft, Sue Reid, Dan Ritchie, Tony Roxburgh, Sally Sheedy, Neil Smith, Carol Tauroa, Lance Tauroa, Tao Tauroa, Kiri Joy Wallace, Brian Walton, Harry Wilson Phil Lyons, Sue Dela Rue, Daniel Howie, Nathalia Jellyman, Jessica Meade, Maureen Poole, Daniel Scanlon, Ricki-Lee Scanlon, Ally Tairi, Janelle Ward 3 Apologies The apologies from Rahui Papa, Gary Dyet, John Erica, Raewyn Jones, Raewyn Kirkham, James Matthews, Jim Mylchreest, Dylan Newbold, Vaughan Payne Ashley Reid, Bruce Scott, Graham Scott, Dene Sambells, Pam Walton were accepted. unconfirmed Maungatautari Ecological Island Trust AGM Minutes – 22 October 2019 Page 1 4 WELCOME AND INTRODUCTION OF TRUSTEES On behalf of the Trust, Acting Co-Chair Don Scarlet welcomed everyone to the 2019 AGM and introduced all current Trustees present at the meeting. -
The Distribution and Current Status of New Zealand Saddleback Philesturnus Carunculatus
Bird Conservation International (2003) 13:79–95. BirdLife International 2003 DOI: 10.1017/S0959270903003083 Printed in the United Kingdom The distribution and current status of New Zealand Saddleback Philesturnus carunculatus SCOTT HOOSON and IAN G. JAMIESON Department of Zoology, University of Otago, P.O. Box 56, Dunedin, New Zealand Summary This paper reviews and updates the distribution and status of two geographically distinct subspecies of New Zealand Saddleback Philesturnus carunculatus, a New Zealand forest passerine that is highly susceptible to predation by introduced mammals such as stoats and rats. The recovery of the North Island and South Island saddleback populations has been rapid since translocations to offshore islands free of exotic predators began in 1964, when both subspecies were on the brink of extinction. South Island saddlebacks have gone from a remnant population of 36 birds on one island to over 1,200 birds spread among 15 island populations, with the present capacity to increase to a maximum of 2,500 birds. We recommend that South Island saddleback be listed under the IUCN category of Near Threatened, although vigilance on islands for invading predators and their subsequent rapid eradication is still required. North Island saddlebacks have gone from a remnant population of 500 birds on one island to over 6,000 on 12 islands with the capacity to increase to over 19,000 individuals. We recommend that this subspecies be downgraded to the IUCN category of Least Concern. The factors that limited the early recovery of saddlebacks are now of less significance with recent advances in predator eradication techniques allowing translocations to large islands that were formerly unsuitable. -
7. Prspresentationecologicalcorridor Final
Ecological Corridor Proposal • What is proposed? • Why do we want to do it? • How would it be implemented? • What would be the benefits? • Why should I be involved? Waipā District Plan already provides for a corridor. The proposed route is the Mangapiko stream (headwaters at Maungatautari) which enters the Waipā River at Pirongia village. From there the Ngaparierua stream links to Mt Pirongia. Why do we want to do it? • Successful large scale restoration projects at Maungatautari and Pirongia with native species set to spread out across the landscape • We need action to keep them safe once they leave the maunga. • We know our waterways need to be improved. • highly degraded habitat • vulnerable to pest plants and fish • elevated temperature and • poor water quality. • Mangapiko Stream is the ideal link between the two maunga Other Reasons • Capitalising on the good work already done by the Lower Mangapiko Streamcare Group. • Iwi connections to the awa will be transformed – cultural benefits • Huge potential for Maori business development and employment – economic benefits • Both MEIT and PRS use community collaboration extensively so able to engage networks and stakeholders – social benefits Wouldn’t it be amazing to see these in the Corridor? Kōkako Korimako/Bellbird Hihi/Stitchbird Tīeke/Saddleback Pōpokotea/Whitehead Pītoitoi/North Island Robin Kākā Titipounamu/Rifleman Miromiro/Tomtit Kārearea/NZ Falcon Pūweto/Spotless crake But how likely is it? Long tailed bats Kōkako video: https://www.youtube.com/watch?v=b1Y6djbURgw “Being able to see these kōkako up close fills me with more joy than I can put into words” Can we expect to see Kōkako in the Corridor? Yes! 1. -
DISSERTATION RESTORING ISLAND BIRDS and SEED DISPERSAL in NEW ZEALAND's FENCED MAINLAND ISLAND SANCTUARIES Submitted by Sara
DISSERTATION RESTORING ISLAND BIRDS AND SEED DISPERSAL IN NEW ZEALAND’S FENCED MAINLAND ISLAND SANCTUARIES Submitted by Sara Petrita Bombaci Graduate Degree Program in Ecology In partial fulfillment of the requirements For the Degree of Doctor of Philosophy Colorado State University Fort Collins, Colorado Summer 2018 Doctoral Committee: Advisor: Liba Pejchar Sarah Reed Julie Savidge Melinda Smith Copyright by Sara Petrita Bombaci 2018 All Rights Reserved ABSTRACT RESTORING ISLAND BIRDS AND SEED DISPERSAL IN NEW ZEALAND’S FENCED MAINLAND ISLAND SANCTUARIES Island ecosystems are global biodiversity hotspots, but many island species face population declines and extinction. These losses are mainly driven by invasive mammals that consume or compete with native animals and degrade their habitats. The decline of island animal populations may also impact ecosystem processes that depend on them, e.g. seed dispersal, pollination, and nutrient cycling. The island nation of New Zealand has pioneered a unique solution – fenced mainland island sanctuaries – which exclude invasive mammals from natural habitats and provide opportunities to restore native birds and other wildlife. Yet, critics question whether sanctuaries, which are costly and require continuous maintenance, effectively conserve birds and ecosystems, given minimal research on sanctuary project outcomes. I assessed if sanctuaries are an effective conservation tool for restoring birds and seed dispersal in New Zealand. I compared bird population densities and bird-mediated seed dispersal in three fenced sanctuary sites to three paired reference sites (with minimal mammal control). From January- April 2016 and 2017, I set seed traps to measure dispersed-seed abundance, conducted focal tree observations to determine foraging rates for six tree species, and used distance sampling-based point counts to survey birds at randomly placed sampling locations within each site. -
Student Worksheet Biological Knowledge The
Student Worksheet The use of Open Sanctuaries. Example: Tiritiri Matangi Island Conserves and Protects the Native Flora and Fauna of New Zealand NCEA Bio 3.2 Ach Std 91602, Int Ass,3 credits. Integrate biological knowledge to develop an informed response to a socio-scientific issue. Biological Knowledge Biological Concepts and Processes 1. What are Sanctuaries: ___________________ for native plant and endemic/native animal species. 2. What does Open Sanctuary mean? A sanctuary with endangered animals and plants (threatened fauna and flora) that_________________________ for the public and education groups to visit. 3. What does a Closed Sanctuary mean? Primary aim is to__________________________ and permits are required. Strict quarantine measures are in place eg Te Hauturu-o-Toi/Little Barrier Island (LBI). 4. What is special about our biodiversity? 5. Why is the NZ biodiversity so different? 6. Why is our native flora and fauna at risk? 7. What are the risks? 8. Who poses a risk? 1 Tiritiri Matangi Education: B Hughes. Biological Implications What has taken place on Tiritiri? Social implications of the Use of Tiritiri Open Sanctuary 1. economic – 2. ethical - 3. cultural - 4. environmental After 30 yrs the island is well covered with vegetation and has had 16 species translocated,15 of which have produced breeding populations. Tīeke - saddleback, pōpokotea - whitehead, toutouwai - Nth. Is. robin are thriving and reaching carrying capacity (S shaped growth curve). Species that were present in 1984 who are winners today in terms of population numbers are: korimako - bellbird, tūī, kererū, kākāriki. Indirect benefits from the kiore eradication in 1993 has led to an increase in tree growth, insects and skinks; the Ruakawa gecko has reappeared along with the giant centipede. -
New Zealand Ecology Sanctuary Mountain Maungatautari
New Zealand Ecology Sanctuary Mountain Maungatautari Sanctuary Mountain Maungatautari is the largest ecological restoration project in New Zealand. The Mountain is surrounded by a 47-kilometer-long pest-proof fence, the longest in the world. This fence completely encircles 3400 hectares of forest, and the now extinct volcano. This forest includes an abundance of large and ancient trees. These trees were protected from logging by the establishment of the Maungatautari scenic reserve in 1929. However, the birdlife and the vegetation were damaged by the invasion of foreign species, including rats, pigs, goats, deer, weasels, cats and possums. By the 1980s there were no more kiwi on the mountain. This decimation of indigenous wildlife was seen across the country. To prevent mass extinction across New Zealand, a series of off shore islands became sanctuaries. The first was little barrier island in 1896, however this island was not predator free until the 1980’s. During the 1980’s several other islands became predator free with the use of hunting and 1080 poisoning. This included Auckland’s Tiritiri-Matangi Island. In the late 1990’s Wellington’s Zealandia was established, this had the first predator proof fence in the country. Following this, volunteers started to work to turn Maungatautari into the largest inland sanctuary in New Zealand. The first two small enclosures were fully fenced by the end of 2004. Then the rest of the Mountain was fully enclosed by the end of 2007. Pest eradication began with two large areal drops of the poison 1080. This was then followed by hunting and trapping. -
Stitchbird (Hihi), Notiomystis Cincta Recovery Plan
Stitchbird (Hihi), Notiomystis cincta Recovery Plan Threatened Species Recovery plan Series No. 20 Department of Conservation Threatened Species Unit PO Box 10-420 Wellington New Zealand Prepared by: Gretchen Rasch,Shaarina Boyd and Suzanne Clegg for the Threatened Species Unit. April 1996 © Department of Conservation ISSN 1170-3806 ISBN 0-478-01709-6 Cover photo: C.R. Veitch, Department of Conservation CONTENTS page 1. Introduction 1 2. Distribution and Cause of Decline 3 2.1 Past distribution 3 2.2 Present distribution 3 2.3 Possible reasons for decline 3 3. Ecology 7 3.1 Foods and feeding 7 3.2 Competition with other honeyeaters 7 3.3 Habitat 8 4. Recovery to Date 9 4.1 Transferred populations 9 4.2 Captive population 11 5. Recovery Strategy 13 5.1 Long term goal 13 5.2 Short term objectives 13 6. Work Plan 15 6.1 Protect all islands with stitchbirds 15 6.2 Monitor stitchbirds on Little Barrier island 15 6.3 Monitor and (where necessary) enhance stitchbird populations on existing transfer sites 16 6.4 Establish self-sustaining populations of stitchbirds in other locations 18 6.5 Support captive breeding programme 18 6.6 Advocacy 19 6.7 Research needs 20 References 23 Appendices 1. Stitchbird Ecology 2. Criteria for assessing suitability of sites for stitchbird transfer. FIGURES page 1. Present distribution of stitchbird (Notiomystis cincta) 4 2. Average number of stitchbirds counted per transect on Little Barrier Island 1975-1989 5 3. Percentage of food types in stitchbird diet, Little Barrier Island 1982-1984 7 Percentage of foods used by honeyeaters on Little Barrier 1982-1983 Appendix 1, p 1 Nectar used by honeyeaters in the Tirikakawa Valley, Little Barrier 1983-1984 Appendix 1, p2 TABLES page 1. -
New Zealand Comprehensive II 23Rd October – 8Th November 2017 Trip Report
New Zealand Comprehensive II 23rd October – 8th November 2017 Trip Report Gibson’s Wandering Albatross off Kaikoura by Erik Forsyth Trip Report compiled by Tour Leader Erik Forsyth Rockjumper Birding Tours View more tours to New Zealand Trip Report – RBL New Zealand - Comprehensive II 2017 2 Daily Diary New Zealand is a must for the serious seabird enthusiast. Not only will you see a variety of albatrosses, petrels and shearwaters, but there are multiple chances of getting out on the high seas and finding something unusual. Seabirds dominate this tour and views of most birds are right alongside the boat. There are also several land birds which are unique to these islands: the kiwis – terrestrial nocturnal inhabitants, the huge swamp-hen like Takahe – prehistoric in its looks and movements, and then the wattlebirds: the saddlebacks and kokako – poor flyers with short wings, which bound along the branches and on the ground. On this tour we had so many highlights, including close encounters with North Island, Southern Brown and Little Spotted Kiwis, walk-away views of a pair of North Island Kokako, both North and South Island Saddlebacks and a pair of the impressive South Island Takahe. With many boat trips the pelagic list was long, with Wandering, Northern and Southern Royal, Salvin’s, Black-browed, Campbell, White- capped and the scarce Grey-headed Albatrosses, Westland, Cook’s and White- chinned Petrels, Buller’s, Flesh-footed and Hutton’s Shearwaters, Common Diving New Zealand (Red-breasted) Plover by Erik Forsyth Petrel, and White-faced and the highly sought-after New Zealand Storm Petrels. -
Results of a Waikato Survey Pamela Kaval
UNIVERSITY OF WAIKATO Hamilton New Zealand The Value of Native Birds in New Zealand: Results of a Waikato Survey Pamela Kaval and Matthew Roskruge University of Waikato Department of Economics Working Paper in Economics 06/08 May 2008 Corresponding Author Pamela Kaval Department of Economics University of Waikato, Private Bag 3105, Hamilton, New Zealand Fax: +64 (07) 838 4331 Phone : +64 (07) 838 4045 Email: [email protected] Abstract Several New Zealand studies have placed a value on recreation. Very few have placed a value on native birdlife. In this report, we make a contribution to this deficiency in the literature. In December 2007 and January 2008, we conducted a phone survey in the Waikato Region of New Zealand. In total, 207 people took part in answering our 13 question survey on native birds. While this information has given us a great deal of insight into the values Waikato residents place on birdlife in the area, some of the most important things we have learned are as follows: 97% of respondents enjoy having birds in their area. The things they enjoy include listening to them, watching them, and that they are part of nature. The tui seems to be the most important bird respondents either see currently, or if they do not see it now, they would like to see it in the future. If there were a greater variety of bird types in their area, respondent well-being would significantly increase. There are several programs in the Waikato Region that are either directly or indirectly linked to an increase in the native bird populations including Maungatautari Ecological Mainland Island, pest control, and the Hamilton Halo Project. -
Proc for Pdf Making
Changes in bird numbers on Tiritiri Matangi Island, New Zealand, over the period of rat eradication M. F. Graham1 and C. R. Veitch2 1 9 Grendon Road, Titirangi, Auckland, New Zealand. 2 48 Manse Road, Papakura, New Zealand. Abstract Tiritiri Matangi is 25 km north of Auckland City in the Hauraki Gulf, New Zealand. Most of its forest cover was removed during many centuries of Maori and European occupation and farming. Some areas of extant forest canopy remained. Farming ceased in 1971. Since 1984 some 300,000 native trees have been planted. Twenty-seven species of native bird are naturally present and breeding on the island. Twenty-two exotic species introduced to main- land New Zealand have found their way to the island. Nine species of native bird have been translocated to the island. Data from bird counting transects within extant forest areas in spring are considered. The data from a three-year period before eradication of Pacific rats (Rattus exulans) in September 1993 are compared to a three-year period following rat eradication, with a three-year settling period between. A number of significant changes are recorded with both in- creases and decreases in bird numbers. These are attributed to the direct impact of the rats or changes in forest compo- sition following rat removal, or the data are confused by conservation management action beyond the immediate count areas. INTRODUCTION Tiritiri Matangi is a low-lying 220 ha island lying 4 km off were at one time plentiful had disappeared by 1908 (Dept the Whangaparaoa Peninsula and 25 km north of Auck- of Lands and Survey 1982).