DISSERTATION RESTORING ISLAND BIRDS and SEED DISPERSAL in NEW ZEALAND's FENCED MAINLAND ISLAND SANCTUARIES Submitted by Sara
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Hall Road, Kerikeri to Create a Retirement Village with 200 Villas and 76 Aged Care Beds
ASSESSMENT OF ECOLOGICAL VALUES AT 57C HALL ROAD AND 22 LIMELIGHT LANE, KERIKERI Report 2018 268 Prepared for KERIKERI LAND LIMITED NZE Quality System: Document Reference : p:\ Projects\2018 268 Kerikeri Land Report Revision : 2 Report Status : Final Prepared by : Dr Gary Bramley Reviewed by : Tricia Scott Approved by : Tricia Scott Date Created : 3 December 2018 Date Issued : 11 February 2020 Assessment of Ecological Values at 57C Hall Road and 22 Limelight Lane, KERIKERI Prepared for Kerikeri Land Limited TABLE OF CONTENTS SECTIONS 1. INTRODUCTION ........................................................................................................................ 1-3 1.1 BACKGROUND ............................................................................................................... 1-3 1.2 SCOPE AND METHODS ................................................................................................. 1-4 2. ECOLOGICAL CONTEXT AND VALUES................................................................................. 2-5 2.1 ECOLOGICAL CONTEXT ............................................................................................... 2-5 2.2 ECOLOGICAL VALUES .................................................................................................. 2-6 2.3 FAUNA VALUES .............................................................................................................. 2-9 2.3.1 Aquatic Fauna................................................................................................... 2-9 2.3.2 -
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). -
Oemona Hirta
EPPO Datasheet: Oemona hirta Last updated: 2021-07-29 IDENTITY Preferred name: Oemona hirta Authority: (Fabricius) Taxonomic position: Animalia: Arthropoda: Hexapoda: Insecta: Coleoptera: Cerambycidae Other scientific names: Isodera villosa (Fabricius), Oemona humilis Newman, Oemona villosa (Fabricius), Saperda hirta Fabricius, Saperda villosa Fabricius Common names: lemon tree borer view more common names online... EPPO Categorization: A1 list more photos... view more categorizations online... EU Categorization: A1 Quarantine pest (Annex II A) EPPO Code: OEMOHI Notes on taxonomy and nomenclature Lu & Wang (2005) revised the genus Oemona, which has 4 species: O. hirta, O. plicicollis, O. separata and O. simplicicollis. They provided an identification key to species and detailed descriptions. They also performed a phylogenetic analysis of all species, suggesting that O. hirta and O. plicicollis are sister species and most similar morphologically. HOSTS O. hirta is a highly polyphagous longhorn beetle. Its larvae feed on over 200 species of trees and shrubs from 63 (Lu & Wang, 2005; Wang, 2017) to 81 (EPPO, 2014) families. Its original hosts were native New Zealand plants, but it expanded its host range to many species exotic to New Zealand, ranging from major fruit, nut, forest and ornamental trees to shrubs and grapevines. Host list: Acacia dealbata, Acacia decurrens, Acacia floribunda, Acacia longifolia, Acacia melanoxylon, Acacia pycnantha, Acer pseudoplatanus, Acer sp., Aesculus hippocastanum, Agathis australis, Albizia julibrissin, Alectryon excelsus, Alnus glutinosa, Alnus incana, Aristotelia serrata, Asparagus setaceus, Avicennia marina, Avicennia resinifera, Azara sp., Betula nigra, Betula pendula, Betula sp., Brachyglottis greyi, Brachyglottis repanda, Brachyglottis rotundifolia, Buddleia davidii, Camellia sp., Carmichaelia australis, Casimiroa edulis, Cassinia leptophylla, Cassinia retorta, Castanea sativa, Casuarina cunninghamiana, Casuarina sp., Celtis australis, Cestrum elegans, Chamaecyparis sp., Chamaecytisus prolifer subsp. -
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. -
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. -
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. -
The Poisonous, Suspected, and Medicinal Plants of New Zealand
7« N.Z. JOURNAL Ol- AtiRR'.Ll.Tl'KIL feb. 20. 1923. THE POISONOUS, SUSPECTED, AND MEDICINAL PLANTS OF NEW ZEALAND. (Conlhiuett.) I). C. ASTON, IM.C., F.N.Z.Inst., Chemist to the Department. LEGUM1N0SAE. The flora of New Zealand is remarkable in containing so few genera, species, and individuals of that great family Leguininosac—the pea or pod-bearers—although it is the second largest family of flowering-plants, containing over four thousand genera and seven thousand species. Cheeseman (190b). indeed, considered (“ Manual/' p. 107) the paucity of legumes to be one of the must remarkable peculiarities of the flora. There are practically no native plants analogous to the clovers on the main islands of this Dominion, the alpine Swainsonia—the only approach to a herbaceous legume—being so rare as to be negligible. The family is represented by a comparatively small number of leafless broom-like shrubs, the well-known kowhai (Sophora tel rapt era), and the kaka-beak Cliant-hns puuiceus). Tlie kowhai is the one instance in the native flora of a suspected poisonous legume. Its affinities in other countries are certainly sus pected—namely, Sophora sericea and 5. secundiflora in America. The former is supposed to be one of tlie plants which cause " locoism "in horses. It may here be remarked that a number of poisonous plants in the wild pastures of America are termed " loco " weeds, the symptoms they occasion being termed " locoism." Regarding the New Zealand species of Sophora, which will probably be split up by future systematic botanists into a number of species, the only evidence tlie writer has as to the poisonous nature of the tree is that two persons were made very ill by eating food with a spoon made of kowhai wood. -
A Planter's Handbook for Northland Natives
A planter’s handbook for Northland natives Including special plants for wetlands, coast and bird food Tiakina nga manu, ka ora te ngahere. Ka ora te ngahere, ka ora nga manu. Look after the birds and the forest flourishes. If the forest flourishes, the birds flourish. Photo courtesy of ????? ACKNOWLEDGEMENTS All photos by Lisa Forester, Katrina Hansen, Jacki Byrd, Brian Chudleigh, Nan Pullman, Malcolm Pullman and Tawapou Coastal Natives. All images copyright of Northland Regional Council unless specified. First published 1999. Updated and reprinted 2020. ISBN: 978-0-909006-65-5. Choosing the right plants Are you deciding on what native Northland plants to use on your land? Whether you’re deciding on plants for landscaping or restoration, this handbook will help. Getting started Photo courtesy of Brian Chudleigh Read on to find out the size and growth rate of plants and which natives attract wildlife. While not listing every plant native to Northland, this book contains a wide range that may be available in local nurseries. Charts on each page show whether a plant provides food for birds, what its final height may be and how quickly it grows. The book also includes plants that will handle harsh coastal environments, windy and/or dry Although primarily a fruit locations and frosts, as well as those plants eater the kūkupa will that tolerate shade or a wetter habitat. This sometimes eat the flowers information will help you choose plants that and new shoots of the kōwhai, Sophora microphylla will benefit you, the local wildlife, and the and some other trees, when environment. -
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. -
“Sanctuary Mountain” - Maungatautari Kokako Census October 2018
“Sanctuary Mountain” - Maungatautari Kokako Census October 2018 Ian Flux 1 Abstract. This report describes the third, sequential, census of kokako at “Sanctuary Mountain” - Maungatautari. This census was conducted during September and October of 2018. Nineteen territorial pairs were confirmed, a further pair was observed for only 15 minutes so is treated as unconfirmed. Six territorial singles were located, making up a total of 44 confirmed territorial individuals. The 22 un-banded territorial kokako located suggest good productivity and recruitment. Overall, as a result of further recruitment of previously transferred kokako and productivity, the territorial population grew by 122% during the past 12 months. Kokako favour higher elevations at Maungatautari; 69% of territorial kokako were located in highest (over 550 m) 20% of the habitat; the lowest 55% of the habitat (under 450m) contained only 11% of territorial kokako. Twenty-two banded kokako were sighted during this census including 5 not seen last season and an additional 4 not seen since their release. The total “potential founders” (individuals paired through a breeding season) is now 26, including 3 un-banded males which are assumed to have been old birds from a relict Maungatautari population. The Maungatautari kokako population is now more stable, more responsive to play-back, and more vocal than it has been during the past 2 seasons – in general kokako here now behave and react similarly to kokako in any other population. Contents. Introduction 3 Methods 4 Results 5 Survey coverage map 6-7 Territorial kokako located 8-9 Map of territories 10 Banded kokako records 11-12 Un-banded kokako 13 Feeding observations 15 Conclusions 16 Recommendations 18 Acknowledgements 19 References 20 2 1.0 Introduction. -
The Responses of New Zealand's Arboreal Forest Birds to Invasive
The responses of New Zealand’s arboreal forest birds to invasive mammal control Nyree Fea A thesis submitted to the Victoria University of Wellington in fulfilment of the requirements for the degree of Doctor of Philosophy Victoria University of Wellington Te Whare Wānanga o te Ūpoko o te Ika a Māui 2018 ii This thesis was conducted under the supervision of Dr. Stephen Hartley (primary supervisor) School of Biological Sciences Victoria University of Wellington Wellington, New Zealand and Associate Professor Wayne Linklater (secondary supervisor) School of Biological Sciences Victoria University of Wellington Wellington, New Zealand iii iv Abstract Introduced mammalian predators are responsible for over half of contemporary extinctions and declines of birds. Endemic bird species on islands are particularly vulnerable to invasions of mammalian predators. The native bird species that remain in New Zealand forests continue to be threatened by predation from invasive mammals, with brushtail possums (Trichosurus vulpecula) ship rats (Rattus rattus) and stoats (Mustela erminea) identified as the primary agents responsible for their ongoing decline. Extensive efforts to suppress these pests across New Zealand’s forests have created “management experiments” with potential to provide insights into the ecological forces structuring forest bird communities. To understand the effects of invasive mammals on birds, I studied responses of New Zealand bird species at different temporal and spatial scales to different intensities of control and residual densities of mammals. In my first empirical chapter (Chapter 2), I present two meta-analyses of bird responses to invasive mammal control. I collate data from biodiversity projects across New Zealand where long-term monitoring of arboreal bird species was undertaken.