Monitoring and Management of Kereru (Hemiphaga Novaeseelandiae)
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New Zealand Comprehensive II Trip Report 31St October to 16Th November 2016 (17 Days)
New Zealand Comprehensive II Trip Report 31st October to 16th November 2016 (17 days) The Critically Endangered South Island Takahe by Erik Forsyth Trip report compiled by Tour Leader: Erik Forsyth RBL New Zealand – Comprehensive II Trip Report 2016 2 Tour Summary New Zealand is a must for the serious seabird enthusiast. Not only will you see a variety of albatross, petrels and shearwaters, 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 alongside the boat. There are also several land birds which are unique to these islands: kiwis - terrestrial nocturnal inhabitants, the huge swamp hen-like Takahe - prehistoric in its looks and movements, and wattlebirds, the saddlebacks and Kokako - poor flyers with short wings Salvin’s Albatross by Erik Forsyth which bound along the branches and on the ground. On this tour we had so many highlights, including close encounters with North Island, South Island and Little Spotted Kiwi, Wandering, Northern and Southern Royal, Black-browed, Shy, Salvin’s and Chatham Albatrosses, Mottled and Black Petrels, Buller’s and Hutton’s Shearwater and South Island Takahe, North Island Kokako, the tiny Rifleman and the very cute New Zealand (South Island wren) Rockwren. With a few members of the group already at the hotel (the afternoon before the tour started), we jumped into our van and drove to the nearby Puketutu Island. Here we had a good introduction to New Zealand birding. Arriving at a bay, the canals were teeming with Black Swans, Australasian Shovelers, Mallard and several White-faced Herons. -
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. -
SOUTH ISLAND SADDLEBACK RECOVERY PLAN (Philesturnus Carunculatus Carunculatus )
THREATENED SPECIES RECOVERY PLAN SERIES NO.11 SOUTH ISLAND SADDLEBACK RECOVERY PLAN (Philesturnus carunculatus carunculatus ) Prepared by Andy Roberts (Southland Conservancy) for the Threatened Species Unit Threatened Species Unit Department of Conservation P.O. Box 10-420 Wellington New Zealand © 1994 ISSN 1170-3806 ISBN 0-478-01481-9 Key words: South Island saddleback, Philesturnus carunculatus carunculatus, recovery plan ABSTRACT South Island saddlebacks (tieke) were widely distributed over the South and Stewart Islands in the 19th century. Their rapid decline was documented during the latter 19th century. Following a rodent invasion on their sole remaining island habitat South Island saddlebacks were under threat of immediate extinction. This was thwarted by prompt translocations of remaining birds to nearby predator-free islands. This plan outlines conservation goals and suggests options for continuing the recovery of this subspecies. Recovery is to be achieved through a programme of island habitat restoration and saddleback translocations. Eradication of rodents and weka is promoted by this plan, in some instances this plan suggests that discussions be held with the local Iwi to determine the appropriateness of these eradications. Saddlebacks are to be introduced or re-introduced to a number of islands around the South Island coast. When recovery has been achieved South Island saddleback populations may be established on up to 26 islands with a total of about 4000 individuals. At this population level they will not be ranked as threatened, but be classified as rare and no longer requiring a programme of on-going intensive conservation management. Recovery management proposed in this plan will be undertaken jointly by Department of Conservation staff, Iwi representatives and members of the public. -
Biodiversity of the Kermadec Islands and Offshore Waters of the Kermadec Ridge: Report of a Coastal, Marine Mammal and Deep-Sea Survey (TAN1612)
Biodiversity of the Kermadec Islands and offshore waters of the Kermadec Ridge: report of a coastal, marine mammal and deep-sea survey (TAN1612) New Zealand Aquatic Environment and Biodiversity Report No. 179 Clark, M.R.; Trnski, T.; Constantine, R.; Aguirre, J.D.; Barker, J.; Betty, E.; Bowden, D.A.; Connell, A.; Duffy, C.; George, S.; Hannam, S.; Liggins, L..; Middleton, C.; Mills, S.; Pallentin, A.; Riekkola, L.; Sampey, A.; Sewell, M.; Spong, K.; Stewart, A.; Stewart, R.; Struthers, C.; van Oosterom, L. ISSN 1179-6480 (online) ISSN 1176-9440 (print) ISBN 978-1-77665-481-9 (online) ISBN 978-1-77665-482-6 (print) January 2017 Requests for further copies should be directed to: Publications Logistics Officer Ministry for Primary Industries PO Box 2526 WELLINGTON 6140 Email: [email protected] Telephone: 0800 00 83 33 Facsimile: 04-894 0300 This publication is also available on the Ministry for Primary Industries websites at: http://www.mpi.govt.nz/news-resources/publications.aspx http://fs.fish.govt.nz go to Document library/Research reports © Crown Copyright - Ministry for Primary Industries TABLE OF CONTENTS EXECUTIVE SUMMARY 1 1. INTRODUCTION 3 1.1 Objectives: 3 1.2 Objective 1: Benthic offshore biodiversity 3 1.3 Objective 2: Marine mammal research 4 1.4 Objective 3: Coastal biodiversity and connectivity 5 2. METHODS 5 2.1 Survey area 5 2.2 Survey design 6 Offshore Biodiversity 6 Marine mammal sampling 8 Coastal survey 8 Station recording 8 2.3 Sampling operations 8 Multibeam mapping 8 Photographic transect survey 9 Fish and Invertebrate sampling 9 Plankton sampling 11 Catch processing 11 Environmental sampling 12 Marine mammal sampling 12 Dive sampling operations 12 Outreach 13 3. -
Manawahe Kokako Survey Report November 2014
Manawahe Kokako Survey Report November 2014 Photo by Bruce Bancroft Prepared for Bay of Plenty Regional Council and the Manawahe Kokako Trust By Bruce Bancroft and Nicole Bancroft 1 Table of Contents Introduction ............................................................................................................................. 3 Methods ................................................................................................................................... 3 Results ..................................................................................................................................... 4 Table 1. Kokako Population Comparisons 2013/2014 ...................................................... 4 Other Birds .............................................................................................................................. 4 Pest Control ............................................................................................................................. 5 Discussion ............................................................................................................................... 5 Table 2. Manawahe Kokako Survey Results Over Time ................................................... 7 Table 3. Manawahe Kokako Pairs change over time. ........................................................ 8 Recommendations ................................................................................................................... 9 References: ......................................................................................................................... -
Assessment of the Weed Control Programme on Raoul Island, Kermadec Group
4000 in extent (Devine 1975).At Low Flat shore hibiscus is extensive in the south-western corner of the flat. In 1993 one small plant was found growing above the strand line at Coral Bay and the same plant was first seen in 1991 (Clapham 1991b). This plant may have established from seed as shore hibiscus is a common strand plant in the Pacific (Merrill 1940). What is uncertain, though, is where the seed originated from. Seedlings have only occasionally been recorded under the large stands on Raoul Island (Clapham 1991b), and seed set has not been observed. It is possible that the Coral Bay plant germinated from seed dispersed from elsewhere in the Pacific. Alternatively, the plant at Coral Bay could have established from a stem fragment washed around the coast from Denham Bay or Low Flat. However, given that all known stands are some distance from the sea, this explanation is less likely. At the start of the weed eradication programme, shore hibiscus was listed as a category A plant (Devine 1977). In 1980, Sykes noted that the plants at Low Flat and Denham Bay had not increased much and because they were only slightly increasing through vegetative layering should be accorded low priority in the eradication programme. 7.3.2 Ecology Shore hibiscus is a sprawling shrub up to 4 m tall belonging to the mallow family (Malvaceae). Leaves are densely hairy below and velvety to touch, almost circular and c. 10-30 cm diam. Yellow flowers with dark purple centres are c. 30-70 mm long. -
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). -
Conservation
SCIENCE OF ECOLOGY AND ART OF CONSERVATION Protection of native species by applying scientific principles of conservation can save New Zealand’s threatened flora and fauna from extinction. Indeed, safeguarding species diversity and abundance will ensure today’s gene pool contributes to the ability of species’ to adapt in tomorrow’s changing environment. Greater biodiversity thereby enhances opportunities for the future evolution of new species. Ecological degradation began with the arrival of humans (circa 1280 AD), along with their cargo of predators to this archipelago. Many species were lost when Polynesians and Europeans respectively destroyed 32% and 38% of the country’s natural forests. Polynesians caused the extinction of >70 native species and European’s another 12 species. Prolonged hunting and habitat loss precipitated extinction of ~58 bird species*. Introduced predators quickly gained supremacy over smaller avian and insect species. Kiore (Rattus exulans) alone led to the loss of ~23 small bird, bat, reptile and invertebrate species. The worldwide IUCN Red List contains 784 extinct species, of which 27 have been lost in the past 20 years. The Red List’s threatened species includes 45 New Zealand birds, including the North Island kokako, kaka, kiwi, kakapo and mohua. The country’s birds are prone to predation and their numbers in most cases continue to decline (Table 1). This includes extinction of the South Island kokako, last reported to occur in Teal Creek, Mount Aspiring National Park in 1967 (Fig. 1). North Island kokako (Callaeas cinerea wilsoni) with their aquamarine wattle are few, and limited mostly to the Mainland Island Restoration Project, Otamatuna, Te Urewera National Park. -
On the Authenticity of De-Extinct Organisms, and the Genesis Argument Douglas Campbell University of Canterbury, New Zealand
Animal Studies Journal Volume 6 | Number 1 Article 5 2017 On the Authenticity of De-extinct Organisms, and the Genesis Argument Douglas Campbell University of Canterbury, New Zealand Follow this and additional works at: https://ro.uow.edu.au/asj Part of the Art and Design Commons, Australian Studies Commons, Creative Writing Commons, Digital Humanities Commons, Education Commons, Feminist, Gender, and Sexuality Studies Commons, Film and Media Studies Commons, Fine Arts Commons, Philosophy Commons, Social and Behavioral Sciences Commons, and the Theatre and Performance Studies Commons Recommended Citation Campbell, Douglas, On the Authenticity of De-extinct Organisms, and the Genesis Argument, Animal Studies Journal, 6(1), 2017, 61-79. Available at:https://ro.uow.edu.au/asj/vol6/iss1/5 Research Online is the open access institutional repository for the University of Wollongong. For further information contact the UOW Library: [email protected] On the Authenticity of De-extinct Organisms, and the Genesis Argument Abstract Are the methods of synthetic biology capable of recreating authentic living members of an extinct species? An analogy with the restoration of destroyed natural landscapes suggests not. The er stored version of a natural landscape will typically lack much of the aesthetic value of the original landscape because of the different historical processes that created it – processes that involved human intentions and actions, rather than natural forces acting over millennia. By the same token, it would appear that synthetically recreated versions of extinct natural organisms will also be less aesthetically valuable than the originals; that they will be, in some strong sense, ‘inauthentic’, because of their peculiar history and mode of origin. -
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. -
Patterns of Prehistoric Human Mobility in Polynesia Indicated by Mtdna from the Pacific Rat (Rattus Exulans͞population Mobility)
Proc. Natl. Acad. Sci. USA Vol. 95, pp. 15145–15150, December 1998 Anthropology Patterns of prehistoric human mobility in Polynesia indicated by mtDNA from the Pacific rat (Rattus exulansypopulation mobility) E. MATISOO-SMITH*†,R.M.ROBERTS‡,G.J.IRWIN*, J. S. ALLEN*, D. PENNY§, AND D. M. LAMBERT¶ *Department of Anthropology and ‡School of Biological Sciences, University of Auckland, P. B. 92019 Auckland, New Zealand; and §Molecular Genetics Unit and ¶Department of Ecology, Massey University, P. B. 11222 Palmerston North, New Zealand Communicated by R. C. Green, University of Auckland, Auckland, New Zealand, October 14, 1998 (received for review July 20, 1998) ABSTRACT Human settlement of Polynesia was a major Recent genetic research focusing on Polynesian populations event in world prehistory. Despite the vastness of the distances has contributed significantly to our understanding of the covered, research suggests that prehistoric Polynesian popu- ultimate origins of this last major human migration. Studies of lations maintained spheres of continuing interaction for at globin gene variation (2) and mtDNA lineages of modern least some period of time in some regions. A low level of genetic Polynesians (3, 4) and studies of ancient DNA from Lapita- variation in ancestral Polynesian populations, genetic admix- associated skeletons (5) may indicate that some degree of ture (both prehistoric and post-European contact), and severe admixture with populations in Near Oceania occurred as more population crashes resulting from introduction of European remote biological ancestors left Southeast Asia and passed diseases make it difficult to trace prehistoric human mobility through Near Oceania. An alternative hypothesis is that the in the region by using only human genetic and morphological biological ancestors of these groups were one of a number of markers. -
Grounded Birds in New Zealand
Flightless Grounded Birds in New Zealand An 8th Grade Research Paper By Nathaniel Roth Hilltown Cooperative Charter Public School June 2014 1 More than half of the birds in New Zealand either can’t fly, can only partially fly, or don’t like to fly. (Te Ara) This is a fact. Although only sixteen species in New Zealand are technically flightless, with another sixteen that are extinct (TerraNature), a majority of more than 170 bird species will not fly unless their lives are threatened, or not even then. This is surprising, since birds are usually known for flying. A flightless bird is a bird that cannot fly, such as the wellknown ostrich and emu, not to mention penguins. The two main islands southeast of Australia that make up New Zealand have an unusually diverse population of these birds. I am personally very interested in New Zealand and know a lot about it because my mother was born there, and I still have family there. I was very intrigued by these birds in particular, and how different they are from most of the world’s birds. I asked myself, why New Zealand? What made this tiny little country have so many birds that can’t fly, while in the rest of the world, hardly any live in one place? My research has informed me that the population and diversity of flightless birds here is so large because it has been isolated for so long from other land masses. Almost no mammals, and no land predators, lived there in the millions of years after it split from the Australian continent, so flying birds didn’t have as much of an advantage during this time.