SHORT NOTE North Island Kokako (Callaeas Cinerea Wilsoni)

Total Page:16

File Type:pdf, Size:1020Kb

SHORT NOTE North Island Kokako (Callaeas Cinerea Wilsoni) 52 Notornis, 2007, Vol. 54: 52-54 0029-4470 © The Ornithological Society of New Zealand, Inc. SHORT NOTE North Island kokako (Callaeas cinerea wilsoni IHHGRQÀD[ Phormium tenax) nectar on Tiritiri Matangi Island, Hauraki Gulf, New Zealand ROSE THOROGOOD School of Biological Sciences, University of Auckland, Private Bag 92019, Auckland, New Zealand Present address: 11 Westridge Rd, Titirangi, Auckland [email protected] TAMARA HENRY Department of Conservation, Warkworth Area, Auckland Conservancy, Auckland, New Zealand SIMON FORDHAM Supporters of Tiritiri Matangi Inc., Auckland, New Zealand The North Is kokako (Callaeas cinerea wilsoni) is an kokako to Tiritiri Matangi was controversial, because endangered member of the New Zealand endemic the island lacked the large areas of structurally Ĵȱ¢ȱǻCallaeatidae). Typically described complex forest thought to be necessary to sustain a as being omnivorous (e.g., Best & Bellingham 1990; population of kokako (Jones 2000). Powlesland 1987), kokako eat predominantly fruit During routine Department of Conservation ȱ ǰȱ ȱ Ě ǰȱ ǰȱ ȱ ȱ ȱ ȱ ǻǼȱ ȱ ȱ ȱ ȱ Ĵǰȱ important depending on their availability (Innes et and casual ornithological observation, 10 of 14 al. in press) and the time of year (Powlesland 1987). individually colour-banded kokako were observed Despite its being widely distributed across the ȱ ȱ Ě¡ȱ ȱ ȱ ȱ ȱ ȱ ŘŖŖśǯȱ ȱ ȱȱȱĴȱǻ ȱet Birds in general feed on nectar either by destructive al.ȱȱǼǰȱȱȱȱ ȱȱȱĴȱ ȱ ȱ Ě ǰȱ ȱ ¢ȱ ȱ ȱ ȱ ȱ ȱȱȱȱȱȱȱěȱȱ ȱ Ě ȱ ȱ ¢ȱ ȱ ȱ ȱ ȱ introduced mammalian pests and competitors, (Newstrom & Robertson 2005). The 2nd method and habitat clearance (Innes et al. 2006). Several ȱ ȱ ȱ ȱ ȱ ȱ ȱ ȱ Ě ȱ Ĵȱ ȱ ȱ ȱ ȱ ȱ ȱ ȱ to the head of the bird, presumably facilitating ěȬȱǰȱȱŜȱȱ ȱȱȱ pollination. We observed kokako feeding directly Tiritiri Matangi I from Mangatutu (via a breeding ȱĚ¡ȱĚ ȱǻǯȱŗǼǰȱȱ ȱĚ¡ȱȱȃȄȱ programme at Mt Bruce National Wildlife Centre) on their foreheads. To our knowledge, kokako have and Mapara in 1997-98 (Innes & Flux 1999). The not previously been described feeding in this fashion habitat of Tiritiri Matangi I consists of a mosaic of ȱ Ě¡ȱ ȱ ǻ ȱ ǰȱ ǯȱ ǯǼǯȱ replanted and regenerating forest, 10-20 years old. feeding methods appeared to be identical to those The predominant species planted were pohutukawa ȱ¢ȱȱȱȱȱȱĚ¡ǰȱȱ (Metrosideros excelsa), mahoe (¢ȱ Ě), (Prosthemadera novaeseelandiae), bellbird (Anthornis cabbage tree (Cordyline australis), and New Zealand melanura), both honeyeaters (Meliphagidae), and the Ě¡ȱǻPhormium tenax). In addition, there are 4 small stitchbird (hihi: Notiomystis cincta) (Craig & Stewart areas of remnant broadleaf coastal forest, whose 1988). The stitchbird has recently been transferred canopies are dominated by kohekohe (Dysoxylum to its own family (Notiomystidae), which is perhaps spectabile), pohutukawa (Metrosideros excelsa), and most closely related to the Callaeatidae (Driskell et taraire (Beilschmiedia tarairi). The introduction of al. 2007). Before our observations, North Island kokako have been recorded feeding on nectar of rewarewa (Knightia excelsa) and puriri (Vitex lucens), albeit Received 25 March 2006; 30 September 2006 at very low rates such as 1% of the diet of 19 Short note 53 Fig. 1 North Is kokako (Callaeas cinerea wilsoniǼȱȱȱĚ¡ȱ (Phormium tenax) nectar on Tiritiri Matangi Island. Note pollen on forehead of bird. Photo: S. Fordham. individuals in Puketi forest (Powlesland 1987). This most of the Tiritiri Matangi I population feeds on contrasts with our observations where all birds a hitherto unrecognised food type demonstrates were seen commonly either actually feeding, or that this species can inhabit low, shrubby, and ȱ Ě¡ȱ ȱ ǯȱ ȱ Ěȱ ȱ structurally simple habitat. The observations also ȱĚ¡ȱěȱȱȱȱ ȱȱȱȱ highlight the importance of not assuming a species ȱȱ£ȱȱȱĚ ȱȱȱȱȱ habitat requirements are limited to those where a long brush-like tongue to access the nectar while they survive today. making contact with pollen (Craig & Stewart 1988). ȱ ȱ ȱ ȱ ȱ ęȱ ȱ ȱ ȱ ȱ ȱ ȱ ACKNOWLEDGEMENTS tongue of the honeyeaters, the tongue of the kokako These observations were made while under employment does end in a ‘yard broom’-like brush (McCann by DoC (TH), and by the Zoological Society of London 1964), which potential allows kokako to incorporate (RT). John Innes and Doug Armstrong discussed ideas, more nectar in their diet than was previously and Sandra Anderson, Luis Ortiz Catedral, and Kevin thought. Parker provided helpful comments on thes manuscript. We Conservation management of kokako has thank the Department of Conservation and the Supporters of Tiritiri Matangi Island for providing support and tended to focus on their being primarily a species of accommodation while we were on the island. mature, complex forest (Innes & Flux 1999), where ¢ȱȱ¢ȱȱȱĚ¡ǯȱ ǰȱȱ ȱȱĞȱȱ ȱȱȱȱȱ LITERATURE CITED early New Zealanders (C.E. Douglas in Pascoe 1957), Best, H.A.; Bellingham, P.J. 1990. A habitat survey of North Island kokako, in Puketi Forest, Northland. Department and were also observed feeding at forest-scrub edges of Conservation Science & Research series 17. Wellington, (McLean 1912) and in subalpine shrubland (Worthy Department of Conservation. & Holdaway 2002). Although our observations Craig, J.L.; Stewart, A.M. 1988. Reproductive biology of may indicate some behavioural plasticity to novel Phormium tenax: a honeyeater-pollinated species. New environments, they also highlight that the species Zealand journal of botany 26: 453-463. may have inhabited much more varied habitats Driskell, A.; Christidis, L.; Gill, B. J.; Boles, W.E.; Barker, K.; than where they are now found. Currently there are Longmore, N.W. 2007. A new endemic family of New 18 kokako on Tiritiri Matangi I (having increased Zealand passerine birds: adding heat to a biodiversity from the 6 introduced) and interestingly, they hotspot. Australian journal of zoology 55: 73–78 Innes, J.; Flux, I. 1999. North Island kokako recovery plan appear to prefer foraging and nesting in areas of 1999-2009. Wellington, Department of Conservation. replanted and regenerating forest, rather than in ǰȱ ǯDzȱ¡ǰȱ ǯDzȱǰȱǯDzȱǰȱ ǯDzȱĴ ǰȱ ǯǯȱŘŖŖŜǯȱ the mature remnants (Jones 2000). One of the stated Callaeas cinerea Kokako. In: Higgins, P.J.; Peter, research questions of the kokako recovery plan J.M.; Cowling, S.J. (ed.) Handbook of Australian, New (Innes & Flux 1999) is to determine what is ‘good’ Zealand and Antarctic Birds, Vol. 7: Boatbill to starlings. habitat for kokako. Our observations that show that Melbourne, Oxford University Press. 54 Short Note Jones, R. 2000. Behavioural ecology and habitat requirements Powlesland, R.G. 1987. The foods, foraging behaviour and of kokako (Callaeas cinerea wilsoni) on Tiritiri Matangi habitat use of North Island Kokako in Puketi State Island. Unpubl. MSc thesis, University of Auckland, Forest, Northland. New Zealand journal of ecology 10: Auckland, New Zealand. 117-128. McCann, C. 1964. Observations on the tongues of some Worthy, T.H.; Holdaway, R.N. 2002. Lost world of the moa: New Zealand birds. Notornis 11: 36-45 prehistoric life in New Zealand Bloomington, Indian McLean, J.C. 1912. Bush-birds of New Zealand. Emu 11: University Press, and Christchurch, Canterbury 223-236. University Press. Newstrom, L.; Robertson, A. 2005. Progress in understanding pollination systems in New Zealand. New Zealand Keywords North Island kokako; Callaeas cinerea wilsoni; journal of botany 43: 1-59. ȱȱĚ¡DzȱPhormium tenaxDzȱDzȱĚ Dzȱ Pascoe, J. (ed.) 1957. Mr Explorer Douglas. Wellington, Reed. nectar; historical distribution; Tiritiri Matangi Island Notornis, 2007, Vol. 54: 54-55 0029-4470 © The Ornithological Society of New Zealand, Inc. SHORT NOTE Cattle egrets (Bubulcus ibis) and other vagrant birds in Fiji GUY DUTSON ȱ ȱħȱǰȱ ǯǯǯȱ¡ȱŗŞřřŘǰȱǰȱħ Present address: Birds Australia, 60 Leicester St, Carlton, Victoria 3053, Australia [email protected] DICK WATLING ȱȱħǰȱǯǯȱ¡ȱŘŖŚŗǰȱ ȱǰȱǰȱħ ȱ ȱ¢ȱȱȱħȱȱȱ ȱ¡ȱȱȱȬǰȱȱȬěȱ 2002 to Aug 2005 to identify the country’s Important head, neck, and mantle. All 8 were seen again on 26 Bird Areas (IBAs). Most surveys were undertaken Dec 2005 and on at least 6 other intermediate dates in wet forest, focussing on threatened and endemic ǻ¢ǰȱ¢ǰȱ ¢ȱ ǰȱ ȱ ĞȦǰȱ birds. A few small seabird-nesting islands were Digger Jackson, Richard Thomas/Birdquest, and surveyed and other incidental birdwatching was Dick Watling). Many visits were made to the airport concentrated around Suva. Although many new between these dates and the birds were clearly not data were collected on the resident birds, only 2 present, probably in the extensive agricultural new vagrant species were recorded. This suggests ǰȱ ȱ ĴȬǰȱ ȱ ȱ ȱ ȱ ȱ ħȱ ȱ ȱ ¢ȱ Ȭ Nausori. In Oct and Nov 2003, all were in breeding documented (excepting pelagic seabirds which ǰȱȱȱ ȱȱ ȱȬĚȱ were very poorly covered by the BirdLife surveys). Ȭǯȱȱȱȱęȱȱȱħǯȱȱȱ ȱ ȱ ȱ ȱ ȱ ȱ ħȂȱȱ ȱ several records of small groups in New Caledonia, Watling (2001) but not breeding (Barré & Dutson 2000; Barré & ȱ Řśȱ ȱ ŘŖŖřǰȱ ȱ Ěȱ ȱ Şȱ Ĵȱ ȱ Bachy 2003). This species has become a regular non- (Bubulcus ibis) was found on the short grassland of breeding visitor from Australia to New Zealand, ȱ ȱ ȱ ǯȱ ¢ȱ ȱ ęȱ ¢ȱ and to Norfolk and Lord Howe Is (Marchant & their small size, stout build, stout bill with a small Higgins 1990; MacAllan et al. 2004). ȱ ¢ȱ ȱ ȱ ¢ȱ ȱ ħȱ ȱ historical times is the white-faced heron (Ardea Received 27 February 2006; 31 October 2006 novaehollandiaeǼǯȱ ȱ ȱ ħȱ ȱ ŗşşŝȱ ǻȱ.
Recommended publications
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • Plant Charts for Native to the West Booklet
    26 Pohutukawa • Oi exposed coastal ecosystem KEY ♥ Nurse plant ■ Main component ✤ rare ✖ toxic to toddlers coastal sites For restoration, in this habitat: ••• plant liberally •• plant generally • plant sparingly Recommended planting sites Back Boggy Escarp- Sharp Steep Valley Broad Gentle Alluvial Dunes Area ment Ridge Slope Bottom Ridge Slope Flat/Tce Medium trees Beilschmiedia tarairi taraire ✤ ■ •• Corynocarpus laevigatus karaka ✖■ •••• Kunzea ericoides kanuka ♥■ •• ••• ••• ••• ••• ••• ••• Metrosideros excelsa pohutukawa ♥■ ••••• • •• •• Small trees, large shrubs Coprosma lucida shining karamu ♥ ■ •• ••• ••• •• •• Coprosma macrocarpa coastal karamu ♥ ■ •• •• •• •••• Coprosma robusta karamu ♥ ■ •••••• Cordyline australis ti kouka, cabbage tree ♥ ■ • •• •• • •• •••• Dodonaea viscosa akeake ■ •••• Entelea arborescens whau ♥ ■ ••••• Geniostoma rupestre hangehange ♥■ •• • •• •• •• •• •• Leptospermum scoparium manuka ♥■ •• •• • ••• ••• ••• ••• ••• ••• Leucopogon fasciculatus mingimingi • •• ••• ••• • •• •• • Macropiper excelsum kawakawa ♥■ •••• •••• ••• Melicope ternata wharangi ■ •••••• Melicytus ramiflorus mahoe • ••• •• • •• ••• Myoporum laetum ngaio ✖ ■ •••••• Olearia furfuracea akepiro • ••• ••• •• •• Pittosporum crassifolium karo ■ •• •••• ••• Pittosporum ellipticum •• •• Pseudopanax lessonii houpara ■ ecosystem one •••••• Rhopalostylis sapida nikau ■ • •• • •• Sophora fulvida west coast kowhai ✖■ •• •• Shrubs and flax-like plants Coprosma crassifolia stiff-stemmed coprosma ♥■ •• ••••• Coprosma repens taupata ♥ ■ •• •••• ••
    [Show full text]
  • 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: .........................................................................................................................
    [Show full text]
  • Identification De Polyphénols, Évaluation De Leur Activité Antioxydante Et Étude De Leurs Propriétés Biologiques François Muanda Nsemi
    Identification de polyphénols, évaluation de leur activité antioxydante et étude de leurs propriétés biologiques François Muanda Nsemi To cite this version: François Muanda Nsemi. Identification de polyphénols, évaluation de leur activité antioxydante et étude de leurs propriétés biologiques. Biologie végétale. Université Paul Verlaine - Metz, 2010. Français. NNT : 2010METZ011S. tel-01752680 HAL Id: tel-01752680 https://hal.univ-lorraine.fr/tel-01752680 Submitted on 29 Mar 2018 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. AVERTISSEMENT Ce document est le fruit d'un long travail approuvé par le jury de soutenance et mis à disposition de l'ensemble de la communauté universitaire élargie. Il est soumis à la propriété intellectuelle de l'auteur. Ceci implique une obligation de citation et de référencement lors de l’utilisation de ce document. D'autre part, toute contrefaçon, plagiat, reproduction illicite encourt une poursuite pénale. Contact : [email protected] LIENS Code de la Propriété Intellectuelle. articles L 122. 4 Code de
    [Show full text]
  • 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).
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • Agathis Australis
    Mike Marden and Chris Phillips [email protected] KKauriauri Agathis australis INTRODUCTION AND METHODS Reasons for planting native trees include the enhancement of plant and animal biodiversity for conservation, establishment of a native cover on erosion-prone sites, improvement of water quality by revegetation of riparian areas and management for production of high quality timber. Signifi cant areas of the New Zealand landscape, both urban and rural, are being re-vegetated using native species. Many such plantings are on open sites where the aim is to quickly achieve canopy closure and often includes the planting of a mixture of shrubs and tree species concurrently. Previously, data have been presented showing the potential above- and below-ground growth performance of eleven native plant species considered typical early colonisers of bare ground, particularly in riparian areas (http://icm.landcareresearch.co.nz/research/land/Trial1results.asp). In this current series of posters we present data on the growth performance of six native conifer (kauri, rimu, totara, matai, miro, kahikatea) and two broadleaved hardwood (puriri, titoki) species most likely to succeed the early colonising species to become a major component in mature stands of indigenous forest (http://icm.landcareresearch.co.nz/research/land/Trial2.asp). Data on the potential above- and below-ground early growth performance of colonising shrubby species together with that of conifer and broadleaved species will help land managers and community groups involved in re-vegetation projects in deciding the plant spacing and species mix most appropriate for the scale of planting and best suited to site conditions. Data are from a trial established in 2006 to assess the relative growth performance of native conifer and broadleaved hardwood tree species.
    [Show full text]