(Felis Catus) on Raoul Island, Kermadec Group
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Seabirds in Southeastern Hawaiian Waters
WESTERN BIRDS Volume 30, Number 1, 1999 SEABIRDS IN SOUTHEASTERN HAWAIIAN WATERS LARRY B. SPEAR and DAVID G. AINLEY, H. T. Harvey & Associates,P.O. Box 1180, Alviso, California 95002 PETER PYLE, Point Reyes Bird Observatory,4990 Shoreline Highway, Stinson Beach, California 94970 Waters within 200 nautical miles (370 km) of North America and the Hawaiian Archipelago(the exclusiveeconomic zone) are consideredas withinNorth Americanboundaries by birdrecords committees (e.g., Erickson and Terrill 1996). Seabirdswithin 370 km of the southern Hawaiian Islands (hereafterreferred to as Hawaiian waters)were studiedintensively by the PacificOcean BiologicalSurvey Program (POBSP) during 15 monthsin 1964 and 1965 (King 1970). Theseresearchers replicated a tracklineeach month and providedconsiderable information on the seasonaloccurrence and distributionof seabirds in these waters. The data were primarily qualitative,however, because the POBSP surveyswere not basedon a strip of defined width nor were raw counts corrected for bird movement relative to that of the ship(see Analyses). As a result,estimation of density(birds per unit area) was not possible. From 1984 to 1991, using a more rigoroussurvey protocol, we re- surveyedseabirds in the southeasternpart of the region (Figure1). In this paper we providenew informationon the occurrence,distribution, effect of oceanographicfactors, and behaviorof seabirdsin southeasternHawai- ian waters, includingdensity estimatesof abundant species. We also document the occurrenceof six speciesunrecorded or unconfirmed in thesewaters, the ParasiticJaeger (Stercorarius parasiticus), South Polar Skua (Catharacta maccormicki), Tahiti Petrel (Pterodroma rostrata), Herald Petrel (P. heraldica), Stejneger's Petrel (P. Iongirostris), and Pycroft'sPetrel (P. pycrofti). STUDY AREA AND SURVEY PROTOCOL Our studywas a piggybackproject conducted aboard vessels studying the physicaloceanography of the easterntropical Pacific. -
Kermadec White-Faced Storm-Petrel Annual Distribution Lineage
To view this as a map and many more go to: www.nabis.govt.nz web mapping tool Type the map name into: Search for a map layer or place Lineage – Scientific methodology Annual distribution of Kermadec white-faced storm-petrel lineage 1. Literature sources were searched for distribution information. a. Scientific papers, published texts, unpublished reports and university theses available to the expert who prepared the distributional layers. b. Aquatic Sciences and Fisheries Abstracts for 1960-2009. c. OSNZ News and Southern Bird for 1977–2009. 2. Other sources. a. NZSAS (New Zealand Seabirds at Sea) database maintained by Natural Environment, Museum of New Zealand Te Papa Tongarewa, Wellington. Also, a database of daily seabird sightings off Kaikoura (www.oceanwings.co.nz). 3. Summary a. An expert scientist integrated information from the literature and expert opinion, and produced hand-drawn distributional zones on a template map. These maps were then digitised and imported into a GIS software package as layers. The areas of the zones were calculated, and the layers were linked to attribute and metadata files. b. The primary sources of distribution data for Kermadec white-faced storm-petrel were the NZSAS database, published texts and unpublished reports. c. A distribution “hotspot” for New Zealand seabirds is defined as “an area of increased abundance of a species, as considered by the expert compiling the species account”. Typical examples of hotspots include areas around breeding locations during the breeding season, regardless of the absolute size of the breeding colony, and areas that are consistently and repeatedly favoured as feeding locations. -
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. -
The Impact of Predation by Introduced Mammals on Endemic Shorebirds in New Zealand: a Conservation Perspective
Biological Conservation 99 (2001) 47±64 www.elsevier.com/locate/biocon The impact of predation by introduced mammals on endemic shorebirds in New Zealand: a conservation perspective John E. Dowding a,*, Elaine C. Murphy b aPO Box 36-274, Merivale, Christchurch 8030, New Zealand bScience and Research Unit, Department of Conservation, Private Bag 4715, Christchurch, New Zealand Abstract The avifauna of New Zealand has been severely depleted since human colonisation and currently contains a disproportionately high number of threatened species. Of the 23 threatened shorebird species worldwide, six are endemic to New Zealand. We review the status of New Zealand's endemic shorebirds and examine the impact on them of various threats, particularly predation by introduced mammals. The conservation status of the 10 extant species (three oystercatchers, one stilt, four plovers and two snipe) is outlined and the factors that predisposed them to predation by introduced mammals are summarised. Individual species accounts are presented, including data on population trends, known or suspected impacts of predation, identi®cation of important predator species, other threats, and conservation measures currently in place or required. One species and two subspecies are extinct, three species are con®ned to predator-free islands and another is found only on the Chatham Islands group. Six survive on the mainland but three have declined to varying degrees and are assigned threatened status by Collar et al. (1994). Only one plover and two oystercatchers are still relatively numerous and/or widespread. Rats, cats and mustelids have had the greatest overall impacts. Conservation measures in place to mitigate the eects of introduced predators include the formulation of recovery plans, predator control around breeding areas, captive breeding and rearing programmes and the founding of new populations by translocation. -
Great Barrier Island Aotea Brochure
AUCKLAND Further information Great Barrier Aotea / Great Barrier Island Base Private Bag 96002 Island/Aotea Great Barrier Island 0961 Hauraki Gulf Marine Park PHONE: 09 429 0044 EMAIL: [email protected] www.doc.govt.nz Published by: Department of Conservation DOC Aotea / Great Barrier Island Base Private Bag 96002 Great Barrier Island October 2019 Editing and design: DOC Creative Services, Conservation House, Wellington Front cover: Aotea Track. Photo: Andris Apse Back cover: Kākā landing in a pōhutukawa tree. Photo: Leon Berard This publication is produced using paper sourced from well-managed, renewable and legally logged forests. R153740 Contents Aotea and Ngāti Rehua Aotea and Ngāti Rehua .................1 The island renown Ridge to reef ..........................2 The west coast ...........................3 Aotea is the ancestral land of the The east coast ............................3 Ngāti Rehua hapū of Ngāti Wai. It is Marine life ................................4 the southeastern outpost of the tribal rohe of the Ngāti Wai iwi. Seabirds ..................................4 Rich history ..........................5 Although each island, islet and rock has its own individual character and identity, Aotea is Mining ...................................5 viewed as a single physical and spiritual entity Whaling ..................................6 over which a ‘spiritual grid’ lies. At its centre Shipwrecks ...............................6 stands Hirakimata (Mt Hobson), the maunga Historic buildings. 6 tapu of Ngāti Rehua. To the -
Distributions of New Zealand Birds on Real and Virtual Islands
JARED M. DIAMOND 37 Department of Physiology, University of California Medical School, Los Angeles, California 90024, USA DISTRIBUTIONS OF NEW ZEALAND BIRDS ON REAL AND VIRTUAL ISLANDS Summary: This paper considers how habitat geometry affects New Zealand bird distributions on land-bridge islands, oceanic islands, and forest patches. The data base consists of distributions of 60 native land and freshwater bird species on 31 islands. A theoretical section examines how species incidences should vary with factors such as population density, island area, and dispersal ability, in two cases: immigration possible or impossible. New Zealand bird species are divided into water-crossers and non-crossers on the basis of six types of evidence. Overwater colonists of New Zealand from Australia tend to evolve into non-crossers through becoming flightless or else acquiring a fear of flying over water. The number of land-bridge islands occupied per species increases with abundance and is greater for water-crossers than for non-crossers, as expected theoretically. Non-crossers are virtually restricted to large land-bridge islands. The ability to occupy small islands correlates with abundance. Some absences of species from particular islands are due to man- caused extinctions, unfulfilled habitat requirements, or lack of foster hosts. However, many absences have no such explanation and simply represent extinctions that could not be (or have not yet been) reversed by immigrations. Extinctions of native forest species due to forest fragmentation on Banks Peninsula have especially befallen non-crossers, uncommon species, and species with large area requirements. In forest fragments throughout New Zealand the distributions and area requirements of species reflect their population density and dispersal ability. -
Obsidian from Macauley Island: a New Zealand Connection
www.aucklandmuseum.com Obsidian from Macauley Island: a New Zealand connection Louise Furey Auckland War Memorial Museum Callan Ross-Sheppard McGill University, Montreal Kath E. Prickett Auckland War Memorial Museum Abstract An obsidian flake collected from Macauley Island during the Kermadec Expedition has been analysed to determine the source. The result indicates a Mayor Island, New Zealand, origin, supporting previous results on obsidian from Raoul Island that Polynesians travelled back into the Pacific from New Zealand. Keywords obsidian; Pacific colonisation; Pacific voyaging; Macauley Island. INTRODUCTION The steep terrain meant there were only a few suitable habitation places confined to flat areas of limited size on The Kermadec Islands comprise Raoul Island, the largest the south and north coasts. The only landing places were of the group, the nearby Meyer Islands and Herald adjacent to these flats. Botanical surveys have recorded Islets, and 100–155 km to the south are Macauley, the presence of Polynesian tropical cultigens including Curtis and Cheeseman iIslands, and L’Esperence Rock. candlenut (Aleurites monuccana) and ti (Cordyline Raoul is approximately 1000 km to the northeast of fruticosa) (Sykes 1977) which are not endemic to the New Zealand. During the 2011 Kermadec Expedition, island and it is assumed they were transported there by samples of naturally occurring obsidian were obtained Polynesian settlers. Polynesian tuberous vegetables such from Raoul, the Meyer Islands, and from the sea floor off as taro (Colocasia esculenta) and kumara (Ipomoea Curtis Island. These are now in the Auckland Museum batatas) were also recorded but their introduction collection. More importantly however was the single attributed to later 19th century immigrants. -
Re-Establishing North Island Kākā (Nestor Meridionalis Septentrionalis
Copyright is owned by the Author of the thesis. Permission is given for a copy to be downloaded by an individual for the purpose of research and private study only. The thesis may not be reproduced elsewhere without the permission of the Author. Re-establishing North Island kākā (Nestor meridionalis septentrionalis) in New Zealand A thesis presented in fulfilment of the requirements for the degree of Master of Science In Conservation Biology Massey University Auckland, New Zealand Tineke Joustra 2018 ii For Orlando, Aurora and Nayeli “I don’t want my children to follow in my footsteps, I want them to take the path next to me and go further than I could have ever dreamt possible” Anonymous iii iv Abstract Recently there has been a global increase in concern over the unprecedented loss of biodiversity and how the sixth mass extinction event is mainly due to human activities. Countries such as New Zealand have unique ecosystems which led to the evolution of many endemic species. One such New Zealand species is the kākā (Nestor meridionalis). Historically, kākā abundance has been affected by human activities (kākā were an important food source for Māori and Europeans). Today, introduced mammalian predators are one of the main threats to wild kākā populations. Although widespread and common throughout New Zealand until the 1800’s, kākā populations on the mainland now heavily rely on active conservation management. The main methods of kākā management include pest control and re-establishments. This thesis evaluated current and past commitments to New Zealand species restoration, as well as an analysis of global Psittacine re-establishment efforts. -
Hauturu (Little Barrier Island) Quick Fact Sheet
Hauturu (Little Barrier Island) Quick Fact Sheet One of New Zealand's oldest off-shore island sanctuaries (established in 1895) One of New Zealand's largest off-shore island sanctuaries (3083 hectares) Volcanic in origin, with rugged, mountainous terrain, rising to 722 metres above sea-level (Mt Hauturu) Home to a greater number of threatened bird species than any other island in the country Home to New Zealand's most diverse assemblage of reptiles (tuatara; five species of gecko and eight species of skink) Home to over 400 species of native plants, including 34 that are nationally or regionally threatened The only site in the Auckland region for three nationally threatened plants: giant- flowered broom, red mistletoe, and Dactylanthus taylorii. Also the site of the largest natural populations in the region of shore spurge, which is declining nationally Home to the only self-sustaining population of hihi (stitchbird) Home to New Zealand's largest earthworm (up to 1.4 metres) and the wetapunga (Deinacrida heteracantha), which is New Zealand’s heaviest recorded insect (up to 71 grams) One of the few remaining sites where both species of native bat (short- and long- tailed) are present a safe haven for up to 23 kakapo, which was close to 50% of the remaining kakapo from 1982 to 1999, most of them moved up from Stewart Island to protect them from cat predation. Kakapo were removed prior to kiore (rat) eradication in the early-2000s and were re-introduced in 2012 Free of all mammalian predators (cat free since 1981 and rat free since 2006) The only known breeding ground in the world for the critically endangered New Zealand storm petrel, rediscovered in 2003 after 108 years of presumed extinction The world’s largest breeding ground of Cook's petrel, estimated at fewer than 30,000 pairs One of the two breeding grounds of the rare black petrel, estimated at 200 pairs . -
Sykes: the Effect of Goats on Kermadec Islands' Vegetation 13
SYKES: THE EFFECT OF GOATS ON KERMADEC ISLANDS' VEGETATION 13 THE EFFECT OF GOATS ON VEGETATION OF THE KERMADEC ISLANDS W. R. SYKES Botanr Divisiol!. D.S.l.R" Christchurch Goats were present on RaouL the largest island partly responsible for the deyelopment of lhis of the Kermadecs, in 1836, (Rhodes il! Straubel habit. Browsing had also resulted in the introduced 1954) although Wright and Metson (1959) stated sedge Cyperus brevifolius (Rotlb.) Hassk. forming that they were liberated there in 1842. Rhodes said short dense mats lowards the bottom of lhe shallow lhat they were few in number on Raoul whereas he guIJies; this appearance being quite unlike that stated that in 1836. lhe second largest island in the usually found in this species elsewhere. On Raoul group, Macauley, "abounds with goats". This the two lasl-named plants do not form short turf. implies that lhese animals mllst have already been The overall appearance of the plaleau as early as present for a number of years. On Macauley the 1887 must have resembled that seen in 1966 vegetation was burnt to some degree prior to the because Cheeseman (1888) found" . a beau- arrival of the goats. As a result, it has - grassland tiful sward of natural grass". covering most of its surface whereas Raoul is still forested. The above monocotyledonous herbs provided the main source of food for the large goat population, and. apart from limiled areas, dicotyledonous Jn July and August 1966, an expedition herbs were relatively insignificant there during the organised by lhe NZ. Wildlife Service probably winter of 1966. -
Hihi – Stitchbird Facts As We Approach Christmas and the New Year We
Hihi – Stitchbird facts As we approach Christmas and the New Year we also approach the first year anniversary of HANZ. Woo! To celebrate us lasting a year and not just my dad listening but actual real people too, I have decided to do what most podcasts do during this time and do an AMAA or Ask Me Almost Anything or a Q and A episode if you like. So, to do that, I need questions that you would like answered! They can be about pretty much anything you want, stuff about the podcast, how I make it, the research, what I wear while recording, I don’t know! But you can also ask anything about me, who I am, my biases and just generally get to know me better if you want! There are a few restrictions though, as you might expect. I won’t answer anything too personal or that might tell you more about where I live and work. All I will say on those fronts is that I live in Wellington and I work in conservation, so don’t bother asking anything deeper. Don’t worry too much about that though, I’ll filter questions that I deem out of scope, so fire away anything you want to know through to me via Twitter, Facebook, Email and all the usual places! I’ll probably need quite a few so really go nuts! Kia ora, gday and welcome to the History of Aotearoa New Zealand. Episode 26: My Birb of the Year. I know I said that we would be talking about Māui this time but he will have to wait for next time cause I decided to do something a bit different. -
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.