Third South Pacific Natiohal Parks & Reserves Conference
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Setting Priorities for Marine Conservation in the Fiji Islands Marine Ecoregion Contents
Setting Priorities for Marine Conservation in the Fiji Islands Marine Ecoregion Contents Acknowledgements 1 Minister of Fisheries Opening Speech 2 Acronyms and Abbreviations 4 Executive Summary 5 1.0 Introduction 7 2.0 Background 9 2.1 The Fiji Islands Marine Ecoregion 9 2.2 The biological diversity of the Fiji Islands Marine Ecoregion 11 3.0 Objectives of the FIME Biodiversity Visioning Workshop 13 3.1 Overall biodiversity conservation goals 13 3.2 Specifi c goals of the FIME biodiversity visioning workshop 13 4.0 Methodology 14 4.1 Setting taxonomic priorities 14 4.2 Setting overall biodiversity priorities 14 4.3 Understanding the Conservation Context 16 4.4 Drafting a Conservation Vision 16 5.0 Results 17 5.1 Taxonomic Priorities 17 5.1.1 Coastal terrestrial vegetation and small offshore islands 17 5.1.2 Coral reefs and associated fauna 24 5.1.3 Coral reef fi sh 28 5.1.4 Inshore ecosystems 36 5.1.5 Open ocean and pelagic ecosystems 38 5.1.6 Species of special concern 40 5.1.7 Community knowledge about habitats and species 41 5.2 Priority Conservation Areas 47 5.3 Agreeing a vision statement for FIME 57 6.0 Conclusions and recommendations 58 6.1 Information gaps to assessing marine biodiversity 58 6.2 Collective recommendations of the workshop participants 59 6.3 Towards an Ecoregional Action Plan 60 7.0 References 62 8.0 Appendices 67 Annex 1: List of participants 67 Annex 2: Preliminary list of marine species found in Fiji. 71 Annex 3 : Workshop Photos 74 List of Figures: Figure 1 The Ecoregion Conservation Proccess 8 Figure 2 Approximate -
Special Issue3.7 MB
Volume Eleven Conservation Science 2016 Western Australia Review and synthesis of knowledge of insular ecology, with emphasis on the islands of Western Australia IAN ABBOTT and ALLAN WILLS i TABLE OF CONTENTS Page ABSTRACT 1 INTRODUCTION 2 METHODS 17 Data sources 17 Personal knowledge 17 Assumptions 17 Nomenclatural conventions 17 PRELIMINARY 18 Concepts and definitions 18 Island nomenclature 18 Scope 20 INSULAR FEATURES AND THE ISLAND SYNDROME 20 Physical description 20 Biological description 23 Reduced species richness 23 Occurrence of endemic species or subspecies 23 Occurrence of unique ecosystems 27 Species characteristic of WA islands 27 Hyperabundance 30 Habitat changes 31 Behavioural changes 32 Morphological changes 33 Changes in niches 35 Genetic changes 35 CONCEPTUAL FRAMEWORK 36 Degree of exposure to wave action and salt spray 36 Normal exposure 36 Extreme exposure and tidal surge 40 Substrate 41 Topographic variation 42 Maximum elevation 43 Climate 44 Number and extent of vegetation and other types of habitat present 45 Degree of isolation from the nearest source area 49 History: Time since separation (or formation) 52 Planar area 54 Presence of breeding seals, seabirds, and turtles 59 Presence of Indigenous people 60 Activities of Europeans 63 Sampling completeness and comparability 81 Ecological interactions 83 Coups de foudres 94 LINKAGES BETWEEN THE 15 FACTORS 94 ii THE TRANSITION FROM MAINLAND TO ISLAND: KNOWNS; KNOWN UNKNOWNS; AND UNKNOWN UNKNOWNS 96 SPECIES TURNOVER 99 Landbird species 100 Seabird species 108 Waterbird -
Great Australian Bight BP Oil Drilling Project
Submission to Senate Inquiry: Great Australian Bight BP Oil Drilling Project: Potential Impacts on Matters of National Environmental Significance within Modelled Oil Spill Impact Areas (Summer and Winter 2A Model Scenarios) Prepared by Dr David Ellis (BSc Hons PhD; Ecologist, Environmental Consultant and Founder at Stepping Stones Ecological Services) March 27, 2016 Table of Contents Table of Contents ..................................................................................................... 2 Executive Summary ................................................................................................ 4 Summer Oil Spill Scenario Key Findings ................................................................. 5 Winter Oil Spill Scenario Key Findings ................................................................... 7 Threatened Species Conservation Status Summary ........................................... 8 International Migratory Bird Agreements ............................................................. 8 Introduction ............................................................................................................ 11 Methods .................................................................................................................... 12 Protected Matters Search Tool Database Search and Criteria for Oil-Spill Model Selection ............................................................................................................. 12 Criteria for Inclusion/Exclusion of Threatened, Migratory and Marine -
Chapter 1 Pre-Settlement
¢¢CHAPTER 1 PRE-SETTLEMENT The Aborigines1 are believed to have been on the South Coast of New South Wales for at least 20,000 years, judging from dating of carbon found in a cave near Burrill Lake. It is hard to get such a number of years into perspective. A thousand generations? A hundred times the duration of white settlement? We are not used to such scales of time. It is short as geologists measure time, but it is long enough to include the peak of the most recent ice age, when sea levels were lower by up to 100 metres. The shore would have been further east, and Brush Island not an island at all, for much of this time. Few legacies of the Aborigines remain.2 Murramarang headland has a large midden which was found by anthropologists from the Australian Museum in the 1920s, and from which many artefacts were collected. At that time, the midden area was bare, with shifting sand dunes that would cover or expose parts of it, so on each visit you could expect to see something new. The present vegetation is recent, and the result of deliberate efforts to ‘stabilise’ the dunes.3 1 Today, the term Aborigine is rarely used, having been replaced by ‘Aboriginal people’ or ‘Indigenous people/communities’ (A.G. and S.F.). 2 Many legacies of traditional Aboriginal use and occupation of the area still remain. The area has numerous recorded archaeological sites, and one of the best known is the large midden on Murramarang headland (see previous section). -
S P E N C E R G U L F S T G U L F V I N C E N T Adelaide
Yatala Harbour Paratoo Hill Turkey 1640 Sunset Hill Pekina Hill Mt Grainger Nackara Hill 1296 Katunga Booleroo "Avonlea" 2297 Depot Hill Creek 2133 Wilcherry Hill 975 Roopena 1844 Grampus Hill Anabama East Hut 1001 Dawson 1182 660 Mt Remarkable SOUTH Mount 2169 440 660 (salt) Mt Robert Grainger Scobie Hill "Mazar" vermin 3160 2264 "Manunda" Wirrigenda Hill Weednanna Hill Mt Whyalla Melrose Black Rock Goldfield 827 "Buckleboo" 893 729 Mambray Creek 2133 "Wyoming" salt (2658±) RANGE Pekina Wheal Bassett Mine 1001 765 Station Hill Creek Manunda 1073 proof 1477 Cooyerdoo Hill Maurice Hill 2566 Morowie Hill Nackara (abandoned) "Bulyninnie" "Oak Park" "Kimberley" "Wilcherry" LAKE "Budgeree" fence GILLES Booleroo Oratan Rock 417 Yeltanna Hill Centre Oodla "Hill Grange" Plain 1431 "Gilles Downs" Wirra Hillgrange 1073 B pipeline "Wattle Grove" O Tcharkuldu Hill T Fullerville "Tiverton 942 E HWY Outstation" N Backy Pt "Old Manunda" 276 E pumping station L substation Tregalana Baroota Yatina L Fitzgerald Bay A Middleback Murray Town 2097 water Ucolta "Pitcairn" E Buckleboo 1306 G 315 water AN Wild Dog Hill salt Tarcowie R Iron Peak "Terrananya" Cunyarie Moseley Nobs "Middleback" 1900 works (1900±) 1234 "Lilydale" H False Bay substation Yaninee I Stoney Hill O L PETERBOROUGH "Blue Hills" LC L HWY Point Lowly PEKINA A 378 S Iron Prince Mine Black Pt Lancelot RANGE (2294±) 1228 PU 499 Corrobinnie Hill 965 Iron Baron "Oakvale" Wudinna Hill 689 Cortlinye "Kimboo" Iron Baron Waite Hill "Loch Lilly" 857 "Pualco" pipeline Mt Nadjuri 499 Pinbong 1244 Iron -
15.2 Sand Islands and Shoals
15 Islands 15.2 Sand Islands and Shoals Figure 15.1: (A) Aerial view of Troubridge Island and surrounding Troubridge Shoals: (c) Coastal Protection Branch, DEWNR. (B). Troubridge Island: (c) W. Bonham, Lighthouses of Australia. Asset Sand Islands and Shoals Description A crest of sand which rises above water level from a broad marine sand bank, forming an unstable sand island - Troubridge Island - which changes shape and size over time. The island is about 5m high at high tide, and about 2 hectares in area when inundated, but considerable larger at low tide. The island is surrounded by shallow sand embankments (Troubridge Shoals). Examples of Key Little Penguin, Black-faced Cormorant, Crested Tern and other breeding sea Species birds (numerous species) migratory wading birds (numerous species) abundant sand-dwelling invertebrates - food sources for fish and wading birds Pink Snapper King George whiting and school whiting syngnathid fishes (e.g. seahorses, pipefishes) sponges (forming “sponge gardens”, on consolidated sand) cowries; volutes and other specimen shells Knobby Argonaut (‘paper nautilus’ octopus) giant spider crab southern calamari Main Location Troubridge Island (and shallow sandbanks to the west - Troubridge Shoals) Notes Troubridge Island Conservation Park (approx. 260 hectares) was declared in 1982, and extended in 1986, partly to protect major breeding colonies of several seabird species, and provide protection for an important feeding ground used by migratory wading birds, listed under international treaties. Oceanography At the bottom of Gulf St Vincent, off the eastern “heel” of Yorke Peninsula, waters less than 20m occur up to 10km from shore. The oceanographic conditions have led to a long-term build-up of sand in some areas, including the creation of Troubridge Island, a sand island about 7km east of Sultana Point. -
Proceedings of the Linnean Society of New South Wales, 1961, Vol
{Issued 1st Sejitenibe?; 1961.) Vol. LXXXVI. No. 395. Part 1. THE PROCEEDINGS LiriNEAN Society New South Wales FOR THE YEAR 1961 vVOOiJS HOLE, MASS. I Part 1 (pp. 1-168). CONTAIIVING THK PROCEEDINGS OP THE ANNUAL, MEETING AND PAPERS READ IN MARCH-APRIL. With seven plates. [Plates i-vii.] Sydney printed and ptjblished fok the society by AUSTRALASIAN MEDICAL PUBLISHING CO. LTD., Seamer and Arundel Streets, Glebe, Sydney, and SOLD BY THE SOCIETY, Science House, 157 Gloucester Street, Sydney. Registered at the General Post Office, Sydney, for transmission by post as a periodical. Agejit in Europe: David Nutt, 41 Colebrooke Row, London, N.i. ac=» osna 280 THE GENUS PELARGONIUM L'HER. EX AIT. IN AUSTRALIA. By R. C. Carolin, University of Sydney. (Four Text-figures.) [Read 29th November, 1961.] Synopsis. Seven indigenous species of Pelargonmm are distinguished and described, P. helmsii for the first time. P. littorale Hiigel and P. drummondii Turcz. are reinstated. Introduced species are also considered. Some problems raised by the distributions of the various species are discussed. Introduction. The genus Pelargonium lias attracted considerable attention due to the horticultural value of many of the species. It is not surprising, then, to find the most showy of the species occurring on the eastern seaboard of Australia being cultivated in Europe at quite an early date. P. australe was described by Willdenow in 1800 and it appears that it was widely cultivated even then. P. inodoriim was described by the same worker a little later and, subsequently, the name was misapplied to a number of Table l. -
Issues Paper for the Grey Nurse Shark (Carcharias Taurus)
Issues Paper for the Grey Nurse Shark (Carcharias taurus) 2014 The recovery plan linked to this issues paper is obtainable from: http://www.environment.gov.au/resource/recovery-plan-grey-nurse-shark-carcharias-taurus © Commonwealth of Australia 2014 This work is copyright. You may download, display, print and reproduce this material in unaltered form only (retaining this notice) for your personal, non-commercial use or use within your organisation. Apart from any use as permitted under the Copyright Act 1968, all other rights are reserved. Requests and enquiries concerning reproduction and rights should be addressed to Department of the Environment, Public Affairs, GPO Box 787 Canberra ACT 2601 or email [email protected]. Disclaimer While reasonable efforts have been made to ensure that the contents of this publication are factually correct, the Commonwealth does not accept responsibility for the accuracy or completeness of the contents, and shall not be liable for any loss or damage that may be occasioned directly or indirectly through the use of, or reliance on, the contents of this publication. Cover images by Justin Gilligan Photography Contents List of figures ii List of tables ii Abbreviations ii 1 Summary 1 2 Introduction 2 2.1 Purpose 2 2.2 Objectives 2 2.3 Scope 3 2.4 Sources of information 3 2.5 Recovery planning process 3 3 Biology and ecology 4 3.1 Species description 4 3.2 Life history 4 3.3 Diet 5 3.4 Distribution 5 3.5 Aggregation sites 8 3.6 Localised movements at aggregation sites 10 3.7 Migratory movements -
Filling the Gaps: Identifying Candidate Sites to Expand Fiji's National Protected Area Network
Filling the gaps: identifying candidate sites to expand Fiji's national protected area network Outcomes report from provincial planning meeting, 20-21 September 2010 Stacy Jupiter1, Kasaqa Tora2, Morena Mills3, Rebecca Weeks1,3, Vanessa Adams3, Ingrid Qauqau1, Alumeci Nakeke4, Thomas Tui4, Yashika Nand1, Naushad Yakub1 1 Wildlife Conservation Society Fiji Country Program 2 National Trust of Fiji 3 ARC Centre of Excellence for Coral Reef Studies, James Cook University 4 SeaWeb Asia-Pacific Program This work was supported by an Early Action Grant to the national Protected Area Committee from UNDP‐GEF and a grant to the Wildlife Conservation Society from the John D. and Catherine T. MacArthur Foundation (#10‐94985‐000‐GSS) © 2011 Wildlife Conservation Society This document to be cited as: Jupiter S, Tora K, Mills M, Weeks R, Adams V, Qauqau I, Nakeke A, Tui T, Nand Y, Yakub N (2011) Filling the gaps: identifying candidate sites to expand Fiji's national protected area network. Outcomes report from provincial planning meeting, 20‐21 September 2010. Wildlife Conservation Society, Suva, Fiji, 65 pp. Executive Summary The Fiji national Protected Area Committee (PAC) was established in 2008 under section 8(2) of Fiji's Environment Management Act 2005 in order to advance Fiji's commitments under the Convention on Biological Diversity (CBD)'s Programme of Work on Protected Areas (PoWPA). To date, the PAC has: established national targets for conservation and management; collated existing and new data on species and habitats; identified current protected area boundaries; and determined how much of Fiji's biodiversity is currently protected through terrestrial and marine gap analyses. -
Montague Island Seabird Habitat Restoration Project
Montague Island Seabird Habitat Restoration Project Proceedings of Shared Island Management Workshop Narooma, NSW, November 2008 Department of Environment, Climate Change and Water NSW Cover photos clockwise from left: www.geoffcomfort.com; S. Cohen, DECCW; S. Donaldson; DECCW. Inset bird: DECCW Published by: Department of Environment and Climate Change NSW 59–61 Goulburn Street, Sydney PO Box A290, Sydney South 1232 Phone: (02) 9995 5000 (switchboard) Phone: 131 555 (environment information and publications requests) Phone: 1300 361 967 (national parks information and publications requests) Fax: (02) 9995 5999 TTY: (02) 9211 4723 Email: [email protected] Website: www.environment.nsw.gov.au ISBN 978 1 74232 337 4 DECCW 2009/443 November 2009 Printed on environmentally sustainable stock B Contents Preface ..........................................................................................................................................................................................................................................................................................................................................................................................1 1. Introduction ........................................................................................................................................................................................................................................................................................................................................3 1.1 Overview -
LONGEVITY of the CRESTED TERN Sterna Bergiiln SOUTH AUSTRALIA
Corella,2008, 32(2): 35-37 LONGEVITYOF THE CRESTEDTERN Sterna bergiilN SOUTHAUSTRALIA M. WATERMAN'andM. D. MURRAY'3 r"DebmarPark", 28 GordonAvenue, St. Agnes, South Australia 5097 '17 AshmoreAvenue. Pvmble. New SouthWales 2073 'Correspondingauthor Received:25 January2007 Recoveriesof aliveand deadCrested Terns Stema bergii, banded as chicksat the colonieson Stonywell,Hallway, Troubridgeand Penguinlslands in SouthAustralia, have shown that birdscan surviveas longas 32 years.Although mostbirds were breeding between ,&-18 years old, several breeding birds ol 19-29years were also captured. INTRODUCTION Watermane, al. (2003)described two typesof dispersalof Crested Tem Stema bergii chicks from their natal islands in SouthAustmlia. Recoveriesfrom the southemcolonies were mainly eastwardsaround southeasternAustralia to as far nofh as southemQueensland, whereas those from coloniesaround the Gulf St.Vincent and Spencer Gulf weremostly within these gulf regions.Chicks were bandedregularly at two localities: Stonywell Island and Halfway Island in the south of the Coorong from 1962-1983, and Troubridge Island at the southem end of the Yorke Peninsulafrom 1966-1975 afi 1985-2003.These colonies were also searchedfor banded breedingadults, and the dataobtained ftom the retapped birds, together with those from other recoveries of birds banded as chicks,from theseand other colonies,have given information on the longevity of Crcsted Terns. METHOD Birds were bandedwith aluminium bandssupplied by the Australian Bird and Bat Banding Scheme.Banded breeding adults were capturedwith a hand-netwhen sitting on eggs dudng late incubationor on youngchicks beforc they disperced aroundthe colony. At Stonywell and Halfway Islands searchesfor bandedadults were madein 17 of the 22 years.Howevel intensivesearches were not attemptedbecause the islands were visited when it was best for banding chicks, and brceding birds were not accustomed to the presenceof humans.At Troubddge Island searches Figure 1. -
DISPERSAL of CRESTED TERNS Sterna Bergii from COLONIES in SOUTH AUSTRALIA
Corella, 2003, 27(4): 93-101 DISPERSAL OF CRESTED TERNS Sterna bergiiFROM COLONIES IN SOUTH AUSTRALIA 1 2 4 3 M. WATERMAN , M. D. MURRAY · and D. CONNELL ''Dcbmar Park', Gordon Avenue, St. Agnes, South Australia 5097 '17 Ashmore Avenue, Pymble. New South Wales 2073 'PO Box 73. Kalangadoo, South Australia 5278 'Corresponding author Received: 30 J1111e 2001 The general dispersal of Crested Terns Sterna bergii, banded as chicks at breeding colonies in South Australia between 1955 and 1995 is described. There was a considerable movement of breeding birds between nearby colonies, and even movement between more distant colonies. Most recoveries (78%) were immature one-year and two-year birds, and both immature and mature birds dispersed similarly. There were two patterns of dispersal. Recoveries from birds which were banded at colonies in the Spencer Gulf and the Gulf St. Vincent, were mostly local within these gulfs of South Australia. Those from the other colonies were eastwards along the Victorian coast and then northwards along the eastern coast of south-eastern Australia to southern Queensland. Such long-distance movements, over 2 000 kilometres, were accomplished within three to four months of banding. The numbers recovered in various zones along the coast indicated that they were not solely a consequence of searching effort by people, but the result of a variety of ecological factors affecting mortality along a 3 500 kilometre coastline. INTRODUCTION reference points. From Penguin Island eastwards the reference points were Cape Nelson. Cape Otway, Wilson's Promontory. Cape Howe. One of the early projects of the Australian Bird Banding Jervis Bay.