Southwest Australia Ecoregion
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Conservation Advice
THREATENED SPECIES SCIENTIFIC COMMITTEE Established under the Environment Protection and Biodiversity Conservation Act 1999 The Minister approved this conservation advice and transferred this species from the Endangered category to the Vulnerable category, effective from 04/07/2019 Conservation Advice Spicospina flammocaerulea Sunset Frog Summary of assessment Conservation status Spicospina flammocaerulea has been found to be eligible for transferring from the Endangered category to the Vulnerable category, as outlined in the attached assessment. Reason for conservation assessment by the Threatened Species Scientific Committee This advice follows assessment of information provided by Western Australia as part of the Common Assessment Method process, to systematically review species that are inconsistently listed under the EPBC Act and relevant state/territory legislation or lists. More information on the Common Assessment Method is available at: http://www.environment.gov.au/biodiversity/threatened/cam The information in this assessment has been compiled by the relevant state/territory government. In adopting this assessment under the EPBC Act, this document forms the Approved Conservation Advice for this species as required under s266B of the EPBC Act. Public consultation Notice of the proposed amendment and a consultation document was made available for public comment for at least 30 business days between 14 August 2018 and 25 September 2018. Any comments received that were relevant to the survival of the species were considered by the Committee as part of the assessment process. Recovery plan A recovery plan for this species under the EPBC Act is not recommended, because the Approved Conservation Advice provides sufficient direction to implement priority actions and mitigate against key threats. -
Their Botany, Essential Oils and Uses 6.86 MB
MELALEUCAS THEIR BOTANY, ESSENTIAL OILS AND USES Joseph J. Brophy, Lyndley A. Craven and John C. Doran MELALEUCAS THEIR BOTANY, ESSENTIAL OILS AND USES Joseph J. Brophy School of Chemistry, University of New South Wales Lyndley A. Craven Australian National Herbarium, CSIRO Plant Industry John C. Doran Australian Tree Seed Centre, CSIRO Plant Industry 2013 The Australian Centre for International Agricultural Research (ACIAR) was established in June 1982 by an Act of the Australian Parliament. ACIAR operates as part of Australia's international development cooperation program, with a mission to achieve more productive and sustainable agricultural systems, for the benefit of developing countries and Australia. It commissions collaborative research between Australian and developing-country researchers in areas where Australia has special research competence. It also administers Australia's contribution to the International Agricultural Research Centres. Where trade names are used this constitutes neither endorsement of nor discrimination against any product by ACIAR. ACIAR MONOGRAPH SERIES This series contains the results of original research supported by ACIAR, or material deemed relevant to ACIAR’s research and development objectives. The series is distributed internationally, with an emphasis on developing countries. © Australian Centre for International Agricultural Research (ACIAR) 2013 This work is copyright. Apart from any use as permitted under the Copyright Act 1968, no part may be reproduced by any process without prior written permission from ACIAR, GPO Box 1571, Canberra ACT 2601, Australia, [email protected] Brophy J.J., Craven L.A. and Doran J.C. 2013. Melaleucas: their botany, essential oils and uses. ACIAR Monograph No. 156. Australian Centre for International Agricultural Research: Canberra. -
Verticordia Staminosa Subsp
INTERIM RECOVERY PLAN NO. 90 WONGAN FEATHERFLOWER (VERTICORDIA STAMINOSA SUBSP. STAMINOSA) INTERIM RECOVERY PLAN 2001-2004 Rebecca Evans & Andrew Brown Photograph: B. Wells May 2001 Department of Conservation and Land Management Western Australian Threatened Species and Communities Unit (WATSCU) PO Box 51, Wanneroo, WA 6946 Interim Recovery Plan for Verticordia staminosa subsp. staminosa FOREWORD Interim Recovery Plans (IRPs) are developed within the framework laid down in Department of Conservation and Land Management (CALM) Policy Statements Nos. 44 and 50. IRPs outline the recovery actions that are required to urgently address those threatening processes most affecting the ongoing survival of threatened taxa or ecological communities, and begin the recovery process. CALM is committed to ensuring that Critically Endangered taxa are conserved through the preparation and implementation of Recovery Plans or Interim Recovery Plans and by ensuring that conservation action commences as soon as possible and always within one year of endorsement of that rank by the Minister. This Interim Recovery Plan will operate from May 2001 to April 2004 but will remain in force until withdrawn or replaced. It is intended that, if the taxon is still ranked Critically Endangered, this IRP will be replaced by a full Recovery Plan after three years. This IRP was approved by the Director of Nature Conservation on 27 June 2001. The provision of funds identified in this Interim Recovery Plan is dependent on budgetary and other constraints affecting CALM, as well as the need to address other priorities. Information in this IRP was accurate at May 2001. 2 Interim Recovery Plan for Verticordia staminosa subsp. -
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 -
Water Balance of Field-Excavated Aestivating Australian Desert Frogs
3309 The Journal of Experimental Biology 209, 3309-3321 Published by The Company of Biologists 2006 doi:10.1242/jeb.02393 Water balance of field-excavated aestivating Australian desert frogs, the cocoon- forming Neobatrachus aquilonius and the non-cocooning Notaden nichollsi (Amphibia: Myobatrachidae) Victoria A. Cartledge1,*, Philip C. Withers1, Kellie A. McMaster1, Graham G. Thompson2 and S. Don Bradshaw1 1Zoology, School of Animal Biology, MO92, University of Western Australia, Crawley, Western Australia 6009, Australia and 2Centre for Ecosystem Management, Edith Cowan University, 100 Joondalup Drive, Joondalup, Western Australia 6027, Australia *Author for correspondence (e-mail: [email protected]) Accepted 19 June 2006 Summary Burrowed aestivating frogs of the cocoon-forming approaching that of the plasma. By contrast, non-cocooned species Neobatrachus aquilonius and the non-cocooning N. aquilonius from the dune swale were fully hydrated, species Notaden nichollsi were excavated in the Gibson although soil moisture levels were not as high as calculated Desert of central Australia. Their hydration state (osmotic to be necessary to maintain water balance. Both pressure of the plasma and urine) was compared to the species had similar plasma arginine vasotocin (AVT) moisture content and water potential of the surrounding concentrations ranging from 9.4 to 164·pg·ml–1, except for soil. The non-cocooning N. nichollsi was consistently found one cocooned N. aquilonius with a higher concentration of in sand dunes. While this sand had favourable water 394·pg·ml–1. For both species, AVT showed no relationship potential properties for buried frogs, the considerable with plasma osmolality over the lower range of plasma spatial and temporal variation in sand moisture meant osmolalities but was appreciably increased at the highest that frogs were not always in positive water balance with osmolality recorded. -
Australia's Biodiversity and Climate Change
Australia’s Biodiversity and Climate Change A strategic assessment of the vulnerability of Australia’s biodiversity to climate change A report to the Natural Resource Management Ministerial Council commissioned by the Australian Government. Prepared by the Biodiversity and Climate Change Expert Advisory Group: Will Steffen, Andrew A Burbidge, Lesley Hughes, Roger Kitching, David Lindenmayer, Warren Musgrave, Mark Stafford Smith and Patricia A Werner © Commonwealth of Australia 2009 ISBN 978-1-921298-67-7 Published in pre-publication form as a non-printable PDF at www.climatechange.gov.au by the Department of Climate Change. It will be published in hard copy by CSIRO publishing. For more information please email [email protected] This work is copyright. Apart from any use as permitted under the Copyright Act 1968, no part may be reproduced by any process without prior written permission from the Commonwealth. Requests and inquiries concerning reproduction and rights should be addressed to the: Commonwealth Copyright Administration Attorney-General's Department 3-5 National Circuit BARTON ACT 2600 Email: [email protected] Or online at: http://www.ag.gov.au Disclaimer The views and opinions expressed in this publication are those of the authors and do not necessarily reflect those of the Australian Government or the Minister for Climate Change and Water and the Minister for the Environment, Heritage and the Arts. Citation The book should be cited as: Steffen W, Burbidge AA, Hughes L, Kitching R, Lindenmayer D, Musgrave W, Stafford Smith M and Werner PA (2009) Australia’s biodiversity and climate change: a strategic assessment of the vulnerability of Australia’s biodiversity to climate change. -
Shifts in Symbiotic Associations in Plants Capable of Forming Multiple Root Symbioses Across a Long-Term Soil Chronosequence Felipe E
Shifts in symbiotic associations in plants capable of forming multiple root symbioses across a long-term soil chronosequence Felipe E. Albornoz1, Hans Lambers1, Benjamin L. Turner1,2, Francßois P. Teste1,3 & Etienne Laliberte1,4 1School of Plant Biology, The University of Western Australia, 35 Stirling Highway, Crawley (Perth), WA 6009, Australia 2Smithsonian Tropical Research Institute, Apartado 0843-03092, Balboa, Ancon, Republic of Panama 3Grupo de Estudios Ambientales, IMASL-CONICET & Universidad Nacional de San Luis, Av. Ejercito de los Andes 950 (5700), San Luis, Argentina 4Departement de Sciences biologiques, Institut de Recherche en Biologie Veg etale, Universite de Montreal, 4101 Sherbrooke Est, Montreal, QC H1X 2B2, Canada Keywords Abstract Arbuscular mycorrhizal fungi, chronosequence, ectomycorrhizal fungi, Changes in soil nutrient availability during long-term ecosystem development nitrogen fixation, pedogenesis, phosphorus, influence the relative abundances of plant species with different nutrient-acqui- rhizobia. sition strategies. These changes in strategies are observed at the community level, but whether they also occur within individual species remains unknown. Correspondence Plant species forming multiple root symbioses with arbuscular mycorrhizal Felipe E. Albornoz, School of Plant Biology, (AM) fungi, ectomycorrhizal (ECM) fungi, and nitrogen-(N) fixing microor- The University of Western Australia, 35 ganisms provide valuable model systems to examine edaphic controls on sym- Stirling Highway, Crawley (Perth), WA 6009, Australia. bioses related to nutrient acquisition, while simultaneously controlling for plant Tel: +61 8 6488 5912; host identity. We grew two co-occurring species, Acacia rostellifera (N2-fixing Fax: +61 8 6488 1108; and dual AM and ECM symbioses) and Melaleuca systena (AM and ECM dual E-mail: [email protected]. -
ASH Newsletter 45.Pub
THE AUSTRALIAN SOCIETY OF HERPETOLOGISTS INCORPORATED NEWSLETTER 45 2 3 History of Office Bearers Formation Committee (April 1964):- MJ Littlejohn (Convenor); State Reps IR Straughan (Qld), FJ Mitchell (SA), HG Cogger (NSW), G Storr (WA), RE Barwick (ACT), JW Warren (Vic), AK Lee (Editor). First AGM (23 August 1965):- President MJ Littlejohn, Vice-President NG Stephenson, Secretary-Treasurer AA Martin, Asst Secretary-Treasurer KJ Wilson, Ordinary Members FJ Mitchell and IR Straughan, Editor AK Lee. PRESIDENT:- MJ Littlejohn (1965-69); AK Lee (1969-70); HG Cogger (1971-73); J de Bavay (1974); H Heat- wole (1975-76); GC Grigg (1976-77); MJ Tyler (1978-79); GF Watson (1979-81); AA Martin (1981-82); RS Seymour (1982-83); R Shine (1983-84); GC Grigg (1984-86); J Coventry (1986-87); RE Barwick (1987-88); J Covacevich (1988-91); M Davies (1991-92); R Shine (1992-94); A Georges (1994-6); D Roberts (1996-98); M Bull (1998-9); R Swain (1999-2001); S Downes (2001-03); J Melville (2004-2005); J-M Hero (2005-2007); P Doherty (2007-2008); M Thompson (2008-2009); M Hutchinson (2009-) VICE-PRESIDENT:- NG Stephenson (1965-67); RE Barwick (1967-69); HG Cogger (1969-70); MJ Littlejohn (1971-72); MJ Tyler (1973); HG Cogger (1974); J de Bavay (1975-76); H Heatwole (1976-77); GC Grigg (1977 -79); MJ Tyler (1979-80); GF Watson (1981-82); AA Martin (1982-83); RS Seymour (1983-84); R Shine (1984- 86); GC Grigg (1986-87); J Coventry (1987-88); RE Barwick (1988-91); J Covacevich (1991-92); M Davies (1992-94); R Shine (1994-6); A Georges (1996-98); D Roberts (1998-99); M Bull(1999-2001); R Swain (2001- 2003); S Downes (2004-5); J Melville (2005-2007); J-M Hero (2007-2008); P Doherty (2008-2009); M Thomp- son (2009-) SECRETARY/TREASURER:- AA Martin (1965-67); GF Watson (1967-72); LA Moffatt (1973-75); J Caughley (1975-76); RWG Jenkins (1976-77); M Davies (1978-83); G Courtice (1983-87); J Wombey (1987-99); S Ke- ogh (1999-2003); N Mitchell (2004-5). -
Hydrological and Thermal Responses of Seeds from Four Co-Occurring Tree Species from Southwest Western Australia
Volume 8 • 2020 10.1093/conphys/coaa021 Research article Hydrological and thermal responses of seeds from four co-occurring tree species from southwest Western Australia RajapaksheP.V.G.S.W.Rajapakshe1,2,3, Shane R. Turner3,2,4, Adam T. Cross1 and Sean Tomlinson2,3,* 1 Centre for Mine Site Restoration, School of Molecular and Life Sciences, Curtin University, PO Box U1987, Perth, Western Australia 6845, Australia 2School of Molecular and Life Sciences, Curtin University, PO Box U1987, Perth, Western Australia 6845, Australia 3Kings Park Science, Department of Biodiversity, Conservation and Attractions, Kattidj Close, Kings Park, WA 6005, Australia 4School of Biological Sciences, Faculty of Science, The University of Western Australia, Crawley, WA 6009, Australia *Corresponding author: School of Molecular and Life Sciences, Curtin University, PO Box U1987, Perth, Western Australia 6845, Australia Email: [email protected] .......................................................................................................................................................... Seed germination is a critical stage in the life cycle of most plants and is defined by specific tolerance thresholds beyond which rates and success of germination rapidly decline. Previous studies have demonstrated that widespread plant species commonly germinate over a broad range of temperatures and water stress levels, whereas range-restricted species often exhibit a narrower germination window in terms of temperature and moisture. We investigated the relationships of the key ◦ germination traits of maximum germination (Gmax) and time to 50% germination (t50) in response to temperature (5–35 C) and water stress (−1.5–0 MPa) in four co-occurring Western Australian native Eucalyptus species with widely varying biogeography. Eucalyptus caesia subsp. caesia and E. ornata exhibit a highly localized distribution and a narrow geographical range, being restricted either to granite outcrops or the upper slopes and tops of lateritic rises, respectively. -
ARAZPA Amphibian Action Plan
Appendix 1 to Murray, K., Skerratt, L., Marantelli, G., Berger, L., Hunter, D., Mahony, M. and Hines, H. 2011. Guidelines for minimising disease risks associated with captive breeding, raising and restocking programs for Australian frogs. A report for the Australian Government Department of Sustainability, Environment, Water, Population and Communities. ARAZPA Amphibian Action Plan Compiled by: Graeme Gillespie, Director Wildlife Conservation and Science, Zoos Victoria; Russel Traher, Amphibian TAG Convenor, Curator Healesville Sanctuary Chris Banks, Wildlife Conservation and Science, Zoos Victoria. February 2007 1 1. Background Amphibian species across the world have declined at an alarming rate in recent decades. According to the IUCN at least 122 species have gone extinct since 1980 and nearly one third of the world’s near 6,000 amphibian species are classified as threatened with extinction, placing the entire class at the core of the current biodiversity crisis (IUCN, 2006). Australasia too has experienced significant declines; several Australian species are considered extinct and nearly 25% of the remainder are threatened with extinction, while all four species native to New Zealand are threatened. Conventional causes of biodiversity loss, habitat destruction and invasive species, are playing a major role in these declines. However, emergent disease and climate change are strongly implicated in many declines and extinctions. These factors are now acting globally, rapidly and, most disturbingly, in protected and near pristine areas. Whilst habitat conservation and mitigation of threats in situ are essential, for many taxa the requirement for some sort of ex situ intervention is mounting. In response to this crisis there have been a series of meetings organised by the IUCN (World Conservation Union), WAZA (World Association of Zoos & Aquariums) and CBSG (Conservation Breeding Specialist Group, of the IUCN Species Survival Commission) around the world to discuss how the zoo community can and should respond. -
Granite Outcrops: a Collective Ecosystem
JournalJournal of theof the Royal Royal Society Society of Westernof Western Australia, Australia, 80(3), 80:113-122, September 1997 1997 Granite outcrops: A collective ecosystem B York Main Department of Zoology, University of Western Australia, Nedlands Western Australia 6907 email: [email protected] Abstract Ecological systems of granite outcrops are posed as having arisen through one of two processes or through a combination of both processes; through colonisation of exposed and weathered rock surfaces and/or through retention of components of relict biotic assemblages surrounding such exposures. In the context of such evolved ecological systems, the inter-relationships of outcrop configuration, the geological and climatic history and associated changes from mesophytic to sclerophyll or xeric vegetation of surrounding landscapes is discussed with reference to selected outcrops. Introduction inclusion of particular rocks in the nature reserve system of Western Australia. Ecosystem, like biodiversity, is an “in” word. But what does it mean? As an abbreviation of ecological The “island” concept of outcrops has been generally system, it denotes some sort of interaction of life forms stimulated by observation of their present biotic and dependence within a physical, non-biological distinctiveness or biotic disjunction with their immediate framework on which the living forms in turn have some surrounds, particularly in relation to vegetation and effect. As a system, an inherent cohesion is intimated; ephemeral aquatic fauna. While documentation of external limits are inferred. All this in turn suggests that vegetation, vertebrates and aquatic invertebrates has an ecosystem has boundaries. A dictionary supports this already been undertaken on selected granite outcrops concept in the definition “The plants and animals of a (see elsewhere in this issue), the terrestrial and/or lithic particular habitat, together with the environment influenced invertebrates are less well known. -
Predation by Introduced Cats Felis Catus on Australian Frogs: Compilation of Species Records and Estimation of Numbers Killed
Predation by introduced cats Felis catus on Australian frogs: compilation of species records and estimation of numbers killed J. C. Z. WoinarskiA,M, S. M. LeggeB,C, L. A. WoolleyA,L, R. PalmerD, C. R. DickmanE, J. AugusteynF, T. S. DohertyG, G. EdwardsH, H. GeyleA, H. McGregorI, J. RileyJ, J. TurpinK and B. P. MurphyA ANESP Threatened Species Recovery Hub, Research Institute for the Environment and Livelihoods, Charles Darwin University, Darwin, NT 0909, Australia. BNESP Threatened Species Recovery Hub, Centre for Biodiversity and Conservation Research, University of Queensland, St Lucia, Qld 4072, Australia. CFenner School of the Environment and Society, Linnaeus Way, The Australian National University, Canberra, ACT 2602, Australia. DWestern Australian Department of Biodiversity, Conservation and Attractions, Bentley, WA 6983, Australia. ENESP Threatened Species Recovery Hub, Desert Ecology Research Group, School of Life and Environmental Sciences, University of Sydney, NSW 2006, Australia. FQueensland Parks and Wildlife Service, Red Hill, Qld 4701, Australia. GCentre for Integrative Ecology, School of Life and Environmental Sciences (Burwood campus), Deakin University, Geelong, Vic. 3216, Australia. HNorthern Territory Department of Land Resource Management, PO Box 1120, Alice Springs, NT 0871, Australia. INESP Threatened Species Recovery Hub, School of Biological Sciences, University of Tasmania, Hobart, Tas. 7001, Australia. JSchool of Biological Sciences, University of Bristol, 24 Tyndall Avenue, Bristol BS8 1TQ, United Kingdom. KDepartment of Terrestrial Zoology, Western Australian Museum, 49 Kew Street, Welshpool, WA 6106, Australia. LPresent address: WWF-Australia, 3 Broome Lotteries House, Cable Beach Road, Broome, WA 6276, Australia. MCorresponding author. Email: [email protected] Table S1. Data sources used in compilation of cat predation on frogs.