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Amphibian Abundance and Detection Trends During a Large Flood in a Semi-Arid Floodplain Wetland
Herpetological Conservation and Biology 11:408–425. Submitted: 26 January 2016; Accepted: 2 September 2016; Published: 16 December 2016. Amphibian Abundance and Detection Trends During a Large Flood in a Semi-Arid Floodplain Wetland Joanne F. Ocock1,4, Richard T. Kingsford1, Trent D. Penman2, and Jodi J.L. Rowley1,3 1Centre for Ecosystem Science, School of Biological, Earth and Environmental Sciences, UNSW Australia, Sydney, New South Wales, 2052, Australia 2Centre for Environmental Risk Management of Bushfires, Institute of Conservation Biology and Environmental Management, University of Wollongong, Wollongong, New South Wales 2522, Australia 3Australian Museum Research Institute, Australian Museum, 6 College St, Sydney, New South Wales 2010, Australia 4Corresponding author, email: [email protected] Abstract.—Amphibian abundance and occupancy are often reduced in regulated river systems near dams, but com- paratively little is known about how they are affected on floodplain wetlands downstream or the effects of actively managed flows. We assessed frog diversity in the Macquarie Marshes, a semi-arid floodplain wetland of conserva- tion significance, identifying environmental variables that might explain abundances and detection of species. We collected relative abundance data of 15 amphibian species at 30 sites over four months, coinciding with a large natural flood. We observed an average of 39.9 ± (SE) 4.3 (range, 0-246) individuals per site survey, over 47 survey nights. Three non-burrowing, ground-dwelling species were most abundant at temporarily flooded sites with low- growing aquatic vegetation (e.g., Limnodynastes tasmaniensis, Limnodynastes fletcheri, Crinia parinsignifera). Most arboreal species (e.g., Litoria caerulea) were more abundant in wooded habitat, regardless of water permanency. -
Threat Abatement Plan
gus resulting in ch fun ytridio trid myc chy osis ith w s n ia ib h p m a f o n o i t THREAT ABATEMENTc PLAN e f n I THREAT ABATEMENT PLAN INFECTION OF AMPHIBIANS WITH CHYTRID FUNGUS RESULTING IN CHYTRIDIOMYCOSIS Department of the Environment and Heritage © Commonwealth of Australia 2006 ISBN 0 642 55029 8 Published 2006 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, available from the Department of the Environment and Heritage. Requests and inquiries concerning reproduction and rights should be addressed to: Assistant Secretary Natural Resource Management Policy Branch Department of the Environment and Heritage PO Box 787 CANBERRA ACT 2601 This publication is available on the Internet at: www.deh.gov.au/biodiversity/threatened/publications/tap/chytrid/ For additional hard copies, please contact the Department of the Environment and Heritage, Community Information Unit on 1800 803 772. Front cover photo: Litoria genimaculata (Green-eyed tree frog) Sequential page photo: Taudactylus eungellensis (Eungella day frog) Banner photo on chapter pages: Close up of the skin of Litoria genimaculata (Green-eyed tree frog) ii Foreword ‘Infection of amphibians with chytrid fungus resulting Under the EPBC Act the Australian Government in chytridiomycosis’ was listed in July 2002 as a key implements the plan in Commonwealth areas and seeks threatening process under the Environment Protection the cooperation of the states and territories where the and Biodiversity Conservation Act 1999 (EPBC Act). disease impacts within their jurisdictions. -
Expert Witness Report
Expert Witness Report Report prepared on instructions of: Bleyer Lawyers, Level 1, 550 Lonsdale Street, Melbourne, Vic 3000 Australia Prepared by: Graeme Gillespie B.Sc. Ph.D. 55 Union Street, Northcote, Vic 3070, Australia Curriculum Vitae Attached (Appendix I) I have read the Expert Witness Code of Conduct and agree to be bound by it. Graeme Gillespie 23 February 2010 Qualifications and Experience Please see my curriculum vitae (Appendix I) for my general qualifications and experience. My Ph.D. in zoology focussed specifically on the conservation biology and ecology of frog species in south-eastern Australia. I have 23 years of field and scientific experience studying amphibians and their conservation and management in south- eastern Australia. I have published 24 refereed scientific papers and 38 technical reports on amphibian ecology, conservation and management. I am recognised throughout Australia as an authority on the frog fauna of Victoria, specifically with respect to conservation issues, and I am regularly asked to provide advice on such matters to individuals, government conservation and land management agencies, and non-government organisations. With regard to the Giant Burrowing Frog, I encountered this species on several occasions between 1986 and 1992 while undertaking and supervising pre-logging biodiversity surveys in East Gippsland, Victoria. These records are documented in the Victorian Wildlife Atlas. During this period, I gained knowledge of the species’ habitat associations, breeding biology, some aspects of its behaviour and an appreciation of its conservation status in Victoria (see Opie et al. 1990; Westaway et al.1990; Lobert et al. 1991). Because of my research into amphibian conservation and management, I am highly familiar with the existing literature on the impact of various forest management activities on amphibians and the implications of these activities for amphibian conservation. -
Toxicity of Glyphosate on Physalaemus Albonotatus (Steindachner, 1864) from Western Brazil
Ecotoxicol. Environ. Contam., v. 8, n. 1, 2013, 55-58 doi: 10.5132/eec.2013.01.008 Toxicity of Glyphosate on Physalaemus albonotatus (Steindachner, 1864) from Western Brazil F. SIMIONI 1, D.F.N. D A SILVA 2 & T. MO tt 3 1 Laboratório de Herpetologia, Instituto de Biociências, Universidade Federal de Mato Grosso, Cuiabá, Mato Grosso, Brazil. 2 Programa de Pós-Graduação em Ecologia e Conservação da Biodiversidade, Universidade Federal de Mato Grosso, Cuiabá, Mato Grosso, Brazil. 3 Setor de Biodiversidade e Ecologia, Universidade Federal de Alagoas, Av. Lourival Melo Mota, s/n, Maceió, Alagoas, CEP 57072-970, Brazil. (Received April 12, 2012; Accept April 05, 2013) Abstract Amphibian declines have been reported worldwide and pesticides can negatively impact this taxonomic group. Brazil is the world’s largest consumer of pesticides, and Mato Grosso is the leader in pesticide consumption among Brazilian states. However, the effects of these chemicals on the biota are still poorly explored. The main goals of this study were to determine the acute toxicity (CL50) of the herbicide glyphosate on Physalaemus albonotatus, and to assess survivorship rates when tadpoles are kept under sub-lethal concentrations. Three egg masses of P. albonotatus were collected in Cuiabá, Mato Grosso, Brazil. Tadpoles were exposed for 96 h to varying concentrations of glyphosate to determine the CL50 and survivorship. The -1 CL50 was 5.38 mg L and there were statistically significant differences in mortality rates and the number of days that P. albonotatus tadpoles survived when exposed in different sub-lethal concentrations of glyphosate. Different sensibilities among amphibian species may be related with their historical contact with pesticides and/or specific tolerances. -
Maritime Southeast Asia and Oceania Regional Focus
November 2011 Vol. 99 www.amphibians.orgFrogLogNews from the herpetological community Regional Focus Maritime Southeast Asia and Oceania INSIDE News from the ASG Regional Updates Global Focus Recent Publications General Announcements And More..... Spotted Treefrog Nyctixalus pictus. Photo: Leong Tzi Ming New The 2012 Sabin Members’ Award for Amphibian Conservation is now Bulletin open for nomination Board FrogLog Vol. 99 | November 2011 | 1 Follow the ASG on facebook www.facebook.com/amphibiansdotor2 | FrogLog Vol. 99| November 2011 g $PSKLELDQ$UN FDOHQGDUVDUHQRZDYDLODEOH 7KHWZHOYHVSHFWDFXODUZLQQLQJSKRWRVIURP $PSKLELDQ$UN¶VLQWHUQDWLRQDODPSKLELDQ SKRWRJUDSK\FRPSHWLWLRQKDYHEHHQLQFOXGHGLQ $PSKLELDQ$UN¶VEHDXWLIXOZDOOFDOHQGDU7KH FDOHQGDUVDUHQRZDYDLODEOHIRUVDOHDQGSURFHHGV DPSKLELDQDUN IURPVDOHVZLOOJRWRZDUGVVDYLQJWKUHDWHQHG :DOOFDOHQGDU DPSKLELDQVSHFLHV 3ULFLQJIRUFDOHQGDUVYDULHVGHSHQGLQJRQ WKHQXPEHURIFDOHQGDUVRUGHUHG±WKHPRUH \RXRUGHUWKHPRUH\RXVDYH2UGHUVRI FDOHQGDUVDUHSULFHGDW86HDFKRUGHUV RIEHWZHHQFDOHQGDUVGURSWKHSULFHWR 86HDFKDQGRUGHUVRIDUHSULFHGDW MXVW86HDFK 7KHVHSULFHVGRQRWLQFOXGH VKLSSLQJ $VZHOODVRUGHULQJFDOHQGDUVIRU\RXUVHOIIULHQGV DQGIDPLO\ZK\QRWSXUFKDVHVRPHFDOHQGDUV IRUUHVDOHWKURXJK\RXU UHWDLORXWOHWVRUIRUJLIWV IRUVWDIIVSRQVRUVRUIRU IXQGUDLVLQJHYHQWV" 2UGHU\RXUFDOHQGDUVIURPRXUZHEVLWH ZZZDPSKLELDQDUNRUJFDOHQGDURUGHUIRUP 5HPHPEHU±DVZHOODVKDYLQJDVSHFWDFXODUFDOHQGDU WRNHHSWUDFNRIDOO\RXULPSRUWDQWGDWHV\RX¶OODOVREH GLUHFWO\KHOSLQJWRVDYHDPSKLELDQVDVDOOSUR¿WVZLOOEH XVHGWRVXSSRUWDPSKLELDQFRQVHUYDWLRQSURMHFWV ZZZDPSKLELDQDUNRUJ FrogLog Vol. 99 | November -
Frogs of the Perth Region – Darling Range
FROGS OF THE PERTH REGION Darling Range Eight species of frogs are found commonly along streams and in the many small swamps in the Darling Range east of Perth. All of these species breed during the wetter months between late autumn and early spring. B. Maryan D. Robinson Whooping Frog Crawling Toadlet Heleioporus inornatus Pseudophryne guentheri BUILD: stout round body and short limbs, BUILD: flattened body, small head and short males have black nuptial spine on first finger limbs LENGTH: maximum length 7cm LENGTH: maximum length 3.5cm LOOK FOR: uniformly copper brown back, LOOK FOR: ‘warty’ back mottled with browns flanks may be mottled with white, grey or and grey, belly blotchy with black on white yellow background, crawls BREEDING SEASON: late autumn BREEDING SEASON: winter MALE CALL: ‘whoop whoop whoop’ MALE CALL: short, sharp grating sound B. Maryan D. Robinson Sand Frog Western Spotted Frog Heleioporus psammophilus Heleioporus albopunctatus BUILD: robust body with short limbs, males BUILD: large with a robust build may have black nuptial spine on first finger LENGTH: maximum length 8.5cm LENGTH: maximum length 6cm LOOK FOR: white or yellow spots on LOOK FOR: back brown to dark grey. Pale chocolate brown body coloured bumps on lower flanks BREEDING SEASON: late autumn BREEDING SEASON: late autumn MALE CALL: short, high pitched ‘coo’ MALE CALL: high pitched trilling ‘purr’ D. Robinson D. Robinson Humming Frog Hooting Frog Neobatrachus pelobatoides Heleioporus barycragus BUILD: medium size, flat broad head, robust BUILD: males have massive front arms and with short legs black nuptial spine on first finger LENGTH: maximum length 4.5cm LENGTH: maximum length 9cm LOOK FOR: back patterns with base colour LOOK FOR: greyish to chocolate brown body of green or grey with darker green or brown with scattering of yellow spots on its flanks irregular patterns. -
Spatial Ecology of the Giant Burrowing Frog (Heleioporus Australiacus): Implications for Conservation Prescriptions
University of Wollongong Research Online Faculty of Science - Papers (Archive) Faculty of Science, Medicine and Health January 2008 Spatial ecology of the giant burrowing frog (Heleioporus australiacus): implications for conservation prescriptions Trent D. Penman University of Wollongong, [email protected] F Lemckert M J Mahony Follow this and additional works at: https://ro.uow.edu.au/scipapers Part of the Life Sciences Commons, Physical Sciences and Mathematics Commons, and the Social and Behavioral Sciences Commons Recommended Citation Penman, Trent D.; Lemckert, F; and Mahony, M J: Spatial ecology of the giant burrowing frog (Heleioporus australiacus): implications for conservation prescriptions 2008, 179-186. https://ro.uow.edu.au/scipapers/724 Research Online is the open access institutional repository for the University of Wollongong. For further information contact the UOW Library: [email protected] Spatial ecology of the giant burrowing frog (Heleioporus australiacus): implications for conservation prescriptions Abstract Management of threatened anurans requires an understanding of a species’ behaviour and habitat requirements in both the breeding and non-breeding environments. The giant burrowing frog (Heleioporus australiacus) is a threatened species in south-eastern Australia. Little is known about its habitat requirements, creating difficulties in vde eloping management strategies for the species.Weradio-tracked 33 individual H. australiacus in order to determine their habitat use and behaviour. Data from 33 frogs followed for between 5 and 599 days show that individuals spend little time near (<15 >m) their breeding sites (mean 4.7 days for males and 6.3 days for females annually). Most time is spent in distinct non- breeding activity areas 20–250m from the breeding sites. -
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. -
An Insectivorous Australian Pratincole Stiltia Isabella Diversifies Its Diet
Northern Territory Naturalist (2013) 24: 61–64 Short Note An insectivorous Australian Pratincole Stiltia isabella diversifies its diet Peter M. Kyne1 and Micha V. Jackson2 1 Research Institute for the Environment and Livelihoods, Charles Darwin University, Darwin NT 0909, Australia. Email: [email protected] 2 North Australian Indigenous Land and Sea Management Alliance Limited, Charles Darwin University, Darwin NT 0909, Australia. Abstract Pratincoles and coursers (family Glareolidae), including the primarily ground-feeding Australian Pratincole Stiltia isabella, are principally insectivorous. This paper presents a brief note on the first documented occurrence of Australian Pratincole (and indeed a rare record of any glareolid bird) feeding on vertebrate prey, in this case a small frog. The family Glareolidae is made up of two distinct sub-families, the coursers (Cursoriinae) and the pratincoles (Glareolinae), both of which are principally insectivorous (del Hoyo et al. 1996; Higgins & Davies 1996). Coursers are mostly ground feeders while pratincoles are mostly aerial feeders; the exception is the Australian Pratincole Stiltia isabella (the sole member of its genus), which forms a link between the two groups and is the only pratincole to feed primarily on the ground (Maclean 1976; del Hoyo et al. 1996). Stomach contents and feeding records indicate that a diversity of insects constitute the species’ diet, with additional prey items including centipedes (Myriapoda) and spiders (Arachnida) (Maclean 1976; Barker & Vestjens 1989; Higgins & Davies 1996). While del Hoyo et al. (1996) state that glareorids will sometimes take small lizards, they do not indicate the group or species for which this has been recorded. Here we present a brief note on the first documented occurrence of Australian Pratincole (and indeed a rare record of any glareolid bird) feeding on vertebrate prey. -
Distribution and Calling Phenology of Generalist Frog Species Along a Climate Gradient
Distribution and calling phenology of generalist frog species along a climate gradient Amelia Walcott A thesis submitted in fulfilment of the requirements for the degree of Doctor of Philosophy Charles Sturt University Faculty of Science School of Environmental Sciences Albury, NSW 2640 Australia January 2017 i ii iii iv TABLE OF CONTENTS List of Figures ......................................................................................................................................... x List of Tables....................................................................................................................................... xiii List of Plates ........................................................................................................................................ xiv Certificate of Authorship ................................................................................................................ xv Acknowledgements ......................................................................................................................... xvii Abstract ................................................................................................................................................ xix Chapter 1 General introduction: Environmental drivers of amphibian distribution and resource use in modified temperate ecosystems ........................................................... 1 1.1 Wetland and amphibian decline ....................................................................................... -
National Recovery Plan for the Stuttering Frog Mixophyes Balbus
National Recovery Plan for the Stuttering Frog Mixophyes balbus David Hunter and Graeme Gillespie Prepared by David Hunter and Graeme Gillespie (Department of Sustainability and Environment, Victoria). Published by the Victorian Government Department of Sustainability and Environment (DSE) Melbourne, October 2011. © State of Victoria Department of Sustainability and Environment 2010 This publication is copyright. No part may be reproduced by any process except in accordance with the provisions of the Copyright Act 1968. Authorised by the Victorian Government, 8 Nicholson Street, East Melbourne. ISBN 978-1-74242-369-2 (online) This is a Recovery Plan prepared under the Commonwealth Environment Protection and Biodiversity Conservation Act 1999, with the assistance of funding provided by the Australian Government. This Recovery Plan has been developed with the involvement and cooperation of a range of stakeholders, but individual stakeholders have not necessarily committed to undertaking specific actions. The attainment of objectives and the provision of funds may be subject to budgetary and other constraints affecting the parties involved. Proposed actions may be subject to modification over the life of the plan due to changes in knowledge. Disclaimer: This publication may be of assistance to you but the State of Victoria and its employees do not guarantee that the publication is without flaw of any kind or is wholly appropriate for your particular purposes and therefore disclaims all liability for any error, loss or other consequence that may arise from you relying on any information in this publication. An electronic version of this document is available on the Department of the Environment, Water, Heritage and the Arts website www.environment.gov.au For more information contact the DSE Customer Service Centre 136 186 Citation: Hunter, D. -
2219573-REP-Marine Assessment Report AR
Appendix L – Marine Assessment GHD | Report for Hunter Water Corporation - Belmont Drought Response Desalination Plant, 2219573 Hunter Water Corporation Belmont Drought Response Desalination Plant Marine Environment Assessment Amendment Report July 2020 Table of contents 1. Introduction..................................................................................................................................... 1 1.1 Background .......................................................................................................................... 1 1.2 Purpose and structure of this report .................................................................................... 2 2. Project changes ............................................................................................................................. 4 2.1 Overview .............................................................................................................................. 4 2.2 Key features of the amended Project .................................................................................. 4 3. Methodology ................................................................................................................................... 7 3.1 Review of relevant legislation .............................................................................................. 7 3.2 Review of databases and searches ..................................................................................... 7 3.3 Review of previous marine ecology reports ........................................................................