From Fish to Philosopher; the Story of Our Internal Environment
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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. -
Population Density of Tarsius Dianae in Central Sulawesi
10 Asian Primates Journal 1(1), 2008 RELATIVE POPULATION DENSITY OF Tarsius dianae IN MAN-INFLUENCED HABITATS OF LORE LINDU NATIONAL PARK, CENTRAL SULAWESI, INDONESIA Indra Yustian1, Stefan Merker2, Jatna Supriatna3, and Noviar Andayani4 1 Dept. of Biology, Faculty of Mathematics and Natural Sciences, University of Sriwijaya, Indonesia. 2 Institute of Anthropology, University of Mainz, Germany. 3 Conservation International Indonesia and Department of Biology, University of Indonesia. 4 Wildlife Conservation Society-Indonesia Program and Department of Biology, University of Indonesia, Indonesia. ABSTRACT The aim of this study was to know the impact of human activities on population density of Tarsius dianae by estimating the relative population density in four habitat types differently influenced by man. The study was conducted in the vicinity of Kamarora, at the northeastern boundary of Lore Lindu National Park, Central Sulawesi. Four different habitats were chosen: (H1) primary or old secondary forest; (H2) secondary forest ± 30 years after clearance with small-scale selective logging; (H3) forest with interspersed small coffee and cocoa plantations; and (H4) forest with selective logging and plantations. The tarsiers’ sleeping sites were determined using triangulation. Relative population density was estimated by measuring the average distances between three nearest neighbors. The results suggest that different human-influenced habitat have different effects on tarsier’s density. The smallest distances (116.2 ± 18 m) between sleeping sites, which represent the highest estimated population density (57.1 groups in one square km), were found in habitat type H1, the least disturbed habitat. Estimated population density in habitat type H3 or “forest plantations” was 38 groups/km2, followed by habitat type H2 or secondary forest with selective logging 36.4 groups/km2, and the smallest population density was estimated at 32.9 groups/km2 in habitat type H4 or forest with selective logging and plantations. -
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. -
Tinamiformes – Falconiformes
LIST OF THE 2,008 BIRD SPECIES (WITH SCIENTIFIC AND ENGLISH NAMES) KNOWN FROM THE A.O.U. CHECK-LIST AREA. Notes: "(A)" = accidental/casualin A.O.U. area; "(H)" -- recordedin A.O.U. area only from Hawaii; "(I)" = introducedinto A.O.U. area; "(N)" = has not bred in A.O.U. area but occursregularly as nonbreedingvisitor; "?" precedingname = extinct. TINAMIFORMES TINAMIDAE Tinamus major Great Tinamou. Nothocercusbonapartei Highland Tinamou. Crypturellus soui Little Tinamou. Crypturelluscinnamomeus Thicket Tinamou. Crypturellusboucardi Slaty-breastedTinamou. Crypturellus kerriae Choco Tinamou. GAVIIFORMES GAVIIDAE Gavia stellata Red-throated Loon. Gavia arctica Arctic Loon. Gavia pacifica Pacific Loon. Gavia immer Common Loon. Gavia adamsii Yellow-billed Loon. PODICIPEDIFORMES PODICIPEDIDAE Tachybaptusdominicus Least Grebe. Podilymbuspodiceps Pied-billed Grebe. ?Podilymbusgigas Atitlan Grebe. Podicepsauritus Horned Grebe. Podicepsgrisegena Red-neckedGrebe. Podicepsnigricollis Eared Grebe. Aechmophorusoccidentalis Western Grebe. Aechmophorusclarkii Clark's Grebe. PROCELLARIIFORMES DIOMEDEIDAE Thalassarchechlororhynchos Yellow-nosed Albatross. (A) Thalassarchecauta Shy Albatross.(A) Thalassarchemelanophris Black-browed Albatross. (A) Phoebetriapalpebrata Light-mantled Albatross. (A) Diomedea exulans WanderingAlbatross. (A) Phoebastriaimmutabilis Laysan Albatross. Phoebastrianigripes Black-lootedAlbatross. Phoebastriaalbatrus Short-tailedAlbatross. (N) PROCELLARIIDAE Fulmarus glacialis Northern Fulmar. Pterodroma neglecta KermadecPetrel. (A) Pterodroma -
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. -
Reproductive Biology of the Opossum Pipefish, Microphis Brachyurus Lineatus, in Tecolutla Estuary, Veracruz, Mexico
Gulf and Caribbean Research Volume 16 Issue 1 January 2004 Reproductive Biology of the Opossum Pipefish, Microphis brachyurus lineatus, in Tecolutla Estuary, Veracruz, Mexico Martha Edith Miranda-Marure Universidad Nacional Autonoma de Mexico Jose Antonio Martinez-Perez Universidad Nacional Autonoma de Mexico Nancy J. Brown-Peterson University of Southern Mississippi, [email protected] Follow this and additional works at: https://aquila.usm.edu/gcr Part of the Marine Biology Commons Recommended Citation Miranda-Marure, M. E., J. A. Martinez-Perez and N. J. Brown-Peterson. 2004. Reproductive Biology of the Opossum Pipefish, Microphis brachyurus lineatus, in Tecolutla Estuary, Veracruz, Mexico. Gulf and Caribbean Research 16 (1): 101-108. Retrieved from https://aquila.usm.edu/gcr/vol16/iss1/17 DOI: https://doi.org/10.18785/gcr.1601.17 This Article is brought to you for free and open access by The Aquila Digital Community. It has been accepted for inclusion in Gulf and Caribbean Research by an authorized editor of The Aquila Digital Community. For more information, please contact [email protected]. Gulf and Caribbean Research Vol 16, 101–108, 2004 Manuscript received September 25, 2003; accepted December 12, 2003 REPRODUCTIVE BIOLOGY OF THE OPOSSUM PIPEFISH, MICROPHIS BRACHYURUS LINEATUS, IN TECOLUTLA ESTUARY, VERACRUZ, MEXICO Martha Edith Miranda-Marure, José Antonio Martínez-Pérez, and Nancy J. Brown-Peterson1 Laboratorio de Zoología, Universidad Nacional Autónoma de México, Facultad de Estudios Superiores Iztacala. Av., de los Barrios No.1, Los Reyes Iztacala, Tlalnepantla, Estado de México, C.P. 05490 Mexico 1Department of Coastal Sciences, The University of Southern Mississippi, 703 East Beach Drive, Ocean Springs, MS 39564 USA ABSTRACT The reproductive biology of the opossum pipefish, Microphis brachyurus lineatus, was investigated in Tecolutla estuary, Veracruz, Mexico, to determine sex ratio, size at maturity, gonadal and brood pouch histology, reproductive seasonality, and fecundity of this little-known syngnathid. -
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. -
The Spectral Tarsier Sharon L
PRIMATE FIELD STUDIES Series Editors: Robert W. Sussman, Washington University Natalie Vasey, Portland State University Series Editorial Board: Simon Bearder, Oxford-Brookes University Marina Cords, Columbia University Agustin Fuentes, Notre Dame University Paul Garber, University of Illinois Annie Gautier-Hion, Station Biologique de Paimpont Joanna Lambert, University of Wisconsin Robert D. Martin, Field Museum Deborah Overdorff, University of Texas Jane Phillips-Conroy, Washington University Karen Strier, University of Wisconsin Series Titles: The Spectral Tarsier Sharon L. Gursky, Texas A&M University Strategies of Sex and Survival in Hamadryas Baboons: Through a Female Lens Larissa Swedell, Queens College, The City University of New York The Behavioral Ecology of Callimicos and Tamarins in Northwestern Bolivia Leila M. Porter, Northern Illinois University The Socioecology of Adult Female Patas Monkeys and Vervets Jill D. Pruetz, Iowa State University Apes of the Impenetrable Forest: The Behavioral Ecology of Sympatric Chimpanzees and Gorillas Craig B. Stanford, University of Southern California PRIMATE FIELD STUDIES Many of us who conduct field studies on wild primates have witnessed a decline in the venues available to publish monographic treatments of our work. As researchers we have few choices other than to publish short tech- nical articles on discrete aspects of our work in professional journals. Also in vogue are popular expositions, often written by non-scientists. To counter this trend, we have begun this series. Primate Field Studies is a venue both for publishing the full complement of findings of long-term studies, and for making our work accessible to a wider readership. Interested readers need not wait for atomized parts of long-term studies to be published in widely scattered journals; students need not navigate the technical literature to bring together a body of scholarship better served by being offered as a cohesive whole. -
Ecology and Behaviour of Tarsius Syrichta in the Wild
O',F Tarsius syrichta ECOLOGY AND BEHAVIOUR - IN BOHOL, PHILIPPINES: IMPLICATIONS FOR CONSERVATION By Irene Neri-Arboleda D.V.M. A thesis submitted in fulfillment of the requirements for the degree of Master of Applied Science Department of Applied and Molecular Ecology University of Adelaide, South Australia 2001 TABLE OF CONTENTS DAge Title Page I Table of Contents............ 2 List of Tables..... 6 List of Figures.... 8 Acknowledgements... 10 Dedication 11 I)eclaration............ t2 Abstract.. 13 Chapter I GENERAL INTRODUCTION... l5 1.1 Philippine Biodiversity ........... t6 1.2 Thesis Format.... l9 1.3 Project Aims....... 20 Chapter 2 REVIEIV OF TARSIER BIOLOGY...... 2t 2.1 History and Distribution..... 22 2.t.1 History of Discovery... .. 22 2.1.2 Distribution...... 24 2.1.3 Subspecies of T. syrichta...... 24 2.2 Behaviour and Ecology.......... 27 2.2.1 Home Ranges. 27 2.2.2 Social Structure... 30 2.2.3 Reproductive Behaviour... 3l 2.2.4 Diet and Feeding Behaviour 32 2.2.5 Locomotion and Activity Patterns. 34 2.2.6 Population Density. 36 2.2.7 Habitat Preferences... ... 37 2.3 Summary of Review. 40 Chapter 3 FßLD SITE AI\D GEIYERAL METHODS.-..-....... 42 3.1 Field Site........ 43 3. 1.1 Geological History of the Philippines 43 3.1.2 Research Area: Corella, Bohol. 44 3.1.3 Physical Setting. 47 3.t.4 Climate. 47 3.1.5 Flora.. 50 3.1.6 Fauna. 53 3.1.7 Human Population 54 t page 3.1.8 Tourism 55 3.2 Methods.. 55 3.2.1 Mapping. -
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.