Mountain Pygmy-Possum Action Statement 1
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
Australian Alps Walking Track
AUSTRALIAN ALPS WALKING TRACK MAP COVERAGE GUIDE Victorian Leg: 1:50K VicMap Topographic Maps Spatial Vision Rooftop’s Adventure Maps Outdoor Recreation Maps Walhalla North Gardens 8122-S Camping Ground Walhalla- Aberfeldy Walhalla 8122-N Woods Point Buller-Howitt Skene 8123-S (1:100K, 2006) Alpine Area (1:50K, 2009) Moroka 8223-S Jamieson- Licola Selwyn Mount Howitt 8223-N Cobungra 8323-N (1:100K, 2004) Bogong Bright- Alpine Area Falls Creek 8324-S Mansfield (1:50K, 2011) Leinster 8424-S (1:100K, 2006) Gibbo 8424-N Dargo- Willis/Suggan Buggan 8524-S Wonnangatta (1:100K, 2006) VICTORIA NEW SOUTH WALES NSW Leg: 1:25K NSW LPI Topographic Maps Suggan Buggan/Willis (1:50K) 8524-S Charcoal Range 8524-1S Corryong-Omeo - Thredbo Davies Plain 8524-4S (1:100K, 2007) Tom Groggin 8524-4N Chimneys Ridge 8524-1N Kosciuszko Perisher Valley Mount Kosciuszko 8525-2S Rooftop’s Actvities Maps Alpine Area Geehi Dam 8525-2N ( 1:50K, 2009) Jagungal 8525-1S Kosciuszko National Park Toolong Range 8525-1N (1:50K, 2008) Old Adaminaby 8625-4N Denison 8626-3S Cabramurra 8526-2-S Kosciuszko Northern Ravine Kiandra 8526-2-N (1:50K, 2011) Tantangara 8626-3N Rules Point 8626-4S Rendezvous Creek 8626-1S Namadgi- Corin Dam Namadgi 8626-1N ACT South National Park (1:50K, 2011) Williamsdale Visitor Centre 8726-4N Note: Map is schematic and for illustrative purposes only. Locations shown Tharwa relate to the Topographic Map listed to the left of each marked point. Australian Alps Walking Track Leg Distance Time Elevation Range 1: Walhalla to Mt Victor 77.1km 30 Hours 225m -
Wombat Mange Information Sheet
WOMBAT MANGE INFORMATION SHEET WHAT IS WOMBAT MANGE? EFFECTS OF WOMBAT MANGE Wombat mange is a disease caused by the parasitic mite, Wombat mange has significant health and welfare impacts for Sarcoptes scabiei. The mite burrows into the skin of its host individual wombats. If left untreated, mange can result in the causing thick, crusty skin, and hair loss. Mange can affect lots of death of affected individuals. mammal species but the common wombat is one of the most Severe outbreaks of mange can result in a significant affected species. This is partly because wombats are burrowing reduction in wombat numbers in local areas as has occurred animals and burrows provide good conditions for mites to in Narawntapu National Park and nearby areas in northern survive and to spread between wombats. Tasmania. Mange has been present in mainland Australia and Tasmania Although mange occurs widely in Tasmania, monitoring of for over 200 years and there is good evidence that it was wombats by DPIPWE in eastern, northern, southern and introduced by Europeans and their domestic animals. central Tasmania for the past 35 years has shown that counts of wombats have generally been stable or have steadily WHERE DOES WOMBAT MANGE increased. There may be other localised declines of wombats OCCUR? that have not been detected. Mange occurs in most common wombat populations While mange may cause localised population declines of throughout their range. It generally occurs at low prevalence, wombats, there is very little evidence to suggest that the but more extreme outbreaks can occur within localised disease will cause wombats to go extinct in Tasmania. -
Platypus Collins, L.R
AUSTRALIAN MAMMALS BIOLOGY AND CAPTIVE MANAGEMENT Stephen Jackson © CSIRO 2003 All rights reserved. Except under the conditions described in the Australian Copyright Act 1968 and subsequent amendments, no part of this publication may be reproduced, stored in a retrieval system or transmitted in any form or by any means, electronic, mechanical, photocopying, recording, duplicating or otherwise, without the prior permission of the copyright owner. Contact CSIRO PUBLISHING for all permission requests. National Library of Australia Cataloguing-in-Publication entry Jackson, Stephen M. Australian mammals: Biology and captive management Bibliography. ISBN 0 643 06635 7. 1. Mammals – Australia. 2. Captive mammals. I. Title. 599.0994 Available from CSIRO PUBLISHING 150 Oxford Street (PO Box 1139) Collingwood VIC 3066 Australia Telephone: +61 3 9662 7666 Local call: 1300 788 000 (Australia only) Fax: +61 3 9662 7555 Email: [email protected] Web site: www.publish.csiro.au Cover photos courtesy Stephen Jackson, Esther Beaton and Nick Alexander Set in Minion and Optima Cover and text design by James Kelly Typeset by Desktop Concepts Pty Ltd Printed in Australia by Ligare REFERENCES reserved. Chapter 1 – Platypus Collins, L.R. (1973) Monotremes and Marsupials: A Reference for Zoological Institutions. Smithsonian Institution Press, rights Austin, M.A. (1997) A Practical Guide to the Successful Washington. All Handrearing of Tasmanian Marsupials. Regal Publications, Collins, G.H., Whittington, R.J. & Canfield, P.J. (1986) Melbourne. Theileria ornithorhynchi Mackerras, 1959 in the platypus, 2003. Beaven, M. (1997) Hand rearing of a juvenile platypus. Ornithorhynchus anatinus (Shaw). Journal of Wildlife Proceedings of the ASZK/ARAZPA Conference. 16–20 March. -
A Dated Phylogeny of Marsupials Using a Molecular Supermatrix and Multiple Fossil Constraints
Journal of Mammalogy, 89(1):175–189, 2008 A DATED PHYLOGENY OF MARSUPIALS USING A MOLECULAR SUPERMATRIX AND MULTIPLE FOSSIL CONSTRAINTS ROBIN M. D. BECK* School of Biological, Earth and Environmental Sciences, University of New South Wales, Sydney, New South Wales 2052, Australia Downloaded from https://academic.oup.com/jmammal/article/89/1/175/1020874 by guest on 25 September 2021 Phylogenetic relationships within marsupials were investigated based on a 20.1-kilobase molecular supermatrix comprising 7 nuclear and 15 mitochondrial genes analyzed using both maximum likelihood and Bayesian approaches and 3 different partitioning strategies. The study revealed that base composition bias in the 3rd codon positions of mitochondrial genes misled even the partitioned maximum-likelihood analyses, whereas Bayesian analyses were less affected. After correcting for base composition bias, monophyly of the currently recognized marsupial orders, of Australidelphia, and of a clade comprising Dasyuromorphia, Notoryctes,and Peramelemorphia, were supported strongly by both Bayesian posterior probabilities and maximum-likelihood bootstrap values. Monophyly of the Australasian marsupials, of Notoryctes þ Dasyuromorphia, and of Caenolestes þ Australidelphia were less well supported. Within Diprotodontia, Burramyidae þ Phalangeridae received relatively strong support. Divergence dates calculated using a Bayesian relaxed molecular clock and multiple age constraints suggested at least 3 independent dispersals of marsupials from North to South America during the Late Cretaceous or early Paleocene. Within the Australasian clade, the macropodine radiation, the divergence of phascogaline and dasyurine dasyurids, and the divergence of perameline and peroryctine peramelemorphians all coincided with periods of significant environmental change during the Miocene. An analysis of ‘‘unrepresented basal branch lengths’’ suggests that the fossil record is particularly poor for didelphids and most groups within the Australasian radiation. -
A Phylogeny and Timescale for Marsupial Evolution Based on Sequences for Five Nuclear Genes
J Mammal Evol DOI 10.1007/s10914-007-9062-6 ORIGINAL PAPER A Phylogeny and Timescale for Marsupial Evolution Based on Sequences for Five Nuclear Genes Robert W. Meredith & Michael Westerman & Judd A. Case & Mark S. Springer # Springer Science + Business Media, LLC 2007 Abstract Even though marsupials are taxonomically less diverse than placentals, they exhibit comparable morphological and ecological diversity. However, much of their fossil record is thought to be missing, particularly for the Australasian groups. The more than 330 living species of marsupials are grouped into three American (Didelphimorphia, Microbiotheria, and Paucituberculata) and four Australasian (Dasyuromorphia, Diprotodontia, Notoryctemorphia, and Peramelemorphia) orders. Interordinal relationships have been investigated using a wide range of methods that have often yielded contradictory results. Much of the controversy has focused on the placement of Dromiciops gliroides (Microbiotheria). Studies either support a sister-taxon relationship to a monophyletic Australasian clade or a nested position within the Australasian radiation. Familial relationships within the Diprotodontia have also proved difficult to resolve. Here, we examine higher-level marsupial relationships using a nuclear multigene molecular data set representing all living orders. Protein-coding portions of ApoB, BRCA1, IRBP, Rag1, and vWF were analyzed using maximum parsimony, maximum likelihood, and Bayesian methods. Two different Bayesian relaxed molecular clock methods were employed to construct a timescale for marsupial evolution and estimate the unrepresented basal branch length (UBBL). Maximum likelihood and Bayesian results suggest that the root of the marsupial tree is between Didelphimorphia and all other marsupials. All methods provide strong support for the monophyly of Australidelphia. Within Australidelphia, Dromiciops is the sister-taxon to a monophyletic Australasian clade. -
Corroboree Ground and Aboriginal Cultural Area, Queanbeyan River
November 2017 ACT Heritage Council BACKGROUND INFORMATION Corroboree Ground and Aboriginal Cultural Area, Queanbeyan River Block 700 MAJURA Part Blocks 662, 663, 699, 680, 701, 702, 703, 704 MAJURA Part Blocks 2002, 2091, 2117 JERRABOMBERRA OAKS ESTATE Block 22, Section 2; Block 13, Section 3; Block 4, Section 13; Block 6, Section 13, Block 5, Section 14; Part Block 15, Section 2; Part Block 19, Section 2; Part Block 20, Section 2; Part Block 21, Section 2; Part Block 5, Section 13; Part Block 1, Section 14; Part Block 4, Section 14; Part Block 1, Section 17 At its meeting of 16 November 2017 the ACT Heritage Council decided that the Corroboree Ground and Aboriginal Cultural Area, Queanbeyan River was eligible for registration. The information contained in this report was considered by the ACT Heritage Council in assessing the nomination for the Corroboree Ground and Aboriginal Cultural Area, Queanbeyan River against the heritage significance criteria outlined in s 10 of the Heritage Act 2004. HISTORY The Ngunnawal people are traditionally affiliated with the lands within the Canberra region. In this citation, ‘Aboriginal community’ refers to the Ngunnawal people and other Aboriginal groups within the ACT who draw significance from the place. Whilst the term ‘Aboriginal community’ acknowledges these groups in the ACT, it is recognised that their traditional territories extend outside contemporary borders. These places attest to a rich history of Aboriginal connection to the area. Traditional Aboriginal society in Canberra during the nineteenth century suffered from dramatic depopulation and alienation from traditional land based resources, although some important social institutions like intertribal gatherings and corroborees were retained to a degree at least until the 1860s. -
Vegetation Benchmarks Rainforest and Related Scrub
Vegetation Benchmarks Rainforest and related scrub Eucryphia lucida Vegetation Condition Benchmarks version 1 Rainforest and Related Scrub RPW Athrotaxis cupressoides open woodland: Sphagnum peatland facies Community Description: Athrotaxis cupressoides (5–8 m) forms small woodland patches or appears as copses and scattered small trees. On the Central Plateau (and other dolerite areas such as Mount Field), broad poorly– drained valleys and small glacial depressions may contain scattered A. cupressoides trees and copses over Sphagnum cristatum bogs. In the treeless gaps, Sphagnum cristatum is usually overgrown by a combination of any of Richea scoparia, R. gunnii, Baloskion australe, Epacris gunnii and Gleichenia alpina. This is one of three benchmarks available for assessing the condition of RPW. This is the appropriate benchmark to use in assessing the condition of the Sphagnum facies of the listed Athrotaxis cupressoides open woodland community (Schedule 3A, Nature Conservation Act 2002). Benchmarks: Length Component Cover % Height (m) DBH (cm) #/ha (m)/0.1 ha Canopy 10% - - - Large Trees - 6 20 5 Organic Litter 10% - Logs ≥ 10 - 2 Large Logs ≥ 10 Recruitment Continuous Understorey Life Forms LF code # Spp Cover % Immature tree IT 1 1 Medium shrub/small shrub S 3 30 Medium sedge/rush/sagg/lily MSR 2 10 Ground fern GF 1 1 Mosses and Lichens ML 1 70 Total 5 8 Last reviewed – 2 November 2016 Tasmanian Vegetation Monitoring and Mapping Program Department of Primary Industries, Parks, Water and Environment http://www.dpipwe.tas.gov.au/tasveg RPW Athrotaxis cupressoides open woodland: Sphagnum facies Species lists: Canopy Tree Species Common Name Notes Athrotaxis cupressoides pencil pine Present as a sparse canopy Typical Understorey Species * Common Name LF Code Epacris gunnii coral heath S Richea scoparia scoparia S Richea gunnii bog candleheath S Astelia alpina pineapple grass MSR Baloskion australe southern cordrush MSR Gleichenia alpina dwarf coralfern GF Sphagnum cristatum sphagnum ML *This list is provided as a guide only. -
Edition 2 from Forest to Fjaeldmark the Vegetation Communities Highland Treeless Vegetation
Edition 2 From Forest to Fjaeldmark The Vegetation Communities Highland treeless vegetation Richea scoparia Edition 2 From Forest to Fjaeldmark 1 Highland treeless vegetation Community (Code) Page Alpine coniferous heathland (HCH) 4 Cushion moorland (HCM) 6 Eastern alpine heathland (HHE) 8 Eastern alpine sedgeland (HSE) 10 Eastern alpine vegetation (undifferentiated) (HUE) 12 Western alpine heathland (HHW) 13 Western alpine sedgeland/herbland (HSW) 15 General description Rainforest and related scrub, Dry eucalypt forest and woodland, Scrub, heathland and coastal complexes. Highland treeless vegetation communities occur Likewise, some non-forest communities with wide within the alpine zone where the growth of trees is environmental amplitudes, such as wetlands, may be impeded by climatic factors. The altitude above found in alpine areas. which trees cannot survive varies between approximately 700 m in the south-west to over The boundaries between alpine vegetation communities are usually well defined, but 1 400 m in the north-east highlands; its exact location depends on a number of factors. In many communities may occur in a tight mosaic. In these parts of Tasmania the boundary is not well defined. situations, mapping community boundaries at Sometimes tree lines are inverted due to exposure 1:25 000 may not be feasible. This is particularly the or frost hollows. problem in the eastern highlands; the class Eastern alpine vegetation (undifferentiated) (HUE) is used in There are seven specific highland heathland, those areas where remote sensing does not provide sedgeland and moorland mapping communities, sufficient resolution. including one undifferentiated class. Other highland treeless vegetation such as grasslands, herbfields, A minor revision in 2017 added information on the grassy sedgelands and wetlands are described in occurrence of peatland pool complexes, and other sections. -
A Species-Level Phylogenetic Supertree of Marsupials
J. Zool., Lond. (2004) 264, 11–31 C 2004 The Zoological Society of London Printed in the United Kingdom DOI:10.1017/S0952836904005539 A species-level phylogenetic supertree of marsupials Marcel Cardillo1,2*, Olaf R. P. Bininda-Emonds3, Elizabeth Boakes1,2 and Andy Purvis1 1 Department of Biological Sciences, Imperial College London, Silwood Park, Ascot SL5 7PY, U.K. 2 Institute of Zoology, Zoological Society of London, Regent’s Park, London NW1 4RY, U.K. 3 Lehrstuhl fur¨ Tierzucht, Technical University of Munich, Alte Akademie 12, 85354 Freising-Weihenstephan, Germany (Accepted 26 January 2004) Abstract Comparative studies require information on phylogenetic relationships, but complete species-level phylogenetic trees of large clades are difficult to produce. One solution is to combine algorithmically many small trees into a single, larger supertree. Here we present a virtually complete, species-level phylogeny of the marsupials (Mammalia: Metatheria), built by combining 158 phylogenetic estimates published since 1980, using matrix representation with parsimony. The supertree is well resolved overall (73.7%), although resolution varies across the tree, indicating variation both in the amount of phylogenetic information available for different taxa, and the degree of conflict among phylogenetic estimates. In particular, the supertree shows poor resolution within the American marsupial taxa, reflecting a relative lack of systematic effort compared to the Australasian taxa. There are also important differences in supertrees based on source phylogenies published before 1995 and those published more recently. The supertree can be viewed as a meta-analysis of marsupial phylogenetic studies, and should be useful as a framework for phylogenetically explicit comparative studies of marsupial evolution and ecology. -
Alpine National Park ‐ Around Heyfield, Licola and Dargo Visitor Guide
Alpine National Park ‐ around Heyfield, Licola and Dargo Visitor Guide The Alpine National Park stretches from central Gippsland all the way to the New South Wales border where it adjoins Kosciuszko National Park. In this south‐western section of the park you will find pleasant Snow Gum woodlands, sprawling mountain vistas, spectacular rivers and gorges, as well as rich cultural heritage ‐ from the rock scatters of the Gunaikurnai people on lofty vantage points, to grazier’s huts nestling in protected folds of the high country. Hut is a further 3 km though groves of snow gums. Built in 1940, the Getting there hut is an excellent example of bush architecture. Continue 1 km This area of the Alpine National Park is situated approximately 250‐ south east from the hut to the carpark. 320 km east of Melbourne. To get to Heyfield take Princes Highway to Traralgon, then take Traralgon‐Maffra Road. Alternatively, stay on First Falls and Moroka Gorge – 6km, 3 hours return Princes Highway to Sale and continue onto A1 to Dargo From Horseyard Flat the track crosses a footbridge over the Moroka The main access is from Licola via the Tamboritha Road, which leads River before meandering through snow gum woodland and crossing to the Howitt and Moroka Roads. wetlands on boardwalks. It follows the river downstream to the First Falls. A rock platform is an ideal viewing point to see the rushing Mountain roads are often unsealed, narrow and winding. Take care Moroka River plunging into a deep pool. as roads may be slippery and surface condition poor. -
The Western Ringtail Possum (Pseudocheirus Occidentalis)
A major road and an artificial waterway are barriers to the rapidly declining western ringtail possum, Pseudocheirus occidentalis Kaori Yokochi BSc. (Hons.) This thesis is presented for the degree of Doctor of Philosophy of The University of Western Australia School of Animal Biology Faculty of Science October 2015 Abstract Roads are known to pose negative impacts on wildlife by causing direct mortality, habitat destruction and habitat fragmentation. Other kinds of artificial linear structures, such as railways, powerline corridors and artificial waterways, have the potential to cause similar negative impacts. However, their impacts have been rarely studied, especially on arboreal species even though these animals are thought to be highly vulnerable to the effects of habitat fragmentation due to their fidelity to canopies. In this thesis, I studied the effects of a major road and an artificial waterway on movements and genetics of an endangered arboreal species, the western ringtail possum (Pseudocheirus occidentalis). Despite their endangered status and recent dramatic decline, not a lot is known about this species mainly because of the difficulties in capturing them. Using a specially designed dart gun, I captured and radio tracked possums over three consecutive years to study their movement and survival along Caves Road and an artificial waterway near Busselton, Western Australia. I studied the home ranges, dispersal pattern, genetic diversity and survival, and performed population viability analyses on a population with one of the highest known densities of P. occidentalis. I also carried out simulations to investigate the consequences of removing the main causes of mortality in radio collared adults, fox predation and road mortality, in order to identify effective management options. -
Exotic to Australia
Fact sheet Introductory statement Foot and mouth disease (FMD) is a highly contagious viral vesicular disease of cloven hoofed animals. It is a major issue in international trade in livestock and livestock products. Australia is free of the disease and it is vital that it remains so. The 2001 outbreak in the United Kingdom resulted in over 10 million cattle and sheep being slaughtered at a cost of over GBP 8 billion in order to eradicate the disease. This fact sheet summarises what is known about FMD and Australian native wildlife. WHA also manages an fact sheet that briefly summarises information on FMD and feral animals “Foot and Mouth Disease (General Information)”. Aetiology and natural hosts FMD is caused by an aphthovirus belonging to the family Picornaviridae. It is a single stranded non enveloped 25 nm RNA virus. There are seven serotypes: A, O, C, SAT 1, SAT 2, SAT 3, and Asia 1. All cloven hoofed animals are considered susceptible. Cases have also been reported in elephants, hedgehogs and some rodents. World distribution and occurrences in Australia FMD is endemic in Africa, the Middle East, Asia and parts of South America. The disease has almost been eradicated from Europe with the most recent cases occurring in the United Kingdom and Cyprus in 2007. FMD has not occurred in Australia for over 130 years, and then only in livestock. Minor outbreaks occurred in 1801, 1804, 1871 and 1872 (Geering et al 1995). However, a case was reported in an eastern grey kangaroo (Macropus giganteus) held in a zoo in India (Bhattacharya et al 2003).