Simpson-Strzelecki Dunefields the Simpson-Strzelecki Dunefields Bioregion
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Dusky Hopping Mouse
Threatened Species of the Northern Territory DUSKY HOPPING-MOUSE Notomys fuscus Conservation status Australia: Vulnerable Northern Territory: Endangered Photo: P. Canty Description as Ooldea in South Australia and east to the Victoria/New South Wales borders. The dusky hopping-mouse is characterized by its strong incisor teeth, long tail, large ears, The species has not been recorded in the dark eyes, and extremely lengthened and Northern Territory since 1939 when it was narrow hind feet, which have only four pads collected in sand dunes on Maryvale Station on the sole. The head-body length is 91-177 and on Andado Station. An earlier record is mm, tail length is 125-225 mm, and body from Charlotte Waters. weight is about 20-50 g. Coloration of the Conservation reserves where reported: upper parts varies from pale sandy brown to None. yellowish brown to ashy brown or greyish. The underparts of dusky hopping-mice are white. The fur is fine, close and soft. Long hairs near the tip of the tail give the effect of a brush. The dusky hopping-mouse has a well- developed glandular area on the underside of its neck or chest. Females have four nipples. Distribution The current distribution of the dusky hopping-mouse appears to be restricted to the eastern Lake Eyre Basin within the Known locations of the dusky hopping-mouse Simpson-Strzelecki Dunefields bioregion in (ο = pre 1970). South Australia and Queensland. An intensive survey in the 1990s located populations at Ecology eight locations in the Strzelecki Desert and adjacent Cobbler Sandhills (South Australia) The dusky hopping-mouse occupies a variety and in south-west Queensland (Moseby et al. -
Broken Hill Complex
Broken Hill Complex Bioregion resources Photo Mulyangarie, DEH Broken Hill Complex The Broken Hill Complex bioregion is located in western New South Wales and eastern South Australia, spanning the NSW-SA border. It includes all of the Barrier Ranges and covers a huge area of nearly 5.7 million hectares with approximately 33% falling in South Australia! It has an arid climate with dry hot summers and mild winters. The average rainfall is 222mm per year, with slightly more rainfall occurring in summer. The bioregion is rich with Aboriginal cultural history, with numerous archaeological sites of significance. Biodiversity and habitat The bioregion consists of low ranges, and gently rounded hills and depressions. The main vegetation types are chenopod and samphire shrublands; casuarina forests and woodlands and acacia shrublands. Threatened animal species include the Yellow-footed Rock- wallaby and Australian Bustard. Grazing, mining and wood collection for over 100 years has led to a decline in understory plant species and cover, affecting ground nesting birds and ground feeding insectivores. 2 | Broken Hill Complex Photo by Francisco Facelli Broken Hill Complex Threats Threats to the Broken Hill Complex bioregion and its dependent species include: For Further information • erosion and degradation caused by overgrazing by sheep, To get involved or for more information please cattle, goats, rabbits and macropods phone your nearest Natural Resources Centre or • competition and predation by feral animals such as rabbits, visit www.naturalresources.sa.gov.au -
Phylogenetic Structure of Vertebrate Communities Across the Australian
Journal of Biogeography (J. Biogeogr.) (2013) 40, 1059–1070 ORIGINAL Phylogenetic structure of vertebrate ARTICLE communities across the Australian arid zone Hayley C. Lanier*, Danielle L. Edwards and L. Lacey Knowles Department of Ecology and Evolutionary ABSTRACT Biology, Museum of Zoology, University of Aim To understand the relative importance of ecological and historical factors Michigan, Ann Arbor, MI 48109-1079, USA in structuring terrestrial vertebrate assemblages across the Australian arid zone, and to contrast patterns of community phylogenetic structure at a continental scale. Location Australia. Methods We present evidence from six lineages of terrestrial vertebrates (five lizard clades and one clade of marsupial mice) that have diversified in arid and semi-arid Australia across 37 biogeographical regions. Measures of within-line- age community phylogenetic structure and species turnover were computed to examine how patterns differ across the continent and between taxonomic groups. These results were examined in relation to climatic and historical fac- tors, which are thought to play a role in community phylogenetic structure. Analyses using a novel sliding-window approach confirm the generality of pro- cesses structuring the assemblages of the Australian arid zone at different spa- tial scales. Results Phylogenetic structure differed greatly across taxonomic groups. Although these lineages have radiated within the same biome – the Australian arid zone – they exhibit markedly different community structure at the regio- nal and local levels. Neither current climatic factors nor historical habitat sta- bility resulted in a uniform response across communities. Rather, historical and biogeographical aspects of community composition (i.e. local lineage per- sistence and diversification histories) appeared to be more important in explaining the variation in phylogenetic structure. -
Arsbc-2008-Williams2 Paper.Pdf
BIOGEOGRAPHY AND BIODIVERSITY OF BIOLOGICAL SOIL CRUSTS ACROSS QUEENSLAND Wendy J. Williams1, Burkhard Büdel2, *Colin Driscoll3 1The University of Queensland, Gatton, Queensland, 4343, Australia; 2Department of Biology, University of Kaiserslautern, Kaiserslautern, Germany 3The University of Newcastle, NSW, 2308, Australia Email: [email protected] ABSTRACT Recent field research has established that biological soil crust communities (cyanobacteria, lichens, liverworts and mosses) are widespread across the rangelands of Queensland. Our survey has covered many national parks and reserves or private properties where necessary, to take in changes in rainfall gradients, vegetation communities and soils. We document for the first time, well-established and extensive cyanobacteria-dominated soil crusts occurring throughout much of the gulf-savannah. An ecologically important biological crust system was found across a fragile dune and flood plain near Skull Hole, Bladensburg NP. Other noteworthy biological crusts with significant biodiversity and cover were found in the jump-ups Diamantina NP; Spinifex ridges, Minerva Hills NP; Grey Range (west of Thargomindah); Sturt Stony Desert (Arrabury region); Stony plains (Coorabulka, Windorah Rd) and Arcadia Valley (Old Towrie). There were considerable and diverse cyanobacteria-dominated soil crusts found south-east of Cunnamulla (Glencoban), Currawinya NP, Bindegolly NP, Boodjamulla NP (Lawn Hill Gorge and Riversleigh sections), sand dunes (various sites, far western QLD) and in the estuarine sand-flats around Karumba. Across western QLD several mesas were surveyed. There were also good representations of hypolithic (cyanobacteria - under quartz, Boulia-Djarra Rd), epilithic (cyanobacteria and lichens) and endolithic (cyanobacteria) communities on various granite or sandstone rocky outcrops. Early results clearly show these biogenic soil crusts are unique in their biodiversity, structure and function. -
Blueys in the Bush: Short Notes on the Distribution and Habitat Of
Blueys in the bush: Short notes on the distribution and habitat of Tiliqua and Cyclodomorphus in New South Wales, Australia. Steven Sass1,2 1nghenvironmental, PO Box 470, Bega NSW. e [email protected] 2Ecology and Biodiversity Group, Institute for Land, Water and Society, Charles Sturt University, Thurgoona NSW. The ‘blue tongue’ lizards are regarded as one of the most iconic reptile species in Australia (Koenig et al., 2001). The Tiliqua are a familiar genus whose members are often encountered in suburbia and along country roads, while the Cyclodomorphus are shy and secretive and rarely observed. ‘Blue tongues’ can be found in almost every part of the continent, with the state of New South Wales being no exception. This paper provides some short notes on the distribution and habitat of Tiliqua and Cyclodomorphus that are known to occur within New South Wales. Tiliqua Of the six species of Tiliqua that occur in Australia, five of these are known to occur in NSW. The Pygmy Blue-tongue Tiliqua adelaidensis occurs in South Australia (Armstrong and Reid, 1992). A sub-species of the Eastern Blue-tongue, the Northern Blue-tongue Tiliqua scincoides intermedia, is found across northern Queensland, Northern Territory and Western Australia (Wilson and Swan, 2008). Tiliqua multifasciata The Centralian Blue tongue is known only to occur in NSW within Sturt National Park (Swan et al., 2004; DECC, 2008a) (Figure 1). The species has been recorded within spinifex grasslands in sandy areas (Swan et al., 2004) (Plate 1). In other parts of its range outside of NSW, the species has also been found where spinifex occurs on stony ground (Fyfe, 1983; Wilson and Swan, 2008). -
BIODIVERSITY Native Vegetation
BIODIVERSITY Native Vegetation Trends • Vegetation Extent: STABLE • Vegetation Condition: UNKNOWN OVERALL but IMPROVED slightly for Kingoonya District in the Pastoral region ‘Lose no species’ is a statement of • Area of land under Protected Status: aspiration. Species decline and become INCREASED 1% since 2003, but slowing extinct naturally. This aspiration reflects compared to last SoE Report the foresight, mindset and commitment needed by all South Australians if we are • Indigenous Revegetation activity: to prevent further loss of our known native DECREASING species due to human impacts, and if we are to conserve our biodiversity for future generations. Goals T3.1 Lose no species: lose no known native Native Vegetation species as a result of human impacts. and a sustainable South Australian Strategic Plan 2007 South Australia T3.2 Land biodiversity: by 2010 have five To achieve a sustainable future for well-established biodiversity corridors South Australia one of the key targets aimed at maximising ecological outcomes for sustainability in the South Australian particularly in the face of climate change. Strategic Plan is to Lose No Species. Native vegetation is an integral South Australian Strategic Plan 2007 component of our natural environment. 162 STATE OF THE ENVIRONMENT REPORT 2008 Native Vegetation As indigenous species provide habitat the importance of native vegetation in for animals native vegetation is maintaining a sustainable environment fundamental to sustainability. for humans. The economic value of these ecosystem services is identified Natural landscapes and the native as pertinent to ensure that their value is vegetation they contain are important included in economic considerations. components of the Australian identity. -
Novel Application of Species Richness Estimators to Predict the Host Range of Parasites
International Journal for Parasitology xxx (2016) xxx–xxx Contents lists available at ScienceDirect International Journal for Parasitology journal homepage: www.elsevier.com/locate/ijpara Novel application of species richness estimators to predict the host range of parasites David M. Watson a,, Kirsty V. Milner b, Andrea Leigh b a School of Environmental Science, Charles Sturt University, Albury 2640, Australia b School of Life Science, University of Technology Sydney, 15 Broadway, Ultimo 2007, Australia article info abstract Article history: Host range is a critical life history trait of parasites, influencing prevalence, virulence and ultimately Received 16 June 2016 determining their distributional extent. Current approaches to measure host range are sensitive to sam- Received in revised form 30 September pling effort, the number of known hosts increasing with more records. Here, we develop a novel applica- 2016 tion of results-based stopping rules to determine how many hosts should be sampled to yield stable Accepted 5 October 2016 estimates of the number of primary hosts within regions, then use species richness estimation to predict Available online xxxx host ranges of parasites across their distributional ranges. We selected three mistletoe species (hemipar- asitic plants in the Loranthaceae) to evaluate our approach: a strict host specialist (Amyema lucasii, Keywords: dependent on a single host species), an intermediate species (Amyema quandang, dependent on hosts Host range Host specificity in one genus) and a generalist (Lysiana -
Australia's 89 Bioregions (PDF
ARC Arnhem Coast ARP Arnhem Plateau TIW AUA Australian Alps AVW Avon Wheatbelt BBN Brigalow Belt North DARWIN ! ARC BBS Brigalow Belt South BEL Ben Lomond ITI DAC PCK ARP BHC Broken Hill Complex CEA BRT Burt Plain CAR Carnarvon ARC CEA Central Arnhem DAB CYP CEK Central Kimberley CER Central Ranges NOK VIB CHC Channel Country CMC Central Mackay Coast GUC COO Coolgardie GFU STU COP Cobar Peneplain COS Coral Sea CEK CYP Cape York Peninsula OVP DAB Daly Basin DAC Darwin Coastal DAL WET GUP EIU DAL Dampierland DEU Desert Uplands DMR Davenport Murchison Ranges COS DRP Darling Riverine Plains DMR TAN EIU Einasleigh Uplands MII ESP Esperance Plains GSD EYB Eyre Yorke Block FIN Finke FLB Flinders Lofty Block CMC FUR Furneaux BRT GAS Gascoyne PIL DEU GAW Gawler MGD BBN GES Geraldton Sandplains GFU Gulf Fall and Uplands MAC GID Gibson Desert LSD GID GSD Great Sandy Desert GUC Gulf Coastal GUP Gulf Plains CAR GAS CER FIN CHC GVD Great Victoria Desert HAM Hampton ITI Indian Tropical Islands SSD JAF Jarrah Forest KAN Kanmantoo KIN King GVD LSD Little Sandy Desert STP BBS MUR SEQ MAC MacDonnell Ranges MUL MAL Mallee ! BRISBANE MDD Murray Darling Depression YAL MGD GES Mitchell Grass Downs STP MII Mount Isa Inlier MUL Mulga Lands NUL MUR Murchison NAN Nandewar GAW NET NCP Naracoorte Coastal Plain SWA COO NAN NET New England Tablelands AVW HAM BHC DRP NNC NSW North Coast FLB NOK Northern Kimberley ! COP PERTH NSS NSW South Western Slopes MDD NNC NUL Nullarbor MAL EYB OVP Ord Victoria Plain PCK Pine Creek JAF ESP SYB PSI PIL Pilbara ADELAIDE ! ! PSI Pacific -
Phylogenetic Structure of Vertebrate Communities Across the Australian
Journal of Biogeography (J. Biogeogr.) (2013) 40, 1059–1070 ORIGINAL Phylogenetic structure of vertebrate ARTICLE communities across the Australian arid zone Hayley C. Lanier*, Danielle L. Edwards and L. Lacey Knowles Department of Ecology and Evolutionary ABSTRACT Biology, Museum of Zoology, University of Aim To understand the relative importance of ecological and historical factors Michigan, Ann Arbor, MI 48109-1079, USA in structuring terrestrial vertebrate assemblages across the Australian arid zone, and to contrast patterns of community phylogenetic structure at a continental scale. Location Australia. Methods We present evidence from six lineages of terrestrial vertebrates (five lizard clades and one clade of marsupial mice) that have diversified in arid and semi-arid Australia across 37 biogeographical regions. Measures of within-line- age community phylogenetic structure and species turnover were computed to examine how patterns differ across the continent and between taxonomic groups. These results were examined in relation to climatic and historical fac- tors, which are thought to play a role in community phylogenetic structure. Analyses using a novel sliding-window approach confirm the generality of pro- cesses structuring the assemblages of the Australian arid zone at different spa- tial scales. Results Phylogenetic structure differed greatly across taxonomic groups. Although these lineages have radiated within the same biome – the Australian arid zone – they exhibit markedly different community structure at the regio- nal and local levels. Neither current climatic factors nor historical habitat sta- bility resulted in a uniform response across communities. Rather, historical and biogeographical aspects of community composition (i.e. local lineage per- sistence and diversification histories) appeared to be more important in explaining the variation in phylogenetic structure. -
Human Refugia in Australia During the Last Glacial Maximum and Terminal Pleistocene: a Geospatial Analysis of the 25-12 Ka Australian Archaeological Record
ResearchOnline@JCU This is the author-created version of the following work: Williams, Alan N., Ulm, Sean, Cook, Andrew R., Langley, Michelle C., and Collard, Mark (2013) Human refugia in Australia during the Last Glacial Maximum and Terminal Pleistocene: a geospatial analysis of the 25-12 ka Australian archaeological record. Journal of Archaeological Science, 40 (12) pp. 4612-4625. Access to this file is available from: https://researchonline.jcu.edu.au/28670/ Published Version: (C) Elsevier Accepted Version: CC BY-NC-ND Please refer to the original source for the final version of this work: https://doi.org/10.1016/j.jas.2013.06.015 Accepted Manuscript Human refugia in Australia during the Last Glacial Maximum and Terminal Pleistocene: A geospatial analysis of the 25-12ka Australian archaeological record Alan N. Williams, Sean Ulm, Andrew R. Cook, Michelle C. Langley, Mark Collard PII: S0305-4403(13)00221-5 DOI: 10.1016/j.jas.2013.06.015 Reference: YJASC 3730 To appear in: Journal of Archaeological Science Received Date: 13 February 2013 Revised Date: 3 June 2013 Accepted Date: 17 June 2013 Please cite this article as: Williams, A.N., Ulm, S., Cook, A.R., Langley, M.C., Collard, M., Human refugia in Australia during the Last Glacial Maximum and Terminal Pleistocene: A geospatial analysis of the 25-12ka Australian archaeological record, Journal of Archaeological Science (2013), doi: 10.1016/ j.jas.2013.06.015. This is a PDF file of an unedited manuscript that has been accepted for publication. As a service to our customers we are providing this early version of the manuscript. -
Protected Areas & Public Land Management
1 Protected areas & public land management Protected Areas Last updated: January 2013 These Fact Sheets are a guide only and are no substitute for legal advice. To request free initial legal advice on an environmental or planning law issue, please visit our website1 or call our Environmental Law Advice Line. Your request will be allocated to one of our solicitors who will call you back, usually within a few days of your call. Sydney: 02 9262 6989 Northern Rivers: 1800 626 239 Rest of NSW: 1800 626 239 Overview Australia and NSW are facing a serious decline in biodiversity.2 It is therefore necessary to set aside sanctuaries or areas in which native species, vegetation and ecosystems can be permanently protected. Such areas are known as protected areas. There are many different types of protected areas in NSW, ranging from World Heritage sites to nature reserves. Similarly, aquatic habitats are protected by marine parks and aquatic reserves. The level of legal protection varies for each type of protected area. In NSW, the main legislation under which protected areas are created and managed is the National Parks and Wildlife Act 1974 (NSW). These are managed by the NSW National Parks and Wildlife Service. In NSW, around 7.1 million hectares, or around 8.8% of the State, is in a protected area of some sort.3 Areas of land can also be protected under the main Commonwealth environmental law, the Environment Protection and Biodiversity Conservation Act 1 http://www.edonsw.org.au/legal_advice 2 NSW State of the Environment Report 2012, Chapter 5 Biodiversity. -
Broken Hill Complex Bioregion Lies in the Far West of NSW, Spanning the the Broken Hill Complex Bioregion Generally Has a Hot, Dry Climate and Lies NSW-SA Border
41 CHAPTER 4 The Broken Hill Complex Bioregion Hill Broken Complex 1. Location 2. Climate The Broken Hill Complex Bioregion lies in the far west of NSW, spanning the The Broken Hill Complex Bioregion generally has a hot, dry climate and lies NSW-SA border. Across these two states the bioregion has an area of within the NSW arid zone.The bioregion is one of four bioregions, all in the far 5,691,042 ha, with 3,811,697 ha or 66.98% falling in NSW. The bioregion west of the state, that are dominated by a hot, persistently dry desert climate occupies about 4.8% of NSW and is bounded by the Murray-Darling (Stern et al. 2000). Patches of semi-arid climate in the centre of the bioregion Depression and Darling Riverine Plains bioregions in the south, and the complement the arid climate prevalent in most of the bioregion. Simpson-Strzelecki Dunefields and Mulga Lands bioregions in the north and east respectively. In SA it is bounded by another four bioregions. 3. Topography The biggest city in the bioregion is Broken Hill with a population of about 20,096 (2001 Census – Australian Bureau of Statistics). There are few other The Broken Hill Complex Bioregion in western NSW is geologically unique in towns in the bioregion. Nearby Silverton was once the main township in the the state. The western half is composed of ancient basement rocks of the 1880s at the peak of mining activity, but it was soon overshadowed by the Adelaide Fold Belt, and the eastern half is the edge of the much younger rocks faster-growing Broken Hill (HO and DUAP 1996).