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Conservation Management Zones of AustraliaSouth Eastern Australia Mallee Woodlands
Prepared by the Department of the Environment
ACKNOWLEDGEMENTS
This project and associated products are the result of a collaboration between the Biodiversity Conservation Division and the Environmental Resources Information Network (ERIN). Invaluable input, advice and support were provided by staff and leading researchers from across the Department of the Environment (DotE), Department of Agriculture (DoA), the Commonwealth Scientific and Industrial Research Organisation (CSIRO), and the academic community. We would particularly like to thank staff within the Wildlife, Heritage and Marine Division, Parks Australia and the Environment Assessment and Compliance Division of DotE, Nyree Stenekes and Robert Kancans (ABARES), Sue McIntyre (CSIRO), Richard Hobbs (University of Western Australia), Michael Hutchinson (ANU); David Lindenmayer and Emma Burns (ANU); and Gilly Llewellyn, Martin Taylor and other staff from the World Wildlife Fund for their generosity and advice.
Special thanks to CSIRO staff Kristen Williams and Simon Ferrier whose modelling of biodiversity patterns enabled identification of the Conservation Management Zones of Australia.
© Commonwealth of Australia, 2015.
The Conservation Management Zones of Australia profile is licensed by the Commonwealth of Australia for use under a Creative Commons By Attribution 3.0 Australia licence with the exception of the Coat of Arms of the Commonwealth of Australia, the logo of the agency responsible for publishing the report, content supplied by third parties, and any images depicting people.
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ContentsAcknowledgement of Traditional Owners and Country.................................................................4
Introduction....................................................................................................................................4
Zone at a glance............................................................................................................................5
Population characteristics............................................................................................................10
Employment, volunteering and incomes......................................................................................15
Agriculture, Natural Resource Management practices and sources of NRM advice...................18
Land tenure, land use, Native Title and Local Government Areas..............................................21
Zone vegetation characteristics...................................................................................................24
Ramsar and Nationally Important Wetlands................................................................................25
World and National Heritage.......................................................................................................27
Major National Reserve System properties.................................................................................27
EPBC Act (1999) threatened ecological communities.................................................................28
EPBC Act (1999) threatened species..........................................................................................29
EPBC Act (1999) migratory species............................................................................................33
Threatened endemic species......................................................................................................35
Invasive species..........................................................................................................................37
Vegetation profiles and management recommendations............................................................40
Acknowledgement of Traditional Owners and CountryThe Australian Government acknowledges Australia’s Traditional Owners and pays respect to Elders past and present of our nation’s Aboriginal and Torres Strait Islander communities. We honour the deep spiritual, cultural and customary connections of Traditional Owners to the Australian landscape, including Australia’s waterways, land and sea country.
Introduction The 23 Conservation Management Zones of Australia are geographic areas, classified according to their ecological and threat characteristics. The zones are also aligned with the Interim Biogeographic Regionalisation of Australia.
The Conservation Management Zones provide a way of understanding Australia’s natural environment that will assist in long-term conservation planning and help the Australian Government to better design, deliver and report on Natural Resource Management (NRM) investments, including ensuring alignment of national NRM priorities with local action.
The Conservation Management Zones also provide a filter through which to make national environmental and socio-economic data more accessible and comprehensible, and a framework for gathering on-ground knowledge and expertise about the environment. This will improve information flow to the Australian Government about regional NRM requirements, best practice management, emerging NRM issues and knowledge gaps.
The Conservation Management Zones do not represent any change to existing administrative boundaries or governance structures, but aim to support the NRM and wider community to cooperatively manage environmental assets across boundaries, where they share common threats, ecological characteristics and stakeholders.
Each Conservation Management Zone profile contains a standard suite of nationally available ecological and socio-economic information. We hope that this information will enable Australians of all ages and backgrounds to engage with, understand and appreciate Australian landscapes, and support all Australians to manage our natural resources more effectively.
The profile information provides an indicative, high-level stock-take of the environmental and socio-economic landscape and it is not intended to be comprehensive. It should also be noted that, at present, the profiles contain only limited information on aquatic ecosystems, coastal assets and Indigenous land management practices. In future, consultation and comprehensive literature reviews will enable us to provide more complete information.
Zone at a glance
Source: Based on Australian Bureau of Statistics data
MAJOR CITIES AND TOWNS POPULATION
Berri 4,107
Kadina 4,461
Mildura 31,272
Murray Bridge 15,642
Port Lincoln 14,083
Port Pirie 13,850
Renmark 4,381
OTHER TOWNS POPULATION
Balaklava 1,828
Bamera 1,916
Bordertown 2,543
Ceduna 2,292
Clare 3,283
Kapunda 2,484
Loxton 3,783
Mannum 2,167
Merbein 1,926
Moonta 3,650
Red Cliffs 2,558
Wallaroo 3,158
Warracknabeal 2,338
NATURAL RESOURCE MANAGEMENT (NRM) REGIONSMurray Local Land Services (LLS) NSW
NATURAL RESOURCE MANAGEMENT (NRM) REGIONSRiverina LLS NSW
Western LLS NSW
Natural Resources (NR) Eyre Peninsula SA
NR Northern and Yorke SA
NR SA Arid Lands SA
NR SA Murray Darling SA
Mallee Catchment Management Authority (CMA) VIC
North Central CMA VIC
Wimmera CMA VIC
TOP FIVE AGRICULTURAL COMMODITIES VALUE (MILLIONS)
Cereals for grain $2,993
Fruit $1,088
Legumes for grain $402
Vegetables for consumption $390
Lamb $306
Total value of agricultural commodities (including other commodities not listed here) $6,485
CLIMATE CHARACTERISTICS*Mean annual temperature 16.5 Celsius
Mean Maximum of the Hottest Month 31.3 Celsius
Mean Minimum of the Coldest Month 4 Celsius
Mean Annual Rainfall 306.6 mm
Dominant rainfall season Winter
* The figures are interpolated 75-year means (1921 to 1995) representing the period prior to the onset of rapid climatic warming. Cited in: Williams KJ, Belbin L, Austin MP, Stein J, Ferrier S (2012) Which environmental variables should I use in my biodiversity model? International Journal of Geographic Information Sciences 26(11), 2009–2047. (Data derived from Australian Climate surfaces version 2.1 for the ANUCLIM-BIOCLIM package).
For future climate projections please refer to: http://www.climatechangeinaustralia.gov.au/
Source: Based on Australian Bureau of Statistics data
Source: Based on data from the National Native Title Register; Collaborative Australian Protected Area Database (CAPAD); National Vegetation Information System (NVIS); Species’ Profile and Threats Database (SPRAT).
Population characteristics
Population
Source: Based on Australian Bureau of Statistics data
LANGUAGES SPOKEN AT HOMEEnglish 79.45%
Other languages 16.16%
Not stated 4.27%
Source: Based on Australian Bureau of Statistics data
Education
Source: Based on Australian Bureau of Statistics data
Employment, volunteering and incomes
Employment
Source: Based on Australian Bureau of Statistics data
Volunteering
Income
Source: Based on Australian Bureau of Statistics data
Agriculture, Natural Resource Management practices and sources of NRM adviceAustralian farmers manage over 60% of the Australian continent and shoulder much of the burden of responsibility for maintaining and protecting Australia’s natural resource wealth. The information contained in this profile aims to assist the wider community, non-governmental organisations and government agencies to support Australia’s key environmental custodians.
Agricultural commodity values
Source: Based on Australian Bureau of Statistics data
Natural Resource Management practices and sources of NRM advice
* Data obtained from the Australian Bureau of Statistics (ABS) 2012 Land Management Practices Survey (LaMPS) 2012. LaMPS collected land practices information from approximately 50,000 farm businesses across Australia. The data has been aligned to Conservation Management Zones from ABS Statistical Area 2 units and Australian Agricultural Environment units. The % figures presented here are indicative only. For more information on LaMPS please refer to: http://www.abs.gov.au/ausstats/[email protected]/mf/4630.0
** The sample for the Drivers of Practice Change 2012 survey consisted of a random subsample of 1228 broadacre farm managers from the Australian Agricultural and Grazing Industries Survey (AAGIS) frame. The data has been aligned to Conservation Management Zones from ABS Statistical Area 2 units. For this reason, the figures presented here are indicative only.
^ This chart indicates the sources of advice utilised for native vegetation management from respondents who identified they sought advice.
For more information please refer to http://www.daff.gov.au/SiteCollectionDocuments/forestry/domestic-forestry/prep-for-future/drivers-
Land tenure, land use, Native Title and Local Government Areas
Source: Land tenure data based on Environmental Resources Information Network (ERIN) categorisation of Public Sector Mapping Authority (PSMA) State Tenure 2012; Land use mapping based on Australian Collaborative Land Use and Management Program (ACLUMP) 2012. For more information on Australian land use and management information and classification please refer to: http://www.daff.gov.au/ABARES/aclump/
INDIGENOUS LAND COUNCILS
New South Wales Aboriginal Land Council: www.alc.org.au
Barengi Gadjin Land Council: www.bglc.org.au
Native Title Services Victoria: http://www.ntsv.com.au
South Australian Native Title Services: http://www.nativetitlesa.org
NATIVE TITLE AND TRADITIONAL OWNERSTraditional Owners Registered Native Title Body Corporate Hectares % of zone
Adnyamathanha People Adnyamathanha Traditional Lands Association (Aboriginal Corporation) RNTBC
1,701,575 5.21
Wotjobaluk People Barengi Gadjin Land Council Aboriginal Corporation RNTBC 723,708 2.22
Adnyamathanha People Adnyamathanha Traditional Lands Association (Aboriginal Corporation) RNTBC
36,638 0.11
First peoples of the River Murray & Mallee Region
The River Murray and Mallee Aboriginal Corporation RNTBC 35,926 0.11
Adnyamathanha People Adnyamathanha Traditional Lands Association (Aboriginal Corporation) RNTBC
33,800 0.10
Gawler Ranges People Gawler Ranges Aboriginal Corporation RNTBC 6,433 0.02
Source: The Native Title Tribunal Register, October 2013. For more information please refer to: http://www.nntt.gov.au/Pages/Searchportal.aspx
LOCAL GOVERNMENT AREASBalranald Shire Council NSW
Bourke Shire Council NSW
Carrathool Shire Council NSW
Central Darling Shire Council NSW
Cobar Shire Council NSW
Lachlan Shire Council NSW
The Council Of The Shire Of Wakool NSW
Unincorporated Far West NSW
Wentworth Shire Council NSW
Alexandrina Council SA
City Of Port Lincoln SA
Clare And Gilbert Valleys Council SA
Coorong Dc SA
Dc Of The Copper Coast SA
Light Regional Council SA
Mid Murray Council SA
Northern Areas Council SA
Port Augusta City Council SA
Port Pirie Regional Council SA
Renmark Paringa Council SA
Southern Mallee Dc SA
LOCAL GOVERNMENT AREASTatiara Dc SA
The Barossa Council SA
The Berri Barmera Council SA
The Dc Of Barunga West SA
The Dc Of Ceduna SA
The Dc Of Cleve SA
The Dc Of Elliston SA
The Dc Of Franklin Harbour SA
The Dc Of Karoonda East Murray SA
The Dc Of Kimba SA
The Dc Of Lower Eyre Peninsula SA
The Dc Of Loxton Waikerie SA
The Dc Of Mallala SA
The Dc Of Mount Remarkable SA
The Dc Of Orroroo Carrieton SA
The Dc Of Peterborough SA
The Dc Of Streaky Bay SA
The Dc Of Tumby Bay SA
The Dc Of Yorke Peninsula SA
The Flinders Ranges Council SA
The Regional Council Of Goyder SA
The Rural City Of Murray Bridge SA
Uia Riverland SA
Wakefield Regional Council SA
Wudinna District Council SA
Buloke Shire VIC
Campaspe Shire VIC
Gannawarra Shire VIC
Hindmarsh Shire VIC
Loddon Shire VIC
Mildura Rural City VIC
Swan Hill Rural City VIC
West Wimmera Shire VIC
Yarriambiack Shire VIC
Zone vegetation characteristicsThe National Vegetation Information System (NVIS) framework is a nationally consistent vegetation classification system based on vegetation data collected by states and territories. It provides information on the extent and distribution of vegetation types across the Australian landscape.
Two products are used to provide the Zone Vegetation Characteristics graph. A modelled pre-European vegetation distribution (pre-1750), and extant (current extent) vegetation, which is based on contemporary vegetation mapping. The information presented here relates to Major Vegetation Subgroups (MVSs). There are 85 MVS types across Australia, describing the structure and floristic composition of dominant and secondary vegetation stratums (e.g. canopy and mid-storey species). Major Vegetation Subgroups only reflect the dominant vegetation type occurring in an area from a mix of vegetation types. Less-dominant vegetation groups which may also be present are therefore not represented.
It is important to note that the vegetation information is indicative only, as state and territory mapping in Australia is of variable resolution and scale. However, this data is the best available nationally consistent information on vegetation, and the dataset continues to evolve and increase in accuracy.
Analysing this information at Conservation Management Zone, rather than national level provides greater discrimination for decision makers, as clearance levels of vegetation types are not uniform across Australia. For example, eucalypt woodlands with a tussock grass understory is a vegetation type found across Australia. In the Brigalow Woodlands Conservation Management Zone, eucalypt open woodlands with a tussock grass understory originally covered approximately 36% of the zone, but today it only covers only 14.5 % of the zone (58.7% of this vegetation community has been cleared in the Brigalow). In the Northern Australia Tropical Savannah zone, this vegetation type originally occupied 19.6% of the zone. Today, it occupies approximately 19.4% of the zone (only 2.3% of this vegetation type has been cleared). It should be noted that this data only provides an indication of change in extent, and not vegetation condition.
For more information on the National Vegetation Information System (NVIS) please refer to: http://www.environment.gov.au/topics/science-and-research/databases-and-maps/national-vegetation-information-system
Ramsar and Nationally Important WetlandsRAMSAR WETLANDS JURISDICTION HECTARESRiverland SA 30,664
Lake Albacutya VIC 5,659
Banrock Station Wetland Complex SA 1,375
The Coorong, and Lakes Alexandrina and Albert Wetland SA 311
Kerang Wetlands – The Marshes VIC 16
For more information on Ramsar please refer to: http://www.environment.gov.au/topics/water/water-our-environment/wetlands/ramsar-convention-wetlands
NATIONALLY IMPORTANT WETLANDS JURISDICTION HECTARES CRITERIA
Darling Anabranch Lakes NSW 42,498 1, 2, 5
Tod River Wetland System SA 39,209 1, 2, 3
Upper Spencer Gulf SA 36,568 1, 3, 5, 6
Riverland Wetland Complex SA 34,447 1, 2, 3, 4, 6
Menindee Lakes NSW 29,110 4, 5, 1, 3
Wimmera River VIC 24,773 1, 2, 3, 4, 5, 6
Lake Tyrrell VIC 17,477 1, 2
Clinton SA 16,993 1, 3
Lindsay Island VIC 15,799 1, 2, 3
Lake Hindmarsh VIC 14,787 1, 2, 3, 6
Talyawalka Anabranch & Teryawynia Creek NSW 11,435 1, 4
Wallpolla Island VIC 9,708 1, 2, 3
Lake Albacutya VIC 5,982 1, 2, 3, 4
Streaky Bay SA 4,041 3, 5
Bunguluke Wetlands, Tyrrell Creek & Lalbert Creek Floodplain
VIC 3,965 1, 2
Franklin Harbour SA 3,830 1, 3, 6
Port Gawler & Buckland Park Lake SA 3,629 1, 3, 5, 6
Lake Newland SA 3,528 1, 3, 5
Barker Inlet & St Kilda SA 3,483 1, 2, 3, 5, 6
Davenport Creek SA 2,412 1, 3, 5, 6
Coffin Bay Coastal Wetland System SA 2,173 3, 5, 6
Lake Hamilton SA 1,956 1
Noora Evaporation Lakes SA 1,626 3
Wills Creek SA 1,529 1, 3
Banrock Swamp Wetland Complex SA 1,375 1, 2, 3
Tumby Bay SA 1,075 1, 3
Pike-Mundic Wetland Complex SA 949 1, 3, 6
Lake Wallawalla VIC 822 1, 3
Gurra Lakes Wetland Complex SA 807 3
Lowbidgee Floodplain NSW 806 1, 2, 3, 4, 5
Baird Bay SA 737 3
Sleaford Mere SA 700 1, 3
NATIONALLY IMPORTANT WETLANDS JURISDICTION HECTARES CRITERIA
Lake Lalbert VIC 686 1, 2, 6
Raak Plain VIC 658 1, 5
Loveday Swamps SA 529 1, 2, 3, 6
Loch Luna Wetland Complex SA 488 1, 2, 3, 6
Wargan Basins (Meridian Lakes) VIC 396 1, 2, 3
Point Labatt SA 393 3, 5
Stockyard Plain SA 387 3, 5
Cardross Lakes VIC 293 1, 3, 5
Spectacle Lakes SA 285 1, 2, 3
The Coorong, Lake Alexandrina & Lake Albert SA 265 1, 2, 3, 4, 5, 6
Pink Lakes VIC 256 1, 6
Lake Ranfurly VIC 219 3, 4
Lower Murray Swamps SA 187 1, 2, 3
Innes Salt Lakes SA 166 1
Swan Reach Wetland Complex SA 151 1, 2, 3
Big Swamp SA 142 1, 3
Native Hen Lagoon SA 117 1
Point Davenport SA 116 1, 3, 5
Lake Cowal/Wilbertroy Wetlands NSW 105 1, 2, 3
Pink Lake (Lochiel) VIC 80 1,
Irwin Flat SA 57 1, 3
Poocher & Mundulla Swamps SA 53 2, 6
Pillie Lake SA 37 1
Gum Flat SA 22 1
Murray Bridge Army Training Area Wetlands SA 20 3, 5
Marne River Mouth SA 19 1, 2, 3
Heywoods Lake VIC 15 6
Lake Bael Bael VIC 6 1, 2, 3
Nationally important wetlands are defined according to the following criteria:
1. It is a good example of a wetland type occurring within a biogeographic region in Australia.
2. It is a wetland which plays an important ecological or hydrological role in the natural functioning of a major wetland system/complex.
3. It is a wetland which is important as the habitat for animal taxa at a vulnerable stage in their life cycles, or provides a refuge when adverse conditions such as drought prevail.
4. The wetland supports 1% or more of the national populations of any native plant or animal taxa.
5. The wetland supports native plant or animal taxa or communities which are considered endangered or vulnerable at the national level.
6. The wetland is of outstanding historical or cultural significance.
Please note, the above are a subset of all the Nationally Important Wetlands found within the Zone. For more information on Nationally Important Wetlands please see: http://www.environment.gov.au/resource/directory-important-w etlands-australia-third-edition
World and National HeritageHERITAGE VALUES WORLD OR NATIONAL HERITAGE
TYPEJURISDICTION HECTARES % OF
ZONEWillandra Lakes Region World and National Heritage Natural,
CulturalNSW 239,184 0.73
Ediacara Fossil Site National Natural SA 169,061 0.52
The Adelaide Park Lands and City Layout
National Historic SA 200 0.00
Please refer to the Australian Heritage Database for detailed information on listing criteria for these heritage values: http://www.environment.gov.au/topics/heritage/publications-and-resources/australian-heritage-database
For more information on Australia’s world and national heritage please refer to: http://www.environment.gov.au/topics/heritage/about-australias-heritage
Major National Reserve System propertiesMAJOR NATIONAL RESERVE SYSTEM PROPERTIES
Name Property type IUCN category
Jurisdiction Hectares % of zone
Murray – Sunset National Park II VIC 665,530 2.04
Wyperfeld National Park II VIC 360,254 1.10
Ngarkat Conservation Park IA SA 239,836 0.73
Danggali Wilderness Protection Area IB SA 203,700 0.62
Big Desert Wilderness Park IB VIC 140,997 0.43
Sunset Wilderness Zone – Schedule 5, National Parks Act
IB VIC 127,914 0.39
Pinkawillinie Conservation Park VI SA 123,766 0.38
Mungo National Park II NSW 122,709 0.38
Yathong Nature Reserve IA NSW 108,393 0.33
Vulkathunha – Gammon Ranges
National Park II SA 106,898 0.33
Taylorville Station National ReserveSystem Program
IV SA 94,146 0.29
Flinders Ranges National Park II SA 93,839 0.29
Chowilla Regional Reserve VI SA 75,523 0.23
Nombinnie Nature Reserve IA NSW 71,041 0.22
Hincks Wilderness Protection Area IB SA 66,913 0.20
Scotia Sanctuary National ReserveSystem Program
IV NSW 64,695 0.20
Billiatt Wilderness Protection Area IB SA 59,255 0.18
Nantawarrina Indigenous Protected Area III SA 58,348 0.18
Mallee Cliffs National Park IA NSW 58,118 0.18
Unnamed (No.HA1196) Heritage Agreement III SA 54,331 0.17
Danggali Conservation Park IA SA 48,626 0.15
THE IUCN CATEGORIES ARE AS FOLLOWS:
Ia Strict Nature Reserve IUCN protected area management categories classify protected areas according to their management objectives. The categories are recognised by international bodies such as the United Nations and are utilised by many national governments, including the Australian Government, as the global standard for defining and recording protected areas.
Ib Wilderness Area
II National Park
III Natural Monument or Feature
IV Habitat/Species Management Area
V Protected Landscape/ Seascape
VI Protected area with sustainable use of natural resources
Please refer to the IUCN website for further explanation: http://www.iucn.org/about/work/programmes/gpap_home/gpap_quality/gpap_pacategories/
For more information on Australia’s National Reserve System please refer to: http://www.environment.gov.au/topics/land/national-reserve-system
Source: Collaborative Australian Protected Area Database 2012.
EPBC Act (1999) threatened ecological communitiesTHREATENED ECOLOGICAL COMMUNITIES
Name Listing status % of total distribution* % of zone**
Eyre Peninsula Blue Gum (Eucalyptus petiolaris) Woodland
Endangered 100 0.009
Iron-grass Natural Temperate Grassland of South Australia
Critically Endangered
98.19 0.421
Peppermint Box (Eucalyptus odorata) Grassy Woodland of South Australia
Critically Endangered
92.95 0.349
Buloke Woodlands of the Riverina and Murray-Darling Depression Bioregions
Endangered 76.01 0.048
Swamps of the Fleurieu Peninsula Critically Endangered
6.79 0.0003
Natural Grasslands of the Murray Valley Plains Critically Endangered
4.31 0.031
Grey Box (Eucalyptus microcarpa) Grassy Woodlands and Derived Native Grasslands of South-eastern Australia
Endangered 1.06 0.056
Seasonal Herbaceous Wetlands (Freshwater) of the Temperate Lowland Plains
Critically Endangered
0.5 0.001
The community of native species dependent on natural discharge of groundwater from the Great Artesian Basin
Endangered 0.4 0.014
White Box-Yellow Box-Blakely’s Red Gum Grassy Woodland and Derived Native Grassland
Critically Endangered
0.3 0.021
* % of the total national distribution describes the proportion of the total national distribution of the Threatened Ecological Community that is found within the zone.
** % of the total zone area describes the proportion of the zone that the Threatened Ecological Community is likely or known to occur in.
It should be noted that the identification of any given Threatened Ecological Community above does not imply that the Threatened Ecological Community (TEC) is found uniformly across the Conservation Management Zone. Rather, the % of the TEC’s total distribution (*) within the zone is an indication of its importance to that zone in terms of conservation efforts. The % of the zone (**) indicates how rare, or difficult the ecological community may be to find within the zone.
The threatened ecological communities above are listed under The Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act), which is the Australian Government’s principal environmental legislation. For more information, please refer to http://www.environment.gov.au/biodiversity/threatened/communities
EPBC Act (1999) threatened speciesTHREATENED MAMMALS
Common name Scientific name Status % of totaldistribution*
% of zone**
Southern Brown Bandicoot (Nuyts Archipelago) Isoodon obesulus nauticus Vulnerable 99.84 0.0035
Yellow-footed Rock-wallaby (SA and NSW) Petrogale xanthopus xanthopus Vulnerable 67.87 5.2393
Wopilkara, Greater Stick-nest Rat Leporillus conditor Vulnerable 35.69 0.0144
Sandhill Dunnart Sminthopsis psammophila Endangered 15.58 4.8284
Dusky Hopping-mouse, Wilkiniti Notomys fuscus Vulnerable 5.03 0.0074
Woylie Bettongia penicillata ogilbyi Endangered 2.21 0.0503
Koala (combined populations of Queensland, New South Wales and the Australian Capital Territory)
Phascolarctos cinereus (combined populations of QLD, NSW and the ACT)
Vulnerable 0.07 0.0885
Greater Bilby Macrotis lagotis Vulnerable 0.04 0.2242
South-eastern Long-eared Bat Nyctophilus corbeni Vulnerable May be present
May be present
Plains Rat, Palyoora Pseudomys australis Vulnerable May be present
May be present
Southern Brown Bandicoot (Eastern) Isoodon obesulus obesulus Endangered May be present
May be present
Australian Sea-lion Neophoca cinerea Vulnerable n/a n/a
Blue Whale Balaenoptera musculus Endangered n/a n/a
Humpback Whale Megaptera novaeangliae Vulnerable n/a n/a
Southern Right Whale Eubalaena australis Endangered n/a n/a
THREATENED BIRDS
Common name Scientific name Status % of totaldistribution*
% of zone**
Southern Emu-wren (Eyre Peninsula) Stipiturus malachurus parimeda Vulnerable 99.99 1.03
Black-eared Miner Manorina melanotis Endangered 99.96 5.56
Red-lored Whistler Pachycephala rufogularis Vulnerable 98.8 8.27
Mallee Emu-wren Stipiturus mallee Endangered 98.47 4.27
Regent Parrot (eastern) Polytelis anthopeplus monarchoides
Vulnerable 96.46 24.03
Western Whipbird (eastern) Psophodes nigrogularis leucogaster
Vulnerable 78.58 5.16
Malleefowl Leipoa ocellata Vulnerable 27.89 77.14
THREATENED BIRDS
Australian Fairy Tern Sternula nereis nereis Vulnerable 15.93 2.81
Thick-billed Grasswren Amytornis modestus Vulnerable 12.48 8.45
Plains-wanderer Pedionomus torquatus Vulnerable 9.91 2.16
Slender-billed Thornbill (western) Acanthiza iredalei iredalei Vulnerable 7.98 13.49
Australian Painted Snipe Rostratula australis Endangered 4 2.39
Australasian Bittern Botaurus poiciloptilus Endangered 3.38 3.84
Southern Emu-wren (Fleurieu Peninsula), Mount Lofty Southern Emu-wren
Stipiturus malachurus intermedius
Endangered 1.39 0.00
Spotted Quail-thrush (Mt Lofty Ranges) Cinclosoma punctatumanachoreta
Critically Endangered
1.23 0.00
Swift Parrot Lathamus discolor Endangered 0.94 0.52
Red-tailed Black-Cockatoo (south-eastern) Calyptorhynchus banksii graptogyne
Endangered 0.37 0.02
Orange-bellied Parrot Neophema chrysogaster Critically Endangered
0.29 0.06
Superb Parrot Polytelis swainsonii Vulnerable 0.07 0.03
Regent Honeyeater Anthochaera phrygia Endangered May be present
May be present
Southern Royal Albatross Diomedea epomophora epomophora
Vulnerable 0.01 0.12
Northern Royal Albatross Diomedea epomophora sanfordi Endangered 0.01 0.12
Shy Albatross, Tasmanian Shy Albatross Thalassarche cauta cauta Vulnerable 0.01 0.12
White-capped Albatross Thalassarche cauta steadi Vulnerable 0.01 0.12
Tristan Albatross Diomedea exulans exulans Endangered n/a n/a
Soft-plumaged Petrel Pterodroma mollis Vulnerable n/a n/a
Wandering Albatross Diomedea exulans (sensu lato) Vulnerable n/a n/a
Blue Petrel Halobaena caerulea Vulnerable n/a n/a
Southern Giant-Petrel Macronectes giganteus Endangered n/a n/a
Campbell Albatross Thalassarche melanophrisimpavida
Vulnerable n/a n/a
Northern Giant-Petrel Macronectes halli Vulnerable n/a n/a
Antipodean Albatross Diomedea exulans antipodensis Vulnerable n/a n/a
Black-browed Albatross Thalassarche melanophris Vulnerable n/a n/a
* % of total distribution describes the proportion of the total national distribution of the threatened species that is found within the zone.
** % of zone describes the proportion of the zone that the threatened species is likely or known to occur in.
The % of zone indicates how rare, or difficult the species may be to find within the zone.
THREATENED REPTILES
Common Name Scientific name Status % of totaldistribution*
% of zone**
Krefft’s Tiger Snake (Flinders Ranges) Notechis scutatus ater Vulnerable 100 0.21
Pygmy Blue-tongue Lizard, Adelaide Blue- Tiliqua adelaidensis Endangered 98.71 0.79
THREATENED REPTILES
tongue Lizard
Flinders Ranges Worm-lizard Aprasia pseudopulchella Vulnerable 96.72 5.48
Striped Legless Lizard Delma impar Vulnerable 0.62 0.12
Pink-tailed Worm-lizard, Pink-tailed Legless Lizard
Aprasia parapulchella Vulnerable 0.03 0.00
Green Turtle Chelonia mydas Vulnerable 0.01 0.16
Loggerhead Turtle Caretta caretta Endangered 0.01 0.16
Leatherback Turtle, Leathery Turtle, Luth Dermochelys coriacea Endangered 0.01 0.16
OTHER THREATENED FAUNA
Common name Scientific name Status % of totaldistribution*
% of zone**
Flinders Ranges Mogurnda, Flinders Ranges Purple-spotted Gudgeon
Mogurnda clivicola Vulnerable 100 0.06
Murray Hardyhead Craterocephalus fluviatilis Endangered 64 2.31
Growling Grass Frog, Southern Bell Frog, Green and Golden Frog, Warty Swamp Frog
Litoria raniformis Vulnerable 8.58 5.72
Golden Sun Moth Synemon plana Critically Endangered
5.41 0.02
Macquarie Perch Macquaria australasica Endangered May be present
May be present
Murray Cod Maccullochella peelii Vulnerable May be present
May be present
Great White Shark Carcharodon carcharias Vulnerable n/a n/a
School Shark, Eastern School Shark, Snapper Shark, Tope, Soupfin Shark
Galeorhinus galeus Conservation Dependent
n/a n/a
Southern Bluefin Tuna Thunnus maccoyii Conservation Dependent
n/a n/a
THREATENED FLORA
Common Name Scientific name Status % of totaldistribution*
% of zone**
Halbury Greenhood Pterostylis sp. Halbury(R.Bates 8425)
Endangered 100 0.38
Prickly Raspwort Haloragis eyreana Endangered 100 0.07
Spiny Everlasting, Spiny Daisy Acanthocladium dockeri Critically Endangered
100 0.08
Spalding Blown Grass, Spalding Blowngrass Lachnagrostis limitanea Endangered 100 0.04
Spiller’s Wattle Acacia spilleriana Endangered 100 0.10
Goldsack’s Leek-orchid Prasophyllum goldsackii Endangered 100 0.03
Tufted Bush-pea Pultenaea trichophylla Endangered 100 0.35
Ghost Spider-orchid Caladenia intuta Critically Endangered
100 0.01
Chalky Wattle Acacia cretacea Endangered 100 0.01
Silver Candles Pleuropappus phyllocalymmeus Vulnerable 99.95 0.16
THREATENED FLORA
Annual Stackhousia, Annual Candles Stackhousia annua Vulnerable 99.94 0.35
Woolcock’s Spider-orchid Caladenia woolcockiorum Vulnerable 99.93 0.09
West Coast Mintbush, Limestone Mintbush, Red Mintbush
Prostanthera calycina Vulnerable 99.91 0.98
White Rabbits, Flinders Ranges White Caladenia
Caladenia xantholeuca Endangered 99.87 0.08
Winter Spider-orchid Caladenia brumalis Vulnerable 99.86 0.94
Spidery Wattle, Balcanoona Wattle Acacia araneosa Vulnerable 99.18 0.15
Fat-leaved Wattle Acacia pinguifolia Endangered 97.31 0.74
Sturdy Leek-orchid Prasophyllum validum Vulnerable 95.9 0.14
Peep Hill Hop-bush Dodonaea subglandulifera Endangered 95.81 0.57
Lowan Phebalium Phebalium lowanense Vulnerable 95.8 1.43
Nodding Rufoushood Pterostylis sp. Eyre Peninsula (R.Bates 19474)
Vulnerable 94.35 0.31
Superb Groundsel Senecio megaglossus Vulnerable 92.73 0.73
Neat Wattle, Resin Wattle (SA) Acacia rhetinocarpa Vulnerable 87.08 1.14
Jumping-jack Wattle Acacia enterocarpa Endangered 86.99 2.27
Hale Dwarf Greenhood Pterostylis sp. Hale (R.Bates 21725)
Endangered 85.83 0.27
Menzel’s Wattle Acacia menzelii Vulnerable 85.31 2.51
Whibley Wattle Acacia whibleyana Endangered 80.22 0.03
Yellow Swainson-pea Swainsona pyrophila Vulnerable 80.18 23.08
Bayonet Spider-orchid, Clubbed Spider-orchid Caladenia gladiolata Endangered 79.32 0.32
None Frankenia plicata Endangered 76.54 5.07
Slender Bell-fruit, Camel Poison Codonocarpus pyramidalis Vulnerable 76.2 12.75
None Atriplex infrequens Vulnerable 74.91 0.02
Hairy-pod Wattle Acacia glandulicarpa Vulnerable 69.59 1.64
Silver Daisy-bush Olearia pannosa subsp. pannosa
Vulnerable 67.36 3.05
Greencomb Spider-orchid, Rigid Spider-orchid Caladenia tensa Endangered 66.12 21.49
Menindee Nightshade Solanum karsense Vulnerable 65.69 6.51
Pale Leek-orchid Prasophyllum pallidum Vulnerable 64.9 2.32
Moore’s Burr-daisy Calotis moorei Endangered 60.07 0.02
Bead Glasswort Tecticornia flabelliformis Vulnerable 54.95 0.17
Wimmera Spider-orchid Caladenia lowanensis Endangered 52.48 0.02
Coast Spider-orchid Caladenia conferta Endangered 50.63 0.01
* % of total distribution describes the proportion of the total national distribution of the threatened species that is found within the zone.
** % of zone describes the proportion of the zone that the threatened species is likely or known to occur in. The % of zone indicates how rare, or difficult the species may be to find within the zone.
The above species are listed under The Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act), the Australian Government’s principal environmental legislation.
Please note that the list of threatened flora species is not comprehensive. The flora listed here have a significant proportion of their total national distribution within the zone. For more information please refer to: http://www.environment.gov.au/biodiversity/threatened/species or the Species Profiles and Threats Database http://www.environment.gov.au/cgi-bin/sprat/public/sprat.pl
EPBC Act (1999) migratory speciesMIGRATORY BIRDS
Common name Scientific name
Antipodean Albatross Diomedea antipodensis
Bar-tailed Godwit Limosa lapponica
Black-browed Albatross Thalassarche melanophris
Black-tailed Godwit Limosa limosa
Broad-billed Sandpiper Limicola falcinellus
Campbell Albatross Thalassarche impavida
Caspian Tern Sterna caspia
Cattle Egret Ardea ibis
Common Greenshank,Greenshank
Tringa nebularia
Common Sandpiper Actitis hypoleucos
Curlew Sandpiper Calidris ferruginea
Double-banded Plover Charadrius bicinctus
Eastern Curlew Numenius madagascariensis
Flesh-footed Shearwater, Fleshy-footed Shearwater Puffinus carneipes
Fork-tailed Swift Apus pacificus
Great Egret,White Egret
Ardea alba
Great Knot Calidris tenuirostris
Greater Sand Plover, Large Sand Plover Charadrius leschenaultii
Grey Plover Pluvialis squatarola
Grey-tailed Tattler Heteroscelus brevipes
Latham’s Snipe,Japanese Snipe
Gallinago hardwickii
Lesser Sand Plover, Mongolian Plover Charadrius mongolus
Little Curlew, Little Whimbrel Numenius minutus
Little Tern Sterna albifrons
Malleefowl Leipoa ocellata
Marsh Sandpiper, Little Greenshank Tringa stagnatilis
Northern Giant-Petrel Macronectes halli
Northern RoyalAlbatross
Diomedea sanfordi
MIGRATORY BIRDS
Oriental Plover, Oriental Dotterel Charadrius veredus
Pacific Golden Plover Pluvialis fulva
Painted Snipe Rostratula benghalensis(sensu lato)
Rainbow Bee-eater Merops ornatus
Red Knot, Knot Calidris canutus
Red-necked Stint Calidris ruficollis
Red-tailed Black-Cockatoo (south-eastern) Calyptorhynchus banksii graptogyne
Regent Honeyeater Xanthomyza phrygia
Ruddy Turnstone Arenaria interpres
Rufous Fantail Rhipidura rufifrons
Sanderling Calidris alba
Satin Flycatcher Myiagra cyanoleuca
Sharp-tailed Sandpiper Calidris acuminata
Short-tailed Shearwater Puffinus tenuirostris
Shy Albatross, Tasmanian Shy Albatross Thalassarche cauta (sensu stricto)
Southern Giant-Petrel Macronectes giganteus
Southern Royal Albatross Diomedea epomophora (sensu stricto)
Terek Sandpiper Xenus cinereus
Tristan Albatross Diomedea dabbenena
Wandering Albatross Diomedea exulans(sensu lato)
Wedge-tailedShearwater
Puffinus pacificus
Whimbrel Numenius phaeopus
White-belliedSea-Eagle
Haliaeetus leucogaster
White-cappedAlbatross
Thalassarche steadi
White-throatedNeedletail
Hirundapus caudacutus
Wood Sandpiper Tringa glareola
OTHER MIGRATORY SPECIES
Common name Scientific name
Humpback Whale Megaptera novaeangliae
Southern Right Whale Eubalaena australis
Green Turtle Chelonia mydas
Loggerhead Turtle Caretta caretta
Leatherback Turtle, Leathery Turtle, Luth Dermochelys coriacea
Bryde’s Whale Balaenoptera edeni
Pygmy Right Whale Caperea marginata
OTHER MIGRATORY SPECIES
Dusky Dolphin Lagenorhynchus obscurus
Killer Whale, Orca Orcinus orca
Porbeagle, Mackerel Shark Lamna nasus
Blue Whale Balaenoptera musculus
Great White Shark Carcharodon carcharias
For more information please refer to: http://www.environment.gov.au/topics/biodiversity/migratory-species
Threatened endemic speciesTHREATENED ENDEMIC SPECIES
Taxonomic group
Scientific name Reservation status EPBC Act status IUCN status
Mammals Lagorchestes leporides Recorded in reserves Extinct Extinct
Molluscs Glyptorhagada euglypta Not recordedin reserves
n/a Vulnerable
Molluscs Glyptorhagada janaslini Recorded in reserves n/a Near Threatened
Molluscs Glyptorhagada silveri Not recordedin reserves
n/a Endangered
Molluscs Glyptorhagada tattawuppana Not recordedin reserves
n/a Vulnerable
Molluscs Lacustrelix yerelinana Recorded in reserves n/a Near Threatened
Molluscs Pleuroxia italowiana Recorded in reserves n/a Near Threatened
Plants Caladenia macroclavia Recorded in reserves Endangered n/a
Plants Caladenia woolcockiorum Recorded in reserves Vulnerable n/a
Plants Caladenia xantholeuca Recorded in reserves Endangered n/a
Plants Pterostylis lepida Not recordedin reserves
Endangered n/a
Plants Pterostylis mirabilis Recorded in reserves Vulnerable n/a
Plants Acanthocladium dockeri Not recordedin reserves
Critically Endangered
n/a
Plants Pleuropappus phyllocalymmeus Recorded in reserves Vulnerable n/a
Plants Senecio megaglossus Recorded in reserves Vulnerable n/a
Plants Acacia araneosa Recorded in reserves Vulnerable n/a
Plants Acacia praemorsa Recorded in reserves Vulnerable n/a
Plants Acacia spilleriana Recorded in reserves Endangered n/a
Plants Acacia whibleyana Not recordedin reserves
Endangered n/a
Plants Swainsona pyrophila Recorded in reserves Vulnerable n/a
Plants Lachnagrostis limitanea Not recordedin reserves
Endangered n/a
Plants Haloragis eyreana Not recordedin reserves
Endangered n/a
Reptiles Tiliqua adelaidensis Recorded in reserves Endangered Endangered
Concentrations of unreserved endemic species
The colour grids and numbers are an indication of the location and number of endemic species that have all their known range outside of the National Reserve System. Concentrations of unreserved endemic species may be useful focal areas for private land conservation efforts.
Endemism analyses were provided by the Australian Government Department of Environment Australian Natural Heritage Assessment Tool (ANHAT). The ANHAT database has been compiled from specimens and site records held in state agency wildlife atlases, museum collections, and the work of individual researchers. For more information please refer to: http://www.environment.gov.au/topics/heritage/publications-and-resources/australian-natural-heritage-assessment-tool
Invasive speciesINVASIVE MAMMALS
Common name Scientific name % of total distribution* % of zone**
Cat, House Cat, Domestic Cat Felis catus 4.25 99.94
Red Fox, Fox Vulpes vulpes 5.29 99.92
Rabbit, European Rabbit Oryctolagus cuniculus 5.91 99.08
Goat Capra hircus 12.77 83.85
House Mouse Mus musculus 7.5 81.67
Brown Hare Lepus capensis 12.94 39.40
Pig Sus scrofa 3.36 36.21
Domestic Cattle Bos taurus 4.5 23.48
Black Rat, Ship Rat Rattus rattus 6.57 22.39
Domestic Dog Canis lupus familiaris 2.87 21.94
Donkey, Ass Equus asinus 0.68 2.52
Feral deer species in Australia n/a 1.85 2.18
Dromedary, Camel Camelus dromedarius 0.14 1.42
Brown Rat, Norway Rat Rattus norvegicus 2.41 1.40
OTHER INVASIVE FAUNA
Common name Scientific name % of total distribution* % of zone**
Common Starling Sturnus vulgaris 14.8 97.86
House Sparrow Passer domesticus 10.76 97.45
Rock Pigeon, Rock Dove, Domestic Pigeon Columba livia 10.47 81.72
Common Blackbird, Eurasian Blackbird Turdus merula 24.14 67.71
European Goldfinch Carduelis carduelis 20.11 55.22
Skylark Alauda arvensis 23.09 45.65
Spotted Turtle-Dove Streptopelia chinensis 10.96 27.98
Mallard Anas platyrhynchos 11.48 24.89
Common Myna, Indian Myna Acridotheres tristis 2.13 3.37
Eurasian Tree Sparrow Passer montanus 1.47 1.25
Red-whiskered Bulbul Pycnonotus jocosus 2.86 0.70
European Greenfinch Carduelis chloris 0.57 0.34
Ostrich Struthio camelus 27.94 0.22
* % of the total national distribution of the invasive species found within the zone.
** % of the total zone area that the invasive species is likely or known to occur in.
INVASIVE FLORA
Common name Scientific name % of total distribution* % of zone**
Bridal Creeper, Bridal Veil Creeper, Smilax, Florist’s Smilax, Smilax Asparagus
Asparagus asparagoides 20.18 50.74
African Boxthorn, Boxthorn Lycium ferocissimum 23.25 37.48
Boneseed Chrysanthemoides monilifera subsp. monilifera
30.11 29.34
Athel Pine, Athel Tree, Tamarisk, Athel Tamarisk, Athel Tamarix, Desert Tamarisk, Flowering Cypress, Salt Cedar
Tamarix aphylla 9.96 21.54
Blackberry, European Blackberry Rubus fruticosus aggregate 7.88 20.11
Silver Nightshade, Silver-leaved Nightshade, White Horse Nettle, Silver-leaf Nightshade, Tomato Weed, White Nightshade, Bull-nettle, Prairie-berry, Satansbos, Silver-leaf Bitter-apple, Silverleaf-nettle, Trompillo
Solanum elaeagnifolium 40.01 18.31
Willows except Weeping Willow, Pussy Willow and Sterile Pussy Willow
Salix spp. except S.babylonica, S.x calodendron & S.x reichardtii
8.54 17.24
Ward’s Weed Carrichtera annua 11.75 15.22
Prickly Pears Opuntia spp. 12.51 14.55
Gorse, Furze Ulex europaeus 7.98 9.73
Mesquite, Algaroba Prosopis spp. 3.02 5.48
Prickly Pears Cylindropuntia spp. 20.26 3.90
Olive, Common Olive Olea europaea 77.47 3.16
Broom Genista sp. X Genista monspessulana
77.47 3.16
Prickly Pears Austrocylindropuntia spp. 50.76 1.92
Parkinsonia, Jerusalem Thorn, Jelly Bean Tree, Horse Bean
Parkinsonia aculeata 0.32 1.56
Montpellier Broom, Cape Broom, Canary Broom, Common Broom, French Broom, Soft Broom
Genista monspessulana 2.32 1.06
Broom, English Broom, Scotch Broom, Common Broom, Scottish Broom, Spanish Broom
Cytisus scoparius 1.19 0.87
Bridal Veil, Bridal Veil Creeper, Pale Berry Asparagus Fern, Asparagus Fern, South African Creeper
Asparagus declinatus 43.14 0.76
Chilean Needle grass Nassella neesiana 0.68 0.55
Flax-leaved Broom, Mediterranean Broom, Flax Broom
Genista linifolia 4.31 0.54
Climbing Asparagus-fern Asparagus plumosus 3.55 0.35
Climbing Asparagus-fern, Ferny Asparagus Protasparagus plumosus 3.55 0.35
Bitou Bush Chrysanthemoides monilifera subsp. rotundata
1.51 0.31
Water Hyacinth, Water Orchid, Nile Lily Eichhornia crassipes 1.07 0.31
Fireweed, Madagascar Ragwort, Madagascar Groundsel
Senecio madagascariensis 0.4 0.18
Madeira Vine, Jalap, Lamb’s-tail, Mignonette Vine, Anredera, Gulf Madeiravine,
Anredera cordifolia 0.42 0.12
INVASIVE FLORA
Heartleaf Madeiravine, Potato Vine
Buffel-grass, Black Buffel-grass Cenchrus ciliaris 0.31 3.29
Cabomba, Fanwort, Carolina Watershield, Fish Grass, Washington Grass, Watershield, Carolina Fanwort, Common Cabomba
Cabomba caroliniana 2.09 0.66
Lantana, Common Lantana, Kamara Lantana, Large-leaf Lantana, Pink Flowered Lantana, Red Flowered Lantana, Red-Flowered Sage, White Sage, Wild Sage
Lantana camara 0.15 0.22
Serrated Tussock, Yass River Tussock, Yass Tussock, Nassella Tussock (NZ)
Nassella trichotoma 0.11 0.10
Delta Arrowhead, Arrowhead, Slender Arrowhead Sagittaria platyphylla 0.16 0.04
Asparagus Fern, Climbing Asparagus Fern Asparagus scandens 0.03 0.00
Asparagus Fern, Ground Asparagus, Basket Fern, Sprengi’s Fern, Bushy Asparagus, Emerald Asparagus
Asparagus aethiopicus 0.02 0.00
* % of the total national distribution of the invasive species found within the zone.
** % of the total zone area that the invasive species is likely or known to occur in.
It should be noted that the identification of any given invasive species above does not imply that the species is found uniformly across the Conservation Management Zone. The % of the zone area (**) indicates how common or rare the species may be within the zone.
For more information on invasive species please refer to: http://www.environment.gov.au/topics/biodiversity/invasive-species
Vegetation profiles and management recommendations
Vegetation extent information and species lists contained in the vegetation profiles are based on analysis from the National Vegetation Information System (NVIS), including analysis of Major Vegetation Subgroups and NVIS Level V descriptions. Please see http://www.environment.gov.au/node/18930 for more information.
The management recommendations have been drawn from EPBC Act Recovery Plans, EPBC Act Ecological Communities Listing Advice and other sources. The recommendations are indicative only. Systematic reviews of management literature, consultation processes and improved Natural Resource Management program monitoring and evaluation will support development of a comprehensive set of management recommendations over time.
Mallee with a tussock grass understorey vegetation profile
1.43% Remaining
Commonly found species within this communityEucalyptus socialis; Eucalyptus dumosa; Eucalyptus odorata; Eucalyptus porosa; Eucalyptus leptophylla; Allocasuarina verticillata; Eucalyptus behriana; Enchylaena tomentosa; Melaleuca lanceolata; Rhagodia spinescens; Austrodanthonia caespitosa; Austrostipa eremophila; Austrodanthonia setacea; Austrostipa scabra; Hordeum leporinum; tussock grass; forb; samphire shrub.
Management recommendationsPROTECTION SUSTAINABLE
AGRICULTURAL PRACTICE
REHABILITATION FIRE MANAGEMENT
WILDLIFE MANAGEMENT
WEED MANAGEMENT
FERAL ANIMAL MANAGEMENT
DISEASE MANAGEMENT
Protect against dryland salinity by maintaining and replanting native vegetation.Close or fence artificial sources of water in conservation reserves as these may attract feral species and trampling.Protect, and where appropriate, fence important wildlife habitat including for Malleefowl.Encourage uptake of conservation agreements and covenants on private land
Exclude stock from remnants to enable recruitment and regeneration of over and under-storey species.Create windbreaks with mallee species to reduce the impacts of soil erosion.Reduce tillage in zones around remnants.Avoid creating new access tracks and roads through remnants.
Undertake restoration where there are few mature overstorey species or lack of suitable sites for seed germination.Choose mallee species that occur in remnants on similar soils and slope aspect. Replicate therelative abundance of species.Manage wildlife corridors between remnant patches.Create buffer zones around remnants by revegetating previously cleared lands with mallee and ground storey species.
Reduce the occurrence of large fires, and use mosaic burning techniques.Ensure mosaic burns are targeted at different age classes of vegetation, to ensure age diversity between and within remnant patches.Discourage broadscale burning for agricultural purposes in areas that harbour Malleefowl.Avoid clearing roadsides for firebreaks.
Manage native grazing animalsMinimise the amount of grain spilt during transport through Malleefowl habitat.Erect signs where needed to warn drivers that Malleefowl may be on the road.
Actively manage weeds when undertaking restoration activities to ensure weeds do not compete for soil moisture with vulnerable native replantings.A 1-metre radius weed free buffer should be maintained around native woody plants. Use spot control to maintain this.Apply herbicides to actively growing weeds and avoid spray drift.Do not leave areas of bare ground to avoid wind and water erosion of soils. Retain some weed cover and stagger removal and replacement with native grasses.
Manage exotic herbivore species including goats, sheep, rabbits especially near habitat for wildlife such as Malleefowl.Control foxes and rabbits simultaneously to avoid foxes switching to predation on native species, or increases in rabbit populations.Shooting is a suitable control for goats, wallabies, goats, deer, hares and foxes. Baiting is appropriate for rabbits, hares and foxes.Monitor for Red-legged earth mites. Populations should be managed with a soil active insecticide.
Saltbush and/or Bluebush shrublands vegetation profile
95.5% Remaining
Commonly found species within this communityAtriplex vesicaria; Atriplex paludosa; Nitraria billardierei; Maireana sedifolia; Maireana pyramidata; Maireana astrotricha; Maireana oppositifolia; Rhagodia spinescens; Frankenia sessilis; shrub; tussock grass; forb.
Management recommendationsPROTECTION SUSTAINABLE
AGRICULTURALPRACTICE
REHABILITATION FIREMANAGEMENT
WILDLIFEMANAGEMENT
WEEDMANAGEMENT
FERALANIMALMANAGEMENT
DISEASEMANAGEMENT
Establish pest-proof fencing around key refugia.Promote wise water use to avoid changes to water flow/water table levels that could impact on aquifers and overland flow.
Avoid continuous or heavy grazing to allow saltbush to regenerate and seed. Experiment with different saltbush species for livestock forage, and implement strategic grazing regimes to maximise both production yields and biodiversity benefits.Refer to http://www.malleecma.vic.gov.au/resources/fact-sheets/enrich-fs.pdfto explore the benefits of different grazing regimes and saltbush species.
Undertake intensive management of identified key refugia and wildlife habitats. Maintain dingo populations to control exotic pests. Re-introduce engineer species (e.g. bilbies and bettongs) where feral animal controls are in place and effective.Manage native grazing pressure (e.g. from kangaroos).
Actively manage weeds when undertaking restoration activities to ensure weeds do not compete for soil moisture with vulnerable native replantings. Apply herbicides to actively growing weeds and avoid spray drift. Do not leave areas of bare ground to avoid wind and water erosion of soils. Retain some weed cover and stagger removal and replacement with native grasses.
Target rabbits, foxes and cats in key refugia and habitats. Manage foxes and rabbits simultaneously to prevent foxes switching to predation on native species, or increases in rabbit populations.
Mallee with a dense shrubby understorey vegetation profile
96.79% remaining
Commonly found species within this communityEucalyptus diversifolia; Eucalyptus porosa; Eucalyptus costata subsp. Murrayana; Eucalyptus brachycalyx; Eucalyptus socialis; Eucalyptus gracilis; Eucalyptus oleosa; Eucalyptus incrassata; Eucalyptus leptophylla; Eucalyptus dumosa; Melaleuca uncinata; Melaleuca lanceolata; Melaleuca acuminata; Sclerolaena diacantha; Enchylaena tomentosa; Rhagodia parabolica; shrub; tussock grass; forb.
Management recommendationsPROTECTION SUSTAINABLE
AGRICULTURALPRACTICE
REHABILITATION FIREMANAGEMENT
WILDLIFEMANAGEMENT
WEEDMANAGEMENT
FERALANIMALMANAGEMENT
DISEASEMANAGEMENT
Protect against dryland salinity by maintaining and replanting native vegetation.Close or fence artificial sources of water in conservation reserves.Protect, and where appropriate fence important wildlife habitat including for Malleefowl.Encourage uptake of conservation agreements and covenants.
Exclude stock from remnants to enable recruitment and regeneration of over and under-storey species.Create windbreaks with mallee species to reduce the impacts of soil erosion.Reduce tillage in zones around remnants.Avoid creating new access tracks and roads through remnants.
Undertake restoration where there are few mature overstorey species or lack of suitable sites for seed germination.Choose mallee species that occur in remnants on similar soils and slope aspect. Replicate the relative abundance of species.Manage wildlife corridors between remnant patches.Create buffer zones around remnants by revegetating previously cleared lands with mallee and ground storey species.
Reduce the occurrence of large fires, and use mosaic burning techniques.Ensure mosaic burns are targeted at different age classes of vegetation, to ensure age diversity between and within remnant patches.Avoid clearing roadsides for firebreaks.Discourage broadscale burning for agricultural purposes in lands near Malleefowl habitat.
Manage native grazing animals.Minimise the amount of grain spilt during transport through Malleefowl habitat, as foraging close to roadsides leaves them susceptible to collisions with vehicles.Erect signs where needed to warn drivers that Malleefowl may be on the road.
Actively manage weeds when undertaking restoration activities to ensure weeds do not compete for soil moisture with vulnerable native replantings.A 1-metre radius weed free buffer should be maintained around native woody plants. Use spot control to maintain this.Apply herbicides to actively growing weeds and avoid spray drift.Do not leave areas of bare ground to avoid wind and water erosion of soils. Retain some weed cover and stagger removal and
Manage exotic herbivore species including goats, sheep, rabbits especially near habitat for wildlife such as Malleefowl.Control foxes and rabbits simultaneously to avoid foxes switching to predation on native species, or increases in rabbit populations.Shooting is a suitable control for goats, wallabies, goats, deer, hares and foxes. Baiting is appropriate for rabbits, hares and foxes.Monitor for Red-legged earth mites. Populations should be managed with a
Mallee with hummock grass vegetation profile
79.8% Remaining
Commonly found species within this communityEucalyptus socialis; Eucalyptus dumosa; Eucalyptus porosa; Callitris glaucophylla; Eucalyptus gracilis; Myoporum platycarpum; Eucalyptus leptophylla; Acacia wilhelmiana; Callitris verrucosa; Leptospermum coriaceum; Acacia ligulata; Triodia scariosa; Rhagodia spinescens; Senna artemisioides ssp. Coriacea; Dodonaea viscosa ssp. angustissima; Halgania cyanea; Brachyloma ericoides; Beyeria opaca; Westringia rigida; Grevillea huegelii; hummock grass; shrub.
Management recommendationsPROTECTION SUSTAINABLE
AGRICULTURALPRACTICE
REHABILITATION FIREMANAGEMENT
WILDLIFEMANAGEMENT
WEEDMANAGEMENT
FERALANIMALMANAGEMENT
DISEASEMANAGEMENT
Protect against dryland salinity by maintaining and replanting native vegetation.Close or fence artificial sources of water in conservation reserves as these may attract feral species and trampling.Protect, and where appropriate, fence important wildlife habitat includingfor Malleefowl.Encourage uptake of conservation agreements and covenants on private land.
Exclude stock from remnants to enable recruitment and regeneration of over andunder-storey species.Create windbreaks with mallee species to reduce the impacts of soil erosion. Reduce tillage in zones around remnants.Avoid creating new access tracks and roads through
remnants.
Undertake restoration where there are few mature overstorey species or lack of suitable sites for seed germination.Choose mallee species that occur in remnants on similar soils and slope aspect. Replicate the relative abundance
of species.Manage wildlife corridors betweenremnant patches. Create buffer zones around remnants by revegetating previously cleared lands with mallee and groundstorey species.
Reduce the occurrence of large fires, and use mosaic burning techniques.Ensure mosaic burns are targeted at different age classes of vegetation, to ensure age diversity between and within remnant patches. Discourage broad-scale burning for agricultural purposes in areas that harbour Malleefowl.Avoid clearing roadsides for firebreaks. Discourage broad-scale burning for agricultural purposes in areas that harbour Malleefowl.
Manage native grazing animals. Minimise the amount of grain spilt during transport through areas that harbour
Malleefowl.Erect signs where needed to warn drivers that Malleefowl may be on the road.
Actively manage weeds when undertaking restoration activities to ensure weeds do not compete for soil moisture with vulnerable native replantings. Apply herbicides to actively growing weeds and avoid spray drift. Avoid wind and water erosion of soils. Retain some weed cover and stagger removal and replacement with native grasses.
Manage exotic herbivore species including goats, sheep, rabbits especially near habitat for wildlife such as Malleefowl. Control foxes and rabbits simultaneously to avoid foxes switching to predation on native species, or increases in rabbit
populations.Shooting is a suitable control for goats, wallabies, goats, deer, hares and foxes. Baiting is appropriate for rabbits, hares and foxes.Monitor for Red-legged earth mites. Populations should be
Casuarina and Allocasuarina open woodlands with a shrubby understorey vegetation profile
98.16% Remaining
Commonly found species within this communityCasuarina pauper; Alectryon oleifolius ssp. Canescens; Callitris gracilis; Olearia decurrens; Senna artemisioides ssp. Coriacea; Senna artemisioides ssp. Petiolaris; Senna artemisioides ssp. filifolia; Alyxia buxifolia; Geijera linearifolia; Maireana sedifolia; Enchylaena tomentosa; Enchylaena tomentosa var.,Maireana georgei/turbinata; shrub.
Management recommendationsPROTECTION SUSTAINABLE
AGRICULTURALPRACTICE
REHABILITATION FIREMANAGEMENT
WILDLIFEMANAGEMENT
WEEDMANAGEMENT
FERALANIMALMANAGEMENT
DISEASEMANAGEMENT
Purchase threatened ecological communities, such as Buloke woodlands into reservation. Encourage uptake of conservation agreements and covenants on private land.Encourage wise water use and avoid changes to water table levels. Retain standing dead trees and fallen timber.
Manage grazing pressure in remnants with an intact, native ground layer.Exclude stock from remnants or areas with scattered trees for a few years to allow regeneration, then protect the young trees if stock need to be re-introduced.Establish buffers of indigenous shrubs around all small reserves, to reduce fertilizer drift and accretion of aeolian soils in overlying loam.Avoid fertiliser and herbicide application.
In-plant woody species where regeneration does not naturally occur.Replicate the species composition and density of good quality remnants (an open canopy of trees; open tall shrubs or small trees; and a number of lower strata, including a dense grassy layer). As far as possible, restore natural infrequent environmental flows along the Wimmera River and River Murray. These floodwaters provide infrequent, but essential inundation and soil moisture levels to
Fires of very low intensity may have been important in maintaining the open nature and the grassiness of Buloke Woodlands.It is suspected that lack of fire, in association with removal of grazing, has led to increased woody species in the lower strata of otherwise good quality remnants.Canopy tree regeneration is unlikely after severe wildfire. In the event of wildfire, revegetation of overstorey species may be necessary.
Manage populations of kangaroos.
Manage Avena species, Brachypodium distachyon, Bromus species, Lolium species, Medicago species, Poa bulbosa and Trifolium species.
Manage exotic herbivore species including goats, sheep, rabbits especially near habitat for wildlife such as Malleefowl. Control foxes and rabbits simultaneously to avoid foxes switching to predation on native species, or increases in rabbit populations.Protect rehabilitation sites from incursions of feral species through fencing.
PROTECTION SUSTAINABLEAGRICULTURALPRACTICE
REHABILITATION FIREMANAGEMENT
WILDLIFEMANAGEMENT
WEEDMANAGEMENT
FERALANIMALMANAGEMENT
DISEASEMANAGEMENT
enable seed germination.
Mallee with an open shrubby understorey vegetation profile
57.63% Remaining
Commonly found species within this communityEucalyptus diversifolia; Eucalyptus dumosa; Eucalyptus socialis; Eucalyptus oleosa; Eucalyptus gracilis; Rhagodia parabolica; Melaleuca uncinata; Melaleuca lanceolata; Melaleuca acuminata; Pittosporum angustifolium; Nitraria billardierei; Maireana pyramidata; Santalum acuminatum; Exocarpos aphyllus; Eremophila glabra; Triodia irritans; Maireana pentatropis; Stenopetalum lineare; samphire shrub; forb; other grass; hummock grass.
Management recommendationsPROTECTION SUSTAINABLE
AGRICULTURALPRACTICE
REHABILITATION FIREMANAGEMENT
WILDLIFEMANAGEMENT
WEEDMANAGEMENT
FERALANIMALMANAGEMENT
DISEASEMANAGEMENT
Protect against dryland salinity by maintaining and replanting native vegetation.Close or fence artificial sources of water in conservation reserves as these may attract feral species and trampling.Protect, and where appropriate, fence important wildlife habitat including for Malleefowl.Encourage uptake of conservation agreements and covenants on private land.
Exclude stock from remnants to enable regeneration of over and under-storey species.Create windbreaks with mallee species to reduce the impacts of soil erosion. Reduce tillage in zones around remnants.Avoid creating new access tracks and roads through remnants.
Undertake restoration where there are few mature overstorey species or lack of suitable sites for seed germination.Choose mallee species that occur in remnants on similar soils and slope aspect. Replicate the relative abundance
of species.Manage wildlife corridors between remnant patches. Create buffer zones around remnants by revegetating previously cleared lands with mallee and ground
Reduce the occurrence of large fires, and use mosaic burning techniques.Ensure mosaic burns are targeted at different age classes of vegetation, to ensure age diversity between and within remnant patches. Discourage broad-scale burning for agricultural purposes in areas that harbour Malleefowl.Avoid clearing roadsides for firebreaks.
Manage native grazing animals. Minimise the amount of grain spilt during transport through Malleefowl habitat.Erect signs where needed to warn drivers that Malleefowl may be on the road.
Actively manage weeds when undertaking restoration activities to ensure weeds do not compete for soil moisture with vulnerable native replantings.Apply herbicides to actively growing weeds and avoid spray drift. Avoid wind and water erosion of soils. Retain some weed cover and stagger removal and replacement with native grasses.
Manage exotic herbivore species including goats, sheep, rabbits. Protect rehabilitation sites from incursions of feral species through fencing. Ensure rabbit control is followed by fox control to avoid foxes switching to predation on native species, or increases in rabbit populations.