DARLING RIVERINE PLAINS BIOREGION Background Report

DARLING RIVERINE 

PLAINS BIOREGION 

Background Report 

NSW BIODIVERSITY STRATEGY 

[JULY 2002]

DARLING RIVERINE 

PLAINS 

BACKGROUND REPORT 

DARLING RIVERINE PLAINS 

BIOREGION 

A project undertaken for the 

NSW Biodiversity Strategy

For more information data contact the: 

Western Regional Assessments Unit, NSW National Parks and Wildlife Service 

PO Box 2111 

DUBBO NSW 2830 

Ph: (02) 6841 9200 

Fax: (02) 6841 9222 

www.npws.nsw.gov.au 

© Crown copyright [July 2002] 

New South Wales Government 

ISBN 0731365305 

This project has been funded by the NSW Biodiversity Strategy and coordinated by Western Regional Assessments Unit, 

NSW National Parks and Wildlife Service 

This report was produced by Anne Kearle, Carl Gosper, Helen Achurch and Tania Laity. Maps in the atlas were produced by 

Fiona Ross. 

Thanks to Gary Saunders for managing the project and providing valuable input. 

For their comments: 

Bill Johnson, NSW National Parks and Wildlife Service; 

Mike Maher, NSW National Parks and Wildlife Service; 

Murray Ellis, NSW National Parks and Wildlife Service; 

Mike Fleming, NSW National Parks and Wildlife Service; 

Steve Lewer, NSW Department of Land and Water Conservation; 

Darren Shelley, NSW Department of Land and Water Conservation; 

Terry Mazzer, NSW Department of Land and Water Conservation; and 

Patrick Tap, State Forests of New South Wales. 

Disclaimer 

While every reasonable effort has been made to ensure that this document is correct at the time of printing, the State of New 

South Wales, its agents and employees, do not assume any responsibility and shall have no liability, consequential or 

otherwise, of any kind, arising from the use of or reliance on any of the information contained in this document.

CONTENTS 

PROJECT SUMMARY 

1 INTRODUCTION 14 

1.1 The Background Report 14 

1.2 The DRP Biodiversity Conservation Assessment Project 15 

1.2.1 Objectives of the DRP project 15 

1.2.2 Funding for the DRP project 15 

1.2.3 Associated projects 16 

1.3 The Darling Riverine Plains Bioregion 18 

1.3.1 Location and area 18 

1.3.2 Human history 18 

1.3.3 Land tenure and administrative boundaries 22 

2 ABIOTIC FEATURES 29 

2.1 Introduction 29 

2.2 Climate 29 

2.2.1 Rainfall: temporal and spatial variation 30 

2.2.2 Winds 36 

2.2.3 Temperature and evaporation 37 

2.3 Geology, Topography And Soils 39 

2.3.1 Geological history 39 

2.3.2 Topography and geomorphology 41 

2.3.3 Soils 41 

2.4 Hydrology 42 

2.4.1 Surface waters: rivers, catchments and wetlands 42 

2.4.2 Groundwaters 49 

2.5 Land Condition 51 

2.5.1 Land degradation 51 

2.5.2 River and wetland degradation 52 

2.5.3 Salinity 53 

2.6 Boundaries Within the DRP 55 

2.6.1 Provinces 55 

2.6.2 Land systems 58 

2.7 Summary and Proposed Further Work 58 

2.7.1 Summary 58 

2.7.2 Proposed further work 59 

3 VEGETATION 60 

3.1 Vegetation in 1750 and Subsequent Modification 60

3.2 Vegetation Mapping and Description in the DRP 62 

3.3 Plant Community Descriptions 64 

3.3.1 Forests and woodlands 70 

3.3.2 Shrublands 73 

3.3.3 Grassland and wetland communities 74 

3.3.4 Plant communities of major DRP wetlands 76 

3.4 Conservation Status of Vegetation Communities in The DRP 80 

3.4.1 Corymbia tessellaris (carbeen) open forest 81 

3.4.2 Acacia loderi (nelia) shrublands 81 

3.4.3 Artesian springs ecological community 82 

3.4.4 The community of native species dependent on natural discharge of groundwater from the 

Great Artesian Basin 83 

3.4.5 Acacia harpophylla (brigalow dominant or co-dominant) 83 

3.5 Summary And Proposed Further Work 84 



4 FLORA 86 

4.1 Available Information 86 

4.1.1 Sources of data 86 

4.1.2 Plant species diversity of the DRP 87 

4.2 Species of Conservation Concern 88 

4.2.1 Threatened and ROTAP species 88 

4.2.2 Predicted threatened species 89 

4.2.3 Extinct species and historical records 90 

4.2.4 Regionally endemic species and significant populations 91 

4.3 Weed And Introduced Species 91 

4.4 Summary And Proposed Further Work 91 



5 TERRESTRIAL VERTEBRATE FAUNA 93 

5.1 Available Information 93 

5.1.1 Sources of data 93 

5.1.2 Species diversity of terrestrial vertebrates in the DRP 94 

5.2 Amphibians 95 

5.2.1 Known species diversity and distribution 95 

5.2.2 Species of conservation concern 95 


5.3 Reptiles 96 




5.4 Birds 99 




5.4.4 Introduced and pest species 106 

5.5 Mammals 106 




5.5.4 Introduced and pest species 109 


5.6.1 Summary 110 

5.6.2 Proposed further work 111

6 OTHER FAUNA 112 

6.1 Invertebrates 112 

6.1.1 Aquatic invertebrates 112 

6.1.2 Terrestrial invertebrates 113 

6.2 Fish 113 




6.2.4 Introduced fish species 116 


6.3.1 Summary 118 


7 ECOLOGICAL AND THREATENING PROCESSES 119 

7.1 Ecological Processes 119 

7.1.1 Nutrient cycling and soil formation 119 

7.1.2 Hydrological regimes 120 

7.2 Listed and Potential Threatening Processes 121 

7.2.1 Listed Threatening Processes 121 

7.2.2 Potential Threatening Processes 126 

7.3 Weeds and Pest Animals 127 

7.3.1 Weeds 127 

7.1.2 Dense tree and shrub regeneration 128 

7.3.2 Kangaroos 129 

7.3.3 Feral animals 129 

7.4 Other Threats to Biodiversity 129 

7.4.1 Firewood collection and timber harvesting on private lands 129 

7.4.2 Grazing 130 


7.5.1 Summary 130 


8 EXISTING CONSERVATION MANAGEMENT 131 

8.1 Existing Conservation Assessments 131 

8.2 Formal Reserves and Other Crown Lands 134 

8.2.1 National Parks and Nature Reserves 134 

8.2.2 Other Crown lands Managed For Conservation 139 

8.3 Off-Reserve Conservation 141 

8.3.1 Voluntary Conservation Agreements 141 

8.3.2 Wildlife Refuges 141 

8.3.3 Forest Management Zones 141 

8.3.4 Catchment Blueprints 142 

8.3.5 Water Management Plans 143 

8.3.6 Regional Vegetation Management Plans 144 

8.3.7 Salinity Management Plans 145 

8.4 Areas of Biological Significance 145 

8.4.1 Key areas 145 

8.4.2 Refugia 146 

8.4.3 Centres of endemism 147 

8.4.4 Areas of high biodiversity 148 

8.5 Wilderness Values in the DRP (NSW) 148 


8.6.1 Summary 148 


9 REFERENCES 150

10 APPENDICES 166 

A CLIMATIC DATA 

B LAND SYSTEMS 

C PLANT SPECIES LIST 

D EXOTIC PLANT SPECIES 

E NATIVE FAUNA 

F WATERBIRD SURVEY DATA 

G INVERTEBRATE TAXA

List of Tables 

Chapter 1 

Table 1.1 NPWS estate in the DRP ...............................................................................................................................22 

Table 1.2 State Forests in the DRP................................................................................................................................23 

Table 1.3 State government electorates within the DRP ...............................................................................................24 

Table 1.4 DLWC regions within the DRP.....................................................................................................................24 

Table 1.5 NPWS administrative boundaries within the DRP ........................................................................................24 

Table 1.6 SFNSW administrative boundaries within the DRP ......................................................................................25 

Table 1.7 RLPBs within DRP .......................................................................................................................................25 

Table 1.8 RVCs within the DRP ...................................................................................................................................26 

Table 1.9 Water Management Committees within the DRP..........................................................................................26 

Table 1.10 CMBs within the DRP...................................................................................................................................26 

Table 1.11 Local Government areas which intersect the DRP ........................................................................................27 

Table 1.12 Aboriginal Land Councils within the DRP....................................................................................................28 

Chapter 2 

Table 2.1 DRP meteorological stations used in this analysis.........................................................................................29 

Table 2.2 Wetlands identified within each catchment of the DRP ................................................................................44 

Table 2.3 River catchments intersecting the DRP .........................................................................................................45 

Table 2.4 Groundwater resources of the Lower Namoi Catchment...............................................................................51 

Table 2.5 Actual and predicted average salinity levels for major rivers in the DRP .....................................................54 

Table 2.6 Predictions of the tonnes of salt mobilised to the land surface per year for river catchments of the DRP.....54 

Chapter 3 

Table 3.1 Existing broad-scale vegetation mapping in the DRP ...................................................................................62 

Table 3.2 Dominant plant communities of major wetlands of the DRP ........................................................................76 

Table 3.3 Dominant plant species in the Lower Gwydir Watercourse ..........................................................................78 

Chapter 4 

Table 4.1 Summary of floristic surveys conducted within the DRP..............................................................................87 

Table 4.2 Plant species of conservation concern recorded in the DRP..........................................................................88 

Table 4.3 Plant species of conservation concern predicted to occur in the DRP ...........................................................89 

Table 4.4 Extinct plant species in New South Wales previously recorded from the DRP.............................................90 

Table 4.5 Plant species of conservation concern known historically from the DRP but with no recent records ...........90 

Chapter 5 

Table 5.1 Summary of systematic fauna surveys conducted within the DRP................................................................93 

Table 5.2 Reptile species of conservation concern recorded within the DRP................................................................98 

Table 5.3 Bird species of conservation significance recorded from the DRP..............................................................102 

Table 5.4 Feral bird species recorded in the DRP .......................................................................................................106 

Table 5.5 Mammal species of conservation concern recorded in the DRP..................................................................107 

Table 5.6 Feral mammals recorded from the DRP. .....................................................................................................109 

Table 5.7 Summary of vertebrate taxa in the DRP ......................................................................................................110 

Chapter 6 

Table 6.1 Fish species known or likely to occur in the Darling Region ......................................................................113 

Table 6.2 Fish species of conservation concern within the DRP.................................................................................115 

Table 6.3 Introduced fish species recorded within the Barwon-Darling Region .........................................................117 

Chapter 7 

Table 7.1 Declared noxious weeds occurring within the DRP ....................................................................................128 

Chapter 8 

Table 8.1 Reservation status of major regional ecosystems in the DRP......................................................................132 

Table 8.2 Threatened fauna recorded within State forests of the DRP ........................................................................140 

Table 8.3 Dominant vegetation types within State forests of the DRP........................................................................140 

Table 8.4 Wildlife Refuges within the DRP................................................................................................................141 

Table 8.5 Forest Management Zones...........................................................................................................................142 

Table 8.6 River flow rules and implementation status within the DRP.......................................................................143 

Table 8.7 Water sharing plans being prepared within the DRP...................................................................................144

List of Maps 

Chapter 1 

Map 1 Location of the Darling Riverine Plains Bioregion 

Map 2 The Darling Riverine Plains Bioregion 

Map 3 Aboriginal sites in the DRP 

Map 4 Land tenure 

Map 5 Aboriginal Land Council Areas in the DRP 

Map 6 State electoral boundaries 

Map 7 NSW National Parks and Wildlife Service Regions and Areas 

Map 8 State Forests of NSW management areas 

Map 9 Department of Land and Water Conservation Regions 

Map 10 Rural Lands Protection Board boundaries 

Map 11 Regional Vegetation Committee boundaries 

Map 12 Catchment Management Board areas 

Map 13 Local Government Areas 

Chapter 2 

Map 14 Average annual rainfall 

Map 15 Average annual temperature 

Map 16 Lithology 

Map 17 Digital elevation model 

Map 18 Soils of the DRP 

Map 19 Major rivers and catchment boundaries 

Map 20 Major wetlands 

Map 21 Darling Riverine Plains provinces 

Map 22 Darling Riverine Plains landsystems 

Chapter 3 

Map 23 Moree RVC pre-clearing vegetation 

Map 24 M305 vegetation densities 

Map 25 Extent of vegetation mapping for the DRP 

Chapter 4 

Map 26 Flora records per 1:100 000 map sheet in the Atlas of NSW Wildlife 

Map 27 Post-1970 threatened flora records 

Map 28 Threatened flora records per 1:100 000 map sheet in Atlas of NSW Wildlife 

Chapter 5 

Map 29 Post-1970 amphibian records in the DRP 

Map 30 Atlas of NSW Wildlife records per 1:100 000 mapsheet: amphibians 

Map 31 Post-1970 reptile records in the DRP 

Map 32 Atlas of NSW Wildlife records per 1:100 000 mapsheet: reptiles 

Map 33 Post-1970 threatened reptile records in the DRP 

Map 34 Post-1970 bird records in the DRP 

Map 35 Atlas of NSW Wildlife records per 1:100 000 mapsheet: birds 

Map 36 Post-1970 threatened bird records in the DRP 

Map 37 Records of feral bird species in the DRP 

Map 38 Post-1970 mammal records in the DRP 

Map 39 Atlas of NSW Wildlife records per 1:100 000 mapsheet: mammals 

Map 40 Post-1970 threatened mammal records in the DRP 

Map 41 Records of feral mammal species in the DRP 

Map 42 Atlas of NSW Wildlife records per 1:100 000 mapsheet: threatened species

List of Figures 

Chapter 1 

Figure 1.1 Reports resulting from the DRP Biodiversity Conservation Assessment Project ..........................................16 

Chapter 2 

Figure 2.1 Annual rainfall records for Bourke 1871-1999..............................................................................................31 

Figure 2.2 Bourke mean monthly rainfall and range between first and ninth decile.......................................................31 

Figure 2.3 Mungindi mean monthly rainfall and range between first and ninth decile...................................................32 

Figure 2.4 Menindee mean monthly rainfall and range between first and ninth decile...................................................32 

Figure 2.5 Trangie mean monthly rainfall and range between first and ninth decile ......................................................33 

Figure 2.6 Walgett mean monthly rainfall and range between first and ninth decile......................................................33 

Figure 2.7 Median monthly rainfall for weather stations across the DRP.......................................................................34 

Figure 2.8 Mean monthly rain days recorded across the DRP ........................................................................................34 

Figure 2.9 Rainfall CuSums for five locations in the DRP .............................................................................................35 

Figure 2.10 Mean monthly wind speed at 9am.................................................................................................................36 

Figure 2.11 Mean monthly wind speed at 3pm.................................................................................................................37 

Figure 2.12 Mean monthly maximum temperatures .........................................................................................................38 

Figure 2.13 Mean monthly minimum temperatures..........................................................................................................38 

Figure 2.14 Mean daily evaporation at Walgett and Bourke.............................................................................................39 

Figure 2.15 Geological history of the Nyngan and Walgett 1:250 000 map sheets ..........................................................40 

Figure 2.16 Lower Gwydir Wetlands ...............................................................................................................................48 

Figure 2.17 Groundwater features of the Coonamble Embayment of the Great Artesian Basin.......................................50 

Chapter 3 

Figure 3.1 Profile of the Bogan-Macquarie Province .....................................................................................................64 

Figure 3.2 Profile of the Castlereagh-Barwon Province .................................................................................................65 

Figure 3.3 Profile of the Culgoa-Bokhara Province........................................................................................................65 

Figure 3.4 Profile of the Warrambool-Moonie Province ................................................................................................66 

Figure 3.5 Profile of the Narran-Lightning Ridge Province............................................................................................66 

Figure 3.6 Profile of the Collarenebri Interfluve Province .............................................................................................67 

Figure 3.7 Profile of the Louth Plains Province..............................................................................................................67 

Figure 3.8 Profile of the Wilcannia Plains Province.......................................................................................................68 

Figure 3.9 Profile of the Menindee Province..................................................................................................................68 

Figure 3.10 Profile of the Great Darling Anabranch Province..........................................................................................69 

Figure 3.11 Profile of the Pooncarie-Darling Province.....................................................................................................69 

Figure 3.12 Profile of land units within the Lower Gwydir Wetlands ..............................................................................78 

Chapter 8 

Figure 8.1. Bioregional conservation assessment framework 133 

Figure 8.2. Nationally significant biological refugia within the DRP 147

PROJECT SUMMARY 

This report forms part of stage one of the two stage Darling Riverine Plains Conservation 

Assessment Project, funded by the NSW Biodiversity Strategy, which was released in 1999. 

The Biodiversity Strategy is a whole of government document and all government agencies 

are committed to working cooperatively towards conserving the biodiversity of NSW. The 

Strategy outlines a framework for coordinating and integrating government and community 

efforts to conserve biodiversity across all landscapes. 

Project objectives and methods 

The existing abiotic and biotic information of the Darling Riverine Plains bioregion (DRP) 

within New South Wales has been collated and synthesised in this report. This information 

provides a baseline for planning further work and conservation needs in this bioregion. The 

human activities in this region are also outlined as these have an impact on the natural 

distribution and abundance of plants and animals and affect the measures required for 

biodiversity conservation. 

Key features of the DRP in NSW 

The Darling Riverine Plains bioregion is a fluvial environment, having been almost entirely 

shaped and maintained by water flow and responses to water. This is reflected by the alluvial 

origin of the underlying geology and soils and by the gently undulating topography. Rivers 

and wetlands of the lower plains and floodplains of six catchments make up the bioregion and 

an understanding of the hydrology of the bioregion is fundamental to an understanding of the 

ecosystems. Flooding is essential for the healthy functioning of the ecosystem. Flooding is 

extremely irregular and does not follow predictable patterns. 

The Darling Riverine Plains bioregion in NSW covers approximately 9 255 000 ha 

(approximately 12% of New South Wales) and includes the lower reaches and alluvial fans of 

the Bogan, Macquarie, Castlereagh, Namoi, Barwon, Culgoa, Bokhara, Narran, Gwydir and 

MacIntyre Rivers and the Darling River corridor from Bourke to the southern edge of the 

Menindee Lakes. 

Although almost all of the bioregion lies within the semi-arid zone, there is substantial 

climatic variation. This is especially so for rainfall, which varies both spatially and

temporally. Annual averages are of little value for understanding the responses of ecological 

processes and requirements. 

Major changes have been made to this natural environment since European occupation. 

Extensive areas have been cleared of native vegetation, especially in the east, and in the west 

the combination of drought and overgrazing by sheep and rabbits have led to extensive 

denudation of the land. Agricultural enterprises have created changes including altered runoff 

patterns, changes in turbidity and nutrient status of rivers and increased salinity in the 

rives and in the soil. Stream regulation has changed flow and flooding patterns resulting in 

change to riverine and wetland ecosystems. Land tenure varies from large areas of leasehold 

land (50% of the bioregion) in the west, to predominantly freehold (40.5% of the bioregion) 

in the east. Approximately 9.5% of the bioregion is Crown land. The large number of 

administrative boundaries crossing this bioregion has resulted in inconsistent levels of 

research being carried out. 

No systematic plant or animal surveys have been conducted across the entire bioregion but 

general descriptions of vegetation communities are broadly consistent, with several 

woodland, shrubland, grassland and wetland communities having been described. Coolibah, 

Black Box and River Red Gum communities are generally the most common associations. 

More detailed mapping of these communities is needed. There are three communities, 

Corymbia tessellaris (carbeen), Acacia loderi (nelia), and the artesian springs community 

listed as threatened under the Threatened Species Conservation Act, 1995 (NSW) (TSC Act) 

and the Acacia harpophylla (brigalow) community has a preliminary determination. The 

brigalow and artesian springs communities are also listed under the Environment Protection 

and Biodiversity Conservation Act, 1999 (Commonwealth of Australia) (EPBC Act) and 

several other communities have been noted as of concern. 

A total of 1 129 plant taxa are recorded on databases covering the Darling Riverine Plains 

bioregion within NSW. Nineteen of these species are listed as vulnerable or endangered, five 

as extinct under the TSC Act and twenty are on the national register of Rare or Threatened 

Australian Plants (ROTAP) (Briggs & Leigh 1996). There are also 229 exotic species 

recorded. These plant records are unevenly distributed across the bioregion and detailed 

floristic surveys have been patchy with large areas never having been surveyed. 

The distribution and abundance of terrestrial vertebrates is also based on few and scattered 

surveys and incidental records and there are substantial gaps in the coverage of the 

information. The most detailed information available is for waterbird fauna in the three major 

wetlands, Macquarie Marshes, Narran Lakes and the Gwydir Wetlands and some detailed 

analysis is possible. Five hundred and six terrestrial vertebrate species have been recorded 

from the DRP. Of these, 65 are listed under the TSC Act, 9 as extinct, 11 endangered and 45 

as vulnerable. Other threatened species are noted as being predicted to occur in the bioregion 

or as of concern, either near threatened or in decline. Twenty-four species are listed under the 

Japan Australia and China Australia Migratory Bird Agreements (JAMBA and CAMBA). 

The information available for invertebrates and fish is more limited than that for the 

terrestrial vertebrates. This needs to be rectified, not only to understand the biodiversity of the 

bioregion but also because of their importance as food resources for vertebrate species both 

within and outside the DRP and as indicators of ecosystem health. There are 30 fish species 

known from the DRP and three of these have been listed as threatened by the Fisheries 

Management Act, 1994 (NSW). 

High fire frequency, anthropogenic climate change, clearing of native vegetation, predation 

by feral cats, foxes and Gambusia, competition and land degradation by feral goats and

abbits are listed as key threatening processes for the DRP under the TSC Act and/or the 

EPBC Act. There have also been preliminary determinations to list river regulation and 

competition by feral honeybees as key threatening processes. Weeds and pest animal species 

also pose significant threats to biodiversity within the DRP. 

Implications for biodiversity conservation management 

Conservation reserves make up less than one percent of the DRP bioregion and these do not 

cover the full range of plant communities present. Off-reserve conservation initiatives include 

the development of Catchment Management Plans, River Management Plans, Groundwater 

Management Plans, Regional Vegetation Management Plans and the declaration of Wildlife 

Refuges and Voluntary Conservation Agreements. There is insufficient information to define 

areas of biological significance but the major wetlands and Artesian Springs require 

consideration. The significance of the rivers as corridors for movement of wildlife also 

requires assessment. 

This bioregion covers a large area within NSW for which the floristic and faunal records and 

vegetation mapping is inadequate. Further survey and assessment must be based on the gaps 

highlighted in both this report and in the accompanying data audit and gap analysis report. It 

is also important to define the internal landscape variation using refined province or land 

system boundaries and to ensure an even coverage of survey effort across these sub-regions 

rather than using mapsheet analysis. Recommendations for further work emerging from the 

background information reviewed and the gap analysis study are listed at the end of each part 

of this report.

16/08/02 Darling Riverine Plains Bioregion Background Report 

1 INTRODUCTION 

1.1 THE BACKGROUND REPORT 

The aim of this report is to collate and synthesise the available abiotic and biotic information 

for the Darling Riverine Plains (DRP) Bioregion within New South Wales and to assess the 

current conservation status of the bioregion. The biotic information includes information 

about vegetation, flora, fauna, ecosystems, ecological processes and threatening processes. 

Simultaneously, a data audit and gap analysis is being undertaken in which the quality and 

completeness of the data will be assessed and inadequacies and gaps identified. These studies 

provide information which forms the basis of proposals for data collection and analysis of 

conservation values across the bioregion. Emerging from the information gathered are 

proposed recommendations for further work. This detailed information is required for 

regional conservation planning and the establishment of a protected area network (including 

formal reserves) and conservation management practices. 

The following conventions are used throughout this report. 

Abbreviations: 

DRP (Aus) - the total area of the Darling Riverine Plains bioregion (as defined by 

Thackway and Cresswell 1995); 

DRP - the portion of the DRP (Aus) in New South Wales; and 

DRP (Qld) - the portion of the DRP (Aus) in Queensland. 

Names for flora and fauna will be cited in the following ways: 

for birds, mammals (excluding bat species), invertebrates, and fish – common name 

followed by scientific name when first used, then common name only used throughout; 

and 

for reptiles, amphibians, bats and all flora – scientific name followed by common name 

(where available) when first used, then scientific name only used throughout. 

The naming authorities recognised and used in this report are as follows: 

for flora – Harden (1990-1993), Royal Botanic Gardens, Sydney (2001); 

for reptiles and amphibians – Cogger (2000); 

for birds – Simpson et al. (1999); and 

for mammals – Strahan (1995). 

14


1.2 THE DRP BIODIVERSITY CONSERVATION ASSESSMENT PROJECT 

This Background Report forms part of Stage 1 of the DRP Biodiversity Conservation 

Assessment Project. The recommendations for further work presented here together with the 

results of the data audit and gap analysis will be used to determine the content of the 

associated projects. 

1.2.1 Objectives of the DRP project 

The objectives of the DRP Biodiversity Conservation Assessment Project are to: 

compile appropriate bioregion-wide biotic and abiotic data for use by planners and land 

managers; 

identify bioregional conservation values for use in regional planning processes such as 

regional vegetation management planning, catchment management planning and river 

management planning; 

provide advice about appropriate conservation measures and management practices; 

provide advice about further detailed assessment needed for the creation of reserves; 

involve the community in information gathering and to present the findings in plain 

English; and 

establish long term monitoring sites that will allow ecological health to be assessed and 

the conservation management practices to be evaluated and reviewed. 

The two stages in the project (NPWS 1999a) are: 

Stage 1: Compilation and analysis of background information, broad data collection, 

development of broad conservation criteria and a biodiversity survey of sites selected 

to cover the ecological variation of the DRP. To undertake a preliminary analysis that 

identifies gaps in the data layers and establishes an understanding of environmental 

patterns and variation within the bioregion. 

Stage 2: Information collected from Stage 1 of this project will be reviewed and used to 

design a targeted survey program, detailed assessment of the conservation status of the 

region and possible modelling to provide more detailed information for use in the 

broader conservation assessment. Areas targeted for more detailed analysis may 

include areas of high conservation value and those considered under greatest threat. 

Stage 2 will be used to identify the processes and funding requirements needed to 

complete the Integrated Biodiversity Conservation and Assessment process across the 

whole bioregion. 

1.2.2 Funding for the DRP project 

The DRP Biodiversity Conservation Assessment Project is funded from two sources: 

under priority action 13 of the New South Wales State Biodiversity Strategy (SBS); and 

the Commonwealth Natural Heritage Trust (NHT). 

The SBS funding covers conservation assessment and vegetation mapping. The NHT funding 

covers community based nature conservation planning. SBS also funds long term monitoring 

sites established for invertebrate diversity assessment, a project conducted by the Australian 

Museum. A separate report will be produced for each project. 

15


1.2.3 Associated projects 

Figure 1.1 below shows how all aspects of the DRP Biodiversity Conservation Assessment 

Project are linked and the reports which shall be produced for this project. This background 

report is part of the initial stages of the project as shown in Figure 1.1. Each component of 

the project is outlined further in this section. 

BACKGROUND DOCUMENT 

(synthesis of pre-survey info on biota, 

state of environment etc.) 

Draft due Oct 2001 

Final draft due Jan 2002 

Final IBCA Review May 2002 

PROJECT REPORTS 

Data Audit and Gap Analysis 

current status of information 

Draft due Dec 2001 

Final draft due March 2002 

Biodiversity Survey 


Final draft due Mar 2002 

Community Technical Report 

Draft due Oct 2001, 

Final draft due June 2002 

Vegetation Mapping 


Final draft due June 2002 

Preliminary Conservation Assessment 

(incl. Technical Framework, 

conservation criteria, Focus on habitat 

/ indicators of habitat quality, bioregional 

boundaries – future work required) 

final draft due October 2002 

COMMUNITY REPORTS 

Community Report 

Draft due October 2001 

Final draft due Dec 2001 

Release date April 2002 

Cultural Community Report 

Draft Due Oct 2001 

Final draft due April 2002 

Further consultation / Workshops 

BIOREGIONAL STRATEGY 

Broad conservation priorities 

Possible conservation areas 

Draft outline due Jan 2002 for 

consultation, 

Draft due July 2002 

Final draft due October 2002 

FIGURE 1.1 REPORTS RESULTING FROM THE DRP BIODIVERSITY CONSERVATION 

ASSESSMENT PROJECT 

Data audit and gap analysis 

The information available on the ecology and biological diversity of the DRP is limited in 

detail and extent. This is a significant impediment to informed land use planning, 

conservation management and regional development. In this project existing data will be 

audited and evaluated in order to develop targeted studies that will fill gaps in the data. This 

includes collation of readily available environmental data and the establishment of a baseline 

for a more comprehensive and detailed assessment of the bioregion. The data audit process 

also involves the maintenance of a comprehensive database. 

A data audit of the western region of New South Wales for the Resource and Conservation 

Assessment Council (RACAC) included data relating to fauna, flora, geoscience, heritage, 

land, photography and imagery, vegetation and water (NPWS 1999c). The data were 

classified by bioregion and the DRP was found to have reasonable coverage of climatic and 

weather information, while vegetation, flora and fauna data are poor or unavailable. In 

general there is an incomplete coverage of all existing base data layers, a variation in methods 

of data collection, variable or unknown reliability of the records and a bias in collection 

locations. 

16


Vegetation mapping 

The aim of this project is to validate and integrate existing vegetation mapping. The 

resolution of the mapping area covered, methods used, type of information collected and 

currency of the data varies across the DRP. From this, targeted flora survey requirements will 

be defined and ecological and geographical patterns determined using a spatial analysis. Preand 

post-clearing vegetation maps of the bioregion, an inventory of vegetation communities, 

vascular plant communities and rare and threatened plant species, an assessment of the 

conservation status of vegetation communities and an understanding of the environmental 

influences on plant and vegetation distribution across the DRP will be provided. 

Biodiversity survey 

This project will develop an appropriate bioregion-wide biodiversity database and data layers, 

which will allow identification of priorities for further assessment, classification of biotic 

assemblages and habitats, areas of high biodiversity and conservation significance, 

identification of conservation management options and a technical report. An important 

component of this project is community participation in biodiversity surveys. 

Regional based nature conservation planning 

The aim of this project is ensure that any future bioregional plan for the Darling Riverine 

Plains incorporates best practices by providing opportunities for community participation and 

information exchange at all levels. It is designed to provide opportunities for all sectors of the 

community to assist with data collection and to provide fauna/flora records in a manner that 

can be used in the project. 

This will be done by providing training, expertise, opportunities, networks and incentives for 

cooperative partnerships with private landholders, local and state government, non 

government organisations, industry and other relevant management authorities involved in 

long term management of key areas for the conservation of biodiversity. This whole of 

landscape approach to biodiversity conservation and appropriate long term conservation 

management practices can be achieved through programs such as the Land for Wildlife 

scheme (ie Land for Wildlife property registration and support), wildlife refuges, voluntary 

conservation agreements, Farming For The Future, Bushcare and the Native Vegetation 

Conservation Act, 1997 (NSW). 

Consultation with the Aboriginal community 

For this project Aboriginal communities will be consulted about traditional or ecological 

knowledge and conservation issues the communities consider important. This may include 

field trips with members of the Aboriginal community to biodiversity survey sites or other 

locations, collecting information about past and present species distribution, habitat 

requirements and the impact of changes to ecosystems. 

Conservation assessment 

This assessment will identify highly significant areas and features of the DRP and provide 

advice on appropriate conservation measures. The report will focus on habitat definition, 

indicators of habitat health and the definition of the bioregional boundaries. It will outline the 

technical framework of the project and future work required. 

17


Bioregional strategy 

This strategy will use existing information and that generated by the project to prepare a 

bioregional conservation strategy. This will be developed through consultation with the 

broad network established by the NHT-funded project and public comment on the strategy. 

1.3 THE DARLING RIVERINE PLAINS BIOREGION 

1.3.1 Location and area 

The DRP (Aus) bioregion was originally defined by Thackway and Cresswell (1995) in their 

Interim Biogeographic Regionalisation of Australia as having ‘Alluvial fans and plains; 

summer/winter rainfall in catchments, including occasional cyclonic influence; grey clays; 

woodlands and open woodlands dominated by Eucalyptus species.’ 

The total area of this bioregion is 10 550 000 hectares with 88% located within NSW and two 

small lobes extending into Queensland. It is surrounded by six other bioregions: to the east is 

the Brigalow Belt South, to the north-west the Mulga Lands, to the south and south-west the 

Cobar Peneplain, Murray Darling Depression and Broken Hill Complex, and the New South 

Wales South Western Slopes in the Narromine area (Map 1). The bulk of the bioregion 

extends from east of Boggabilla to Weilmoringle on the Queensland border, south almost to 

Peak Hill and west to Nyngan and Bourke. South west from Bourke it becomes a narrow 

riverine corridor along the Darling River to the Menindee overflow lakes. 

The New South Wales portion of the DRP covers approximately 9 255 000 hectares. It 

includes the lower reaches and alluvial fans of the Bogan, Macquarie, Castlereagh, Namoi, 

Barwon, Culgoa, Bokhara, Narran, Gwydir and MacIntyre Rivers and the Darling River 

corridor from Bourke to the southern edge of the Menindee Lakes (Map 2). The alluvial fans 

form extensive fertile plains. 

The DRP (QLD) has been described by Sattler and Williams (1999) as forming two distinct 

provinces of the Brigalow Belt South Bioregion. These are the Balonne-Culgoa Fan (Province 

35) that contains extensive quaternary alluvial sediments along the Balonne and Culgoa 

Rivers and the predominantly alluvial plains and associated riverine landforms of the 

MacIntyre-Weir Fan (Province 36) (refer to section 2.6.1 for an outline of the provinces 

described by Morgan and Terrey (1992) within the bioregion in New South Wales). 

1.3.2 Human history 

Aboriginal and cultural heritage 

Aboriginal people have occupied this continent for approximately 55 000 years and their 

connection with this continent dates back to far earlier times, to the time of the creation itself. 

The Aboriginal people of Australia represent one of the oldest continuously living cultures in 

the world. 

Approximately 3 000 people occupied the Barwon-Darling area prior to European settlement. 

The river tribes of the DRP settled along the main rivers during the summer months, moving 

to regular campsites on drier country in the winter months (Dargin, 1976). 

18


The DRP covers land belonging to several Aboriginal nations including the Wiradjuri, 

Gamilaroi, Yullaroi, Murriwarri, Ngiyampaa/Wongaibon and Baarkinji. For Aboriginal 

people, the land, waterways, flora, fauna and the skies, are central to their traditional lifestyles 

and cultural beliefs and there are many areas of cultural significance within the DRP (NPWS 

undated; Dargin 1976). 

In 1836 white settlement extended to the Barwon-Castlereagh River junction. Traditional life 

was disrupted, with the introduction of stock and agriculture and many Aboriginal women 

being forced to live with white stockmen (NPWS undated; Dargin 1976). Violent conflicts 

between the Aboriginal and white people occurred throughout the area during the 1880s 

(Dargin 1976; Butlin 1983). The dwindling Aboriginal population of the area was further 

decimated by the European-introduced small pox and venereal disease. Outbreaks of small 

pox within the Aboriginal populations of the Darling area lead occurred between 1820 and 

1830, causing many deaths. Rapid population decline from disease, which mainly affected 

the old and young, coupled with venereal diseases, which caused sterility in some, greatly 

affected the recovery rate of the Aboriginal population of the region (Butlin 1983; NPWS 

2000). 

As white settlement of the area continued to expand, the newly appointed Protector of 

Aborigines called a census of Aboriginal people in 1882. The results of this census for the 

region found that a total of approximately 440 people of Aboriginal descent were living in 

Walgett, Brewarrina and Wilcannia (Dargin 1976). 

The Brewarrina area was particularly important as one of the great intertribal meeting places 

of eastern Australia where Aboriginal elders deliberated on policies aimed at maintaining 

balance between tribes and their environment. Ceremonial grounds, burial areas and 

extensive stone flaking are the only remaining evidence of these meetings (Dargin 1976). 

The late 1880s saw the almost total demise of traditional Aboriginal life in the region (Dargin 

1976; NPWS undated). The last traditional initiation ceremony occurring at the bora grounds 

at Collymongle, approximately 18km east-north-east of Collarenebri (Dargin 1976). 

Many Aboriginal sites and areas of significance in the DRP have been mapped and include 

physical and non-physical or spiritual sites. Physical remains of earlier Aboriginal occupation 

as indicated by the presence of stone tools, rock art, rock peckings, rock engravings, scarred 

and carved trees are protected under the National Parks and Wildlife Act, 1974 (NSW) and 

many are still being located. The spiritually important sites are more difficult to classify and 

map but can include a mountain range or a waterway incorporated in the creation stories, 

totemic animals or plants. These features of the landscape continue to be used by Aboriginal 

people. 

Known and mapped sites of significance to Aboriginal people are spread throughout the DRP, 

with a high concentration in the Darling riverine corridor south of Wilcannia (Map 3). Two 

areas of high significance to the Ngiyampaa/Wongaibon people are the Brewarrina fish traps 

and Mt Grenfell. There are also other highly significant areas to the Ngiyampaa/Wongiabon 

and other nations within the DRP but many of these cannot be revealed to the broader 

community. 

19


European settlement of the bioregion 

The DRP has been significantly modified since European settlement that began after the early 

exploration along the rivers in 1817. John Oxley was the first European to the region, naming 

and crossing the Castlereagh River in 1818. George Clarke, an escaped convict, traversed the 

northern part of the DRP with the Kamilaroi people between 1826 and 1831. When 

recaptured, he reported to the acting governor a great inland river. This prompted Sir Thomas 

Mitchell to investigate and he found the Barwon River in 1832 (Fairfax 2001). European 

explorers, Charles Sturt and Hamilton Hume first reached the Darling River in 1829. 

River frontage properties along the Barwon and Macquarie Rivers were taken up by the 

1840s and extended to the Darling River in the 1850s. To begin with, the runs were unfenced 

and the lack of water restricted stock movement with only spasmodic occupation of the 

surrounding lands after rain. This pattern of occupation and development changed 

significantly in the 1870s and 1880s with the construction of wells, bores and tanks enabling 

the stock runs to expand permanently into the dryland. At the same time, good seasons and a 

strong demand for wool caused an almost complete change from cattle to sheep and a strong 

increase in sheep numbers. Fencing of stock runs began in this period along with the use of 

timber for construction of dwellings, firewood, lining of well and mine shafts and for stock 

fodder which led to the clearing of timber from large areas, especially in the Western 

Division. By the 1890s the massive build up of stock, invasion of rabbits and drought led to 

the broad scale and profound environmental degradation of the Western Division. 

The river boat trade was a major contributing factor to the development of the DRP with 90 

paddle steamers using the Darling River by 1890 (Outback NSW 2001a). Captain William 

Randall took the first riverboat up the Darling River in 1859 to the location where Brewarrina 

now stands. This was the beginning of the river trade at Brewarrina and Bourke. Bourke 

became the major port along the Darling River from 1860 to 1885. Menindee, Wilcannia and 

Brewarrina were also important river ports along the Darling River (Back O’Bourke 2001; 

Australian Museums and Galleries Online 2001). 

Menindee was the first town established on the Darling River (in the 1850s but was not 

gazetted until 1863), with Bourke being surveyed in 1862, Brewarrina being officially 

declared a town in 1863 and Wilcannia officially notified as a township in 1866 (renaming 

the town formerly known as Mount Murchison). These townships were developed to service 

the river trade (Outback NSW 2001b; Australian Museums and Galleries Online 2001). 

In 1859, Vincent Dowling, the pioneer station builder of the Bourke area, brought his wife 

(the first white woman in the area) out to the Darling. In 1878 the Artesian Basin was tapped 

for the first time at Kallara and Kerbree Stations near Bourke. The cotton industry began in 

1966 in the Bourke district (Back O’Bourke 2001; Outback NSW 2001b). 

A number of important historic sites of early European settlement exist. It is beyond the scope 

of this report to document these sites in detail but in addition to the more obvious sites of 

cemeteries and settlements there are graves scattered across the landscape. For example, the 

graves of the first settlers in the Macquarie Marshes area, George Gibson and Henry Wage 

are still located there and are a designated historic site within Warren Shire. The presence of 

marked European survey trees is evidence of early exploration of the area. 

20


Land use 

The most common land use across the bioregion is grazing, with average livestock densities 

of 0.85 animals/ha. Stock routes to the main markets were developed in the 1880s and these 

crossed the DRP from south to north, up the Darling River from Wilcannia to Bourke, across 

to Hungerford and over the border to Queensland. This major route also connected the south 

of the bioregion to others heading east to Dubbo and south to Deniliquin and Echuca. By the 

1890s a vast network of stockroutes spanned the DRP (McKnight 1977). 

Irrigated and dryland cropping is a more recent land use, but it is becoming more extensive. 

The cotton industry began with the construction of the Keepit Dam in 1960, with 20 000 ha of 

cotton planted in the Narrabri / Wee Waa area by 1968/69, increasing to 48 000 ha by 

1989/90 (NWCMC 1996). The following land use descriptions by province have been drawn 

primarily from Morgan and Terry (1990) (see section 2.6.1 for a description and Map 21 for a 

map of the provinces). 

In the Bogan-Macquarie Province grazing is the dominant land use with dryland and 

irrigated cropping becoming more significant in the south. Stock levels in the region range 

from six dry sheep equivalents per hectare (dse) in the pastoral eastern area, to 0.25 dse in the 

west (Macquarie 2100 Plan 1999). 

Wheat, cotton, beef and wool dominate in the Narromine to Collie, Bogan River and Merri 

Merri Creek area with cropping increasing since livestock returns were reduced in 1994-5. 

Total gross value of cropping in this region was $260 million in 1996 to 1997 and livestock, 

$50 million, in the same period. The area cultivated for cotton production increased by 400% 

from 1981 to1992 and 60% of the cotton is grown within five kilometres of the Macquarie 

River (Macquarie 2100 Plan 1999). 

The Castlereagh-Barwon Province is the most intensively developed with rapid growth in 

the cropping industry. Dryland cropping is widespread and irrigated crops cover large areas 

near Wee Waa and Moree in the east and, to a lesser extent, near the Barwon River and 

Moomin Creek. In the Border Rivers region, which includes the northern portion of this 

province, 57 000 ha were irrigated for cotton, producing an income of approximately $200 

million per annum and 13 500 ha irrigated for summer crops such as lucerne (DNR & DLWC 

2000). Grazing is also a significant land use in this province. 

Throughout the remainder of the bioregion, land use is dominated by grazing but in the 

Culgoa-Bokhara and Warrambool-Moonie Provinces substantial areas have been cultivated 

for dryland cropping and this is increasing. Narran Lakes (Narran-Lightning Ridge 

Province) are also used for lakebed cropping and extensive clearing has recently occurred in 

the Collarenebri Interfluve Province. Horticulture is an expanding industry in the 

Menindee Province. 

The fertility and higher moisture levels of the wetlands within the DRP has frequently 

resulted in a concentration of agricultural activities in these areas. The Gwydir Wetlands were 

mostly used for wool production during the early part of the century. By the 1970s beef cattle 

were the mainstay of the grazing industry. The crash of beef prices in the early 1970s when 

wheat prices were buoyant, resulted in many landholders clearing extensively for cultivation 

cropping but in the 1980s sheep and cattle re-emerged as important industries. Dryland 

cropping is still important but the produce has diversified to include barley, oats, chickpeas, 

safflower and canola. Irrigated cotton production is important upstream from the wetlands 

21


around Moree since the construction of Copeton Dam, and there has been pressure to build 

another dam to allow for irrigation in the wetlands (Keyte 1994; NWCMC 1996). 

1.3.3 Land tenure and administrative boundaries 

Land tenure 

The current land tenure of the DRP is shown in Map 4. 

Crown lands 

The available data on Crown lands (Map 4) (from Crown Lands Information Database, 

DLWC) at the time of writing is not totally accurate because there is considerable spatial 

overlap between classifications and a lack of data verification and updated information in the 

database. There are also inconsistencies in the data with some, but not all classifications 

coinciding. Leasehold land within the occupies approximately 4 628 000 ha, 50% of the 

bioregion. Crown reserves include travelling stock reserves, transport corridors, National 

Parks, Nature Reserve and State Forests that cover an estimated 9.5% (879 350 ha) of the 

bioregion (Map 4). 

Freehold 

The remaining 40.5% (3 748 800 ha approximately) of the DRP is freehold land, located 

mainly in the south and east of the bioregion (Map 4). 

National Parks and Wildlife Service estate 

Two national parks and six nature reserves cover 0.89% of the DRP. Two recent acquisitions 

by the NPWS, Mount Murchison, and Tillpilly Stations (45 km and 100 km north-east of 

Wilcannia respectively), partially fall within the DRP and are yet to be formally declared. 

Another ungazetted area adjacent to Narran Nature Reserve is also part of the NPWS estate 

within the DRP. These ungazetted areas of NPWS estate increase the total area of by NPWS 

estate within the DRP to 1.13% (Map 4). The largest reserves are Culgoa National Park in the 

far north west of the DRP, and Kinchega National Park in the far south west of the bioregion 

(Table 1.1). 

Table 1.1 NPWS estate in the DRP 

Name Hectares % within Protected area management category under the International 

within DRP DRP Union for the Conservation of Nature (IUCN) 

Kinchega National Park 37 861 86% II – national park managed for ecosystem protection and recreation 

Culgoa National Park 20 918 95% II – national park managed for ecosystem protection and recreation 

Macquarie Marshes Nature 18 192 100% IV – habitat / species management area managed for conservation 

Reserve 

through management intervention 

Narran 

Reserve 

Lake Nature 4 527 100% Ia – strict nature reserve managed mainly for science 

Midkin Nature Reserve 359 100% Ia – strict nature reserve managed mainly for science 

Boronga Nature Reserve 195 100% Ia – strict nature reserve managed mainly for science 

Boomi Nature Reserve 156 100% Ia – strict nature reserve managed mainly for science 

Boomi 

Reserve 

West Nature 149 100% Ia – strict nature reserve managed mainly for science 

Mt Murchison ungazetted 13 677 30% not assigned 

Tillpilly ungazetted 5 048 21% not assigned 

Narran Lake ungazetted 3 691 100% not assigned 

Total area within DRP 104 773 1.13% 

22


State Forests of NSW estate 

Twenty-two State Forests occur within, or partially within, the DRP (Map 4). These forests 

cover an estimated 13 900 ha, or 0.15% of the total area of the bioregion. Each State forest, 

and the area occurring within DRP, is listed in Table 1.2. They are all located in the southern 

part of the DRP, and in a narrow belt of ‘Monkey scrub’ (Eucalyptus chloroclada-Callitris 

glaucophylla community on a relict channel of the Castlereagh River) running to the north 

west of Gulargambone. 

The Sandgate Flora Reserve within the DRP has been exempted from mining and is therefore 

equivalent to IUCN I-IV. Timber harvesting and grazing by domestic stock are not permitted 

in flora reserves unless specified in a working plan. To date State Forests within the DRP 

have not been assigned IUCN categories. However, parts of these forests are likely to qualify 

for IUCN categories of I-IV under future Forest Management Zoning and initiatives 

associated with habitat or species management. 

Table 1.2 State Forests in the DRP 

State Forest Hectares intersecting DRP % within DRP 

Sandgate Flora Reserve 16 100% 

Gilwarny State Forest 3 452 100% 

Pilliga West State Forest 2 808 2% 

Tallegar State Forest 1 601 100% 

Narraway State Forest 881 100% 

Sandgate State Forest 780 100% 

Bourbah State Forest 623 100% 

Merrinele State Forest 536 100% 

Cowal State Forest 504 100% 

Tenandra State Forest 490 100% 

Nebea State Forest 361 100% 

Warrie State Forest 295 100% 

Wingadee State Forest 283 100% 

Tailby State Forest 196 22% 

Mellerstain State Forest 194 100% 

Merri Merri State Forest 191 100% 

Gilgandra State Forest 190 100% 

Carrabear State Forest 174 100% 

Holybon State Forest 125 100% 

Berida State Forest 68 100% 

Eringanerin State Forest 58 88% 

Girilambone State Forest 53 100% 

Gin Gin State Forest 39 100% 

Total area within DRP 13 916 0.15% 

23


Administrative boundaries 

In addition to crossing a State border, the DRP (Aus) bioregion is divided by a number of 

other administrative boundaries. Among the more significant of these are the DLWC Regions 

(Map 9) that have influenced the coverage of research throughout the bioregion. Research 

carried out in the Western Division (Far West Region, Table 1.4, Map 9) has frequently 

differed in content and comprehensiveness from that undertaken in the regions to the east. 

New South Wales State government 

Four State Government electorates (Table 1.3, Map 6) intersect the DRP. Most of this 

bioregion is in the Electorate of Barwon (79%). 

Table 1.3 State government electorates within the DRP 

Electorate Area intersecting DRP (ha) % electorate % DRP 

Barwon 7 351 190 63% 79% 

Murray – Darling 1 758 506 5% 19% 

Dubbo 130 234 8% 1% 

Northern Tablelands 13 432 0.4% 0.1% 

Department of Land and Water Conservation administrative boundaries 

The DRP lies within three Department of Land and Water Conservation (DLWC) Regions 

(Table 1.4, Map 9). 

Table 1.4 DLWC regions within the DRP 

DLWC Region Area intersecting DRP (ha) % region % DRP 

Far West 3 993 322 12% 43% 

Central West 3 164 952 23% 34% 

Barwon 2 093 817 23% 23% 

National Parks and Wildlife Service administrative boundaries 

99.9% of the DRP falls under the jurisdiction of the Western Directorate of NPWS, with the 

remaining 0.1% being within Northern Directorate (Map 7). Table 1.5 shows NPWS 

Directorates, Regions and Areas within these Directorates, and the area of the DRP covered 

by each. Narrabri Area Office has jurisdiction over 39% of the DRP, with Coonabarabran and 

Cobar Area Offices covering 23% and 25% respectively. 

Table 1.5 NPWS administrative boundaries within the DRP 

Directorate Region Area Area intersecting % NPWS % DRP 

DRP (ha) 

Area 

Western Northern Plains Narrabri 3 590 790 56% 39% 

Coonabarabran 2 117 223 56% 23% 

Upper Darling Cobar 2 281 882 19% 25% 

Far West Broken Hill 854 947 9% 9% 

Central West Lachlan 394 384 10% 4% 

Northern Northern 

Tablelands 

Glen Innes West 13581 1% 0.1% 

24


State Forests of NSW administrative boundaries 

Eight SFNSW Management Areas lie partially within the DRP (Table 1.6, Map 8). The 

Walgett Management Area covers the largest percentage of the DRP (41%). 

Table 1.6 SFNSW administrative boundaries within the DRP 

SF Management Area Area intersecting DRP (ha) % SF Management % DRP 

Walgett 3 828 033 

Area 

99% 41% 

Pilliga 1 728 155 44% 19% 

Unincorporated 1 214 062 7% 13% 

Dubbo 1 070 150 35% 12% 

Gilgandra 943 077 65% 10% 

Mildura 302 673 3% 3% 

Inverell 119 265 6% 1% 

Forbes 30 618 1% 0.3% 

Condobolin 20 053 0.4% 0.2% 

Rural Lands Protection Boards administrative boundaries 

Sixteen Rural Lands Protection Boards (RLPBs) intersect the DRP, with the Walgett RLPB 

covering 27% of the DRP (Table 1.7, Map 10). Other RLPBs that are mostly within the DRP 

are Brewarrina, Coonamble and Moree. 

Table 1.7 RLPBs within DRP 

RLPB Area intersecting DRP (ha) % RLPB %DRP 

Walgett 2 471 851 96% 27% 

Brewarrina 1 293 744 87% 14% 

Coonamble 1 121 902 99% 12% 

Moree 1 010 819 63% 11% 

Nyngan 798 382 45% 9% 

Dubbo 538 118 31% 6% 

Wilcannia 515 072 11% 6% 

Bourke 506 480 13% 5% 

Broken Hill 339 875 8% 4% 

Narrabri 299 695 24% 3% 

Cobar 142 876 4% 2% 

Warialda 128 837 10% 1% 

Coonabarabran 49 447 4% 1% 

Molong 18 836 2% 0.2% 

Condobolin 16 871 1% 0.2% 

Wentworth 539 0.02% 0.01% 

Regional Vegetation Committees administrative boundaries 

Of the seven Regional Vegetation Committees (RVCs) which cover portions of the DRP, the 

Lower Macquarie - Castlereagh and Walgett RVCs cover the largest land area within the 

bioregion (50%) as indicated in Table 1.8 and Map 11. 

25


Table 1.8 RVCs within the DRP 

RVC Area intersecting DRP 

(ha) 

% RVC % DRP 

Lower Macquarie – Castlereagh 2 470 760 72% 27% 

Walgett 2 162 767 97% 23% 

Brewarrina 1 400 409 73% 15% 

Moree 1 120 193 63% 12% 

Nth Lachlan – Bogan 301 993 13% 3% 

Narrabri – Coonabarabran – Coolah 298 615 12% 3% 

Mid – Lachlan 18 948 1% 0.2% 

Water Management Committee administrative boundaries 

Water management committees established under the Water Management Act, 2000 whose 

coverages fall within the DRP are listed in Table 1.9. 

Table 1.9 Water Management Committees within the DRP 

(DLWC 2001a) 

Water Management Committee 

Gwydir River (Regulated) River Management Committee 

Namoi Regulated River Management Committee 

Gwydir Unregulated River Management Committee 

Namoi Unregulated River Management Committee 

Macquarie – Cudgeon (Regulated) River Management Committee 

Central West (Unregulated) River Management Committee 

Barwon-Darling River Management Committee 

Great Artesian Basin Groundwater Management Committee 

Gwydir Groundwater Management Committee 

Macquarie Groundwater Management Committee 

Namoi Groundwater Management Committee 

Border Rivers Unregulated River and Groundwater Management Committee 

Catchment Management Board administrative boundaries 

Six Catchment Management Boards (CMBs) have jurisdiction over sections of the DRP 

(Table 1.10, Map 12) with Central West and Western CMBs covering 72% of the DRP. All 

CMBs within NSW are preparing Catchment Management Plans or Blueprints. 

Table 1.10 CMBs within the DRP 

CMB Area intersecting DRP (ha) % CMB % DRP 

Central West 3 563 432 39% 38% 

Western 3 190 730 14% 34% 

Gwydir 910 366 34% 10% 

Namoi 779 814 19% 8% 

Border Rivers 522 455 22% 6% 

Lower Murray Darling 271 354 4% 4% 

26


Local Government boundaries 

The DRP is divided between 18 Local Government areas, covering 99% of the bioregion 

(Table 1.11, Map 13). The remaining 1% of the DRP is not under the jurisdiction of any local 

Government and is shown as unincorporated. 

Table 1.11 Local Government areas which intersect the DRP 

LGA Area intersecting DRP (ha) % LGA % DRP 

Walgett 2 162 767 97% 23% 

Brewarrina 1 400 409 73% 15% 

Moree Plains 1 120 193 63% 12% 

Warren 1 069 140 100% 12% 

Coonamble 908 063 91% 10% 

Central Darling 753 005 14% 8% 

Bourke 458 674 11% 5% 

Narromine 358 423 68% 4% 

Narrabri 296 398 23% 3% 

Bogan 284 772 20% 3% 

Cobar 143 013 3% 2% 

Gilgandra 135 135 28% 1% 

Unincorporated area 103 325 1% 1% 

Parkes 18 948 3% 0.2% 

Lachlan 17 221 1% 0.2% 

Inverell 14 200 2% 0.2% 

Yallaroi 9 576 2% 0.1% 

Coonabarabran 2 217 0.3% 0.02% 

Wentworth 752 0.03% 0.01% 

Local Aboriginal Land Council administrative boundaries 

Aboriginal Land Council boundaries within the DRP are shown on Map 5. Twenty-seven 

Aboriginal Land Councils (ALC) and an unincorporated area exist within the DRP. Local 

ALCs that cover the largest sections of the DRP are Walgett, Brewarrina, Collarenebri, 

Quambone and Coonamble (Table 1.12), covering 39% of the DRP. Collarenebri, 

Quambone, Lightning Ridge, Trangie, Warren-Macquarie and Goodooga LALCs all fall 

entirely within the DRP. 

27


Table 1.12 Aboriginal Land Councils within the DRP 

ALC Area 

(ha) 

intersecting DRP %ALC %DRP 

Walgett 1127 695 93.6% 12% 

Brewarrina 881 442 89.5% 10% 

Collarenebri 847 748 100.0% 9% 

Quambone 765 698 100.0% 8% 

Coonamble 732 096 96.1% 8% 

Lightning Ridge 498 545 100.0% 5% 

Mungindi 484 517 98.4% 5% 

Wilcannia 473 773 13.2% 5% 

Menindee 456 183 20.1% 5% 

Warren-Macquarie 436 320 99.6% 5% 

Nyngan 294 483 18.8% 3% 

Goodooga 274 486 99.9% 3% 

Nulla Nulla 262 499 21.4% 3% 

Wee Waa 261646 73.1% 3% 

Weilmoringle 219 042 49.8% 2% 

Winbar 203 898 17.6% 2% 

Toomelah 189 855 20.9% 2% 

Peak Hill 170 015 17.4% 2% 

Moree 141 622 14.1% 2% 

Gilgandra 110 141 16.2% 1% 

Trangie 109 059 100.0% 1% 

Unincorporated 86 495 3.5% 1% 

Narromine 71 737 43.7% 1% 

Pilliga 16 858 4.9% 0.2% 

Narrabri 13 750 2.7% 0.1% 

Murrawari 13 509 1.7% 0.1% 

Condobolin 13 002 0.8% 0.1% 

Coonabarabran 755 0.1% 0.01% 

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2 ABIOTIC FEATURES 

2.1 INTRODUCTION 

In this section the climate, geology, topography, soils and hydrology of the DRP are 

described to provide a basis for mapping and predicting the distribution and stability of plant 

communities, habitats and species distributions. Predictive distributions are essential as 

survey cannot cover the entire land surface. This bioregion is strongly influenced by water 

systems and the hydrological parameters are crucial in the biological assessment of the 

region. 

The effect of human activities, particularly clearing and agricultural activities also need to be 

understood in order to assess the changes to plant and animal distribution patterns, population 

viability and provenance, water quality and the conservation protocols required. Activities 

within the DRP can have an impact on flora and fauna outside the bioregion, for example, the 

disruption of migration routes for migratory vertebrate species or the loss of migratory 

invertebrate species through control of larval stages in agricultural areas. Activities within 

the DRP can also impact on downstream riverine health, water supply and water quality. 

Consideration of abiotic factors is important in the development of a meaningful subdivision 

of the Bioregion into smaller, manageable units. Boundaries previously defined within the 

DRP are outlined in this section. 

2.2 CLIMATE 

Almost all of the DRP lies within the semi-arid zone of New South Wales, except for a small 

portion of the eastern edge that extends into the temperate zone. The semi-arid zone covers an 

extensive area and in order to evaluate the climatic influence on the ecological processes of 

that area the climatic data for six meteorological stations across the bioregion are used in the 

following analysis (Table 2.1, Australian Meteorological Bureau). 

Table 2.1 DRP meteorological stations used in this analysis 

Town Location within DRP Latitude Longitude Elevation Years of 

(m) 

records 

Moree north-east 29.50 S 149.90 E 207 86 

Mungindi northern NSW border 28.98 S 148.99 E 160 113 

Walgett central 30.04 S 148.12 E 133 121 

Trangie south-east boundary 32.03 S 147.98 E 219 102 

Bourke north-west at the beginning of the 30.09 S 145.94 E 106 129 

Darling corridor 

Menindee south-western on the Darling River 

corridor 

32.40 S 142.42 E 61 124 

29


Variation in temperature and rainfall across the bioregion has also been modelled from the 

digital elevation model. The mapping shows that the variation in climatic variables is not 

affected by variation in local relief. 

2.2.1 Rainfall: temporal and spatial variation 

Most of the bioregion occurs within the summer rainfall region of New South Wales, with 

higher and more reliable rainfalls occurring in the east. The mean monthly rainfall ranges 

from about 60 mm in the east of the bioregion to 15 mm in the west and along most of the 

Darling River (Map 14). At the six meteorological stations, mean annual rainfall ranges from 

578.6 mm at Moree to 508.3 mm at Mungindi, 504.8 mm at Trangie, 477.8 mm at Walgett, 

355.1 mm at Bourke and 243.7 mm at Menindee (Bureau of Meteorology 2001). These mean 

values, however, mask the fact that the rainfall in the bioregion is highly variable in 

frequency and intensity and is generally unreliable. There are occasional periods of intense 

rainfall, which are often the products of deep extra-tropical depressions. Large portions of the 

bioregion also experience prolonged periods of no rainfall. 

The annual rainfall recorded at Bourke from 1871, graphed on Figure 2.1, illustrates this 

variability, with annual total rainfall ranging from about 80mm to 850mm. This variability is 

also demonstrated by the mean and first and ninth deciles calculated for the Bourke’s monthly 

rainfall averages (Figure 2.2). The first decile is the rainfall amount not exceeded by the 

lowest 10% of rainfall events. The ninth decile is the rainfall amount exceeded by the highest 

10% of rainfall events. The first and ninth decile are measured to give the ‘normal’ rainfall 

range (that which 80% of all rainfall events falls within). The rainfall at Mungindi in the 

north east of the bioregion has a more definite summer pattern with January and February 

being the wettest months. The range between the first and ninth deciles is also greatest for 

those months (Figure 2.3). This contrasts with Menindee in the southwest (Figure 2.4) and 

Trangie in the southeast (Figure 2.5) where there is no evidence of summer dominance in the 

rainfall although the range between the first and ninth deciles is greatest in December and 

January. Monthly means and ranges, which illustrate the degree of rainfall variability, have 

also been calculated for Walgett in the centre of the bioregion (Figure 2.6). The distribution 

and intensity of rainfall is also illustrated by median monthly rainfall (Figure 2.7) and mean 

monthly rain days (Figure 2.8) (Bureau of Meteorology 2001). 

Mean monthly rainfall and mean monthly rainfall graphs for each of these weather stations 

across the DRP are shown in Appendix A. 

30

ainfall (mm) 

900 

800 

700 

600 

500 

400 

300 

200 

100 


0 

1871 

1877 

mm 

120 

100 

80 

60 

40 

20 

0 

1883 

1889 

1895 

1901 

1907 

Bourke mean annual rainfall 

1913 

1919 

1925 

1931 

Figure 2.1 Annual rainfall records for Bourke 1871-1999 

Bourke mean monthly rainfall 

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec 

month 

Figure 2.2 Bourke mean monthly rainfall and range between first and ninth decile 

(Bureau of Meteorology 2001) 

1937 

year 

1943 

1949 

1955 

1961 

1967 

1973 

1979 

1985 

1991 

31


mm 

160 

140 

120 

100 

80 

60 

40 

20 

0 

Mungindi mean monthly rainfall 


month 

Figure 2.3 Mungindi mean monthly rainfall and range between first and ninth decile 


mm 

70 

60 

50 

40 

30 

20 

10 

0 

Menindee mean monthly rainfall 


month 

Figure 2.4 Menindee mean monthly rainfall and range between first and ninth decile 


32


mm 

140 

120 

100 

80 

60 

40 

20 

0 

Trangie mean monthly rainfall 


month 

Figure 2.5 Trangie mean monthly rainfall and range between first and ninth decile 


mm 

160 

140 

120 

100 

80 

60 

40 

20 

0 

Walgett mean monthly rainfall 


month 

Figure 2.6 Walgett mean monthly rainfall and range between first and ninth decile 


33


mm 

50 

45 

40 

35 

30 

25 

20 

15 

10 

5 

0 

median monthly rainfall 


month 

Trangie Bourke Walgett Menindee Mungindi Moree 

Figure 2.7 Median monthly rainfall for weather stations across the DRP 


days 

7 

6 

5 

4 

3 

2 

mean monthly raindays 


month 


Figure 2.8 Mean monthly rain days recorded across the DRP 


34

1500 

1000 

500 

0 

-500 

-1000 

-1500 

-2000 

-2500 


Long term rainfall variation 

Trends in available moisture resulting from the annual variation in rainfall are determined by 

calculating the Cusum (cumulative residual mass) curves for Menindee, Mungindi, Trangie, 

Walgett and Bourke. These curves (Figure 2.9) indicate that the rainfall was high throughout 

the 1880s and 1890s but there was a steady decrease from about 1900 until 1948 with a 

resultant moisture deficit throughout the bioregion. The severity and timing of this deficit 

varied between the five locations. Since about 1950, the moisture availability generally shows 

an upward trend although this was delayed until 1974 at Menindee and was not sustained at 

Trangie from 1960 to 1974. 

Cummulative Sums for Rainfall 

Menindee Mungindi Trangie Walgett Bourke 

Figure 2.9 Rainfall CuSums for five locations in the DRP 

The rainfall within the DRP does not have a regular annual cycle and plant growth and animal 

breeding patterns will be controlled by this long term pattern. This will influence the recovery 

rates of particular habitats and populations, with the current upward trend in the rainfall 

suggesting that conditions are favourable for potential re-establishment and recovery of 

populations. This may help explain the increased growth of the unpalatable native shrubs or 

‘woody weeds’ in parts of the bioregion. 

35


2.2.2 Winds 

Wind has a strong influence on rainfall and the degree of erosion that occurs in the area. 

Nyngan is subjected to dominant southerly winds and subdominant north-easterlies in January 

with a modal speed of 11 to 20 km/hr. This changes to dominant southerlies of between six 

and 10 km/hr in winter. At Walgett, north-easterlies are dominant in summer with modal 

speeds of one to five km/hr, while in winter this changes to light southerlies and southwesterlies 

(Wolfgang 1998). 

Figure 2.10 below shows that the mean monthly wind speed at 9am at Walgett, Menindee, 

Bourke and Mungindi varies from 13.1 km/hr at Menindee to 7.1 km/hr at Mungindi in 

December and from 7.4 km/hr at Menindee to 3.5 km/hr at Mungindi in June. Wind speeds 

of the DRP are greatest, on average, in the spring months at all stations, and lowest in the 

winter months at all stations. Only the weather stations with long term data have been 

included in Figures 2.10 and 2.11 (Bureau of Meteorology 2001). 

km/hr 

14 

12 

10 

8 

6 

4 

2 

mean monthly 9am wind speed 


month 

Bourke Walgett Menindee Mungindi 

Figure 2.10 Mean monthly wind speed at 9am 

36


km/hr 

14 

13 

12 

11 

10 

9 

8 

7 

mean monthly 3pm wind speed 


month 

Bourke Walgett 

Figure 2.11 Mean monthly wind speed at 3pm 

2.2.3 Temperature and evaporation 

In general terms the summers are mild to hot and winters mild to cool. Across the bioregion 

the average annual temperatures increase from 17ºC in the south east to 20ºC in the 

northwest. Most of the bioregion has an annual average temperature of 18 or 19ºC (Map 15). 

The average mean maximum temperature in January ranges from 33ºC to 36ºC and the 

average mean minimum temperature in July ranges from 3ºC to 6ºC (Bureau of Meteorology 

2001). The mean monthly maximum and mean monthly minimum temperatures are illustrated 

in Figure 2.12 and Figure 2.13. 

Average annual potential evaporation varies from 1 800 mm east of Trangie to 2 000 mm 

west of Bourke (Wolfgang 1998). Total average annual evaporation figures range from 2 131 

mm at Moree to 1 825 mm at Bourke. Mean daily evaporation has been recorded for the 

Bourke and Walgett weather stations within the DRP. These figures are graphed in Figure 

2.14 and range from 1.7mm at Walgett in June to 8.5 mm at Bourke in December (Bureau of 

Meteorology 2001). 

37


degrees celcius 

37 

35 

33 

31 

29 

27 

25 

23 

21 

19 

17 

15 

average daily maximum temperature 


month 


Figure 2.12 Mean monthly maximum temperatures 


degrees celcius 

22 

20 

18 

16 

14 

12 

10 

8 

6 

4 

2 

average daily minimum temperature 


month 


Figure 2.13 Mean monthly minimum temperatures 


38


mm 

10 

8 

6 

4 

2 

0 

mean daily evaporation 


month 

Walgett Bourke 

Figure 2.14 Mean daily evaporation at Walgett and Bourke 


2.3 GEOLOGY, TOPOGRAPHY AND SOILS 

2.3.1 Geological history 

The underlying lithology of the bioregion is almost entirely formed from transported 

sediments. Cainozoic (Quaternary) alluvium is found in 87% of the area and the Cainozoic 

lacustrine sediments and Cainozoic residual and aeolian sands are present in another 10% of 

the region. The lacustrine sediments are found along the lower reaches of the Macquarie and 

Castlereagh Rivers, and the aeolian sands are along the lower reaches of the Darling River 

with large areas associated with the Menindee overflow lakes. The broad lithology of the 

bioregion has been mapped (Map 16) and there has also been more detailed geological 

mapping of some portions of the bioregion. 

The Great Artesian Basin underlies the DRP bioregion, and this is divided into a series of 

smaller basins including the Surat and Euromanga Basins. The Great Artesian Basin consists 

of extensive Quaternary alluvial deposits associated with the Darling River. In a broader 

context, the entire Barwon-Darling basin can be described as a large intercratonic Cainozoic 

basin, which has been infilled with sediments derived mainly from continental alluvium 

(Thoms et al. 1995). 

In two areas the lithology reflects the underlying geology. In the north of the bioregion the 

coarse grained Cretaceous Surat Basin sandstone has not been covered by the more recent 

alluvium, forming the Lightning Ridge and the Collarenebri Interfluves. In areas of rolling 

downs and lowlands between the Culgoa and Barwon Rivers there are ridges and residuals of 

various rock types including conglomerate, sandstone, claystone, shale, siltstone, quartzite 

and granite. 

The geological history of the Walgett and Nyngan 1:250 000 map sheets, covering an area 

from Walgett in the north, south to Trangie, west to Girilambone and east to Coonamble, has 

39


been mapped and the formations are illustrated on Figure 2.15 (Watkins & Meakin 1996). 

The geological history and stratigraphy of the Macquarie-Bogan catchment is also described 

by Wolfgang (1998) and geological framework studies have been carried out in the Bourke 

region (Thoms et al. 1995). 

Figure 2.14 Geological history of the Nyngan and Walgett 1:250 000 map sheets 

(Watkins & Meakin 1996) 

40


2.3.2 Topography and geomorphology 

The alluvial deposits form extensive plains with slopes to the west and south of less than one 

degree and local relief rarely exceeds a few metres. The relief of the bioregion varies from 

40m above sea level (asl) in the southwest to 300m asl in the east. A digital elevation model 

(DEM) for the bioregion has been developed using two different levels of resolution (Map 

17). The coverage of the eastern third of the bioregion is at a 25 m grid size while the 

remainder is at 250 m. It would be preferable if the western portion was mapped at a finer 

resolution but this will not occur in the timeframe of this bioregional assessment. 

While more detailed modelling is desirable, its value would be limited by the generally low 

relief and little variation in elevation within the bioregion. Minor relief may be locally 

important (run on and run off areas), but these subtle changes may not be detected even at a 

25 m grid resolution. The Narrabri-Lightning Ridge and Collarenebri Interfluve provinces 

(see Section 2.6) are the areas most likely to benefit from more detailed modelling. 

The present day alluvial landscape of the bioregion is dominated by abandoned quaternary 

river systems, which are slightly higher than the modern river systems. Since the Pliocene (2- 

5 million years ago) the lower reaches of the tributaries of the Darling system have built 

outwash fans from material eroded from the eastern highlands. Watkins and Meakin (1996) 

defined four fluvial units in the alluvial landscape of the Nyngan and Walgett sheets: the 

Trangie formation, Carrabear formation, Bugwah formation and Marra Creek formation. The 

low hill lands adjacent to the riverine plain contain erosional surfaces of pre-Cainozoic rock 

blanketed by Quaternary residual and colluvial deposits. 

As a part of the Smith et al. (1998) report on the fauna of the northern floodplains, nine 

landforms were defined and four of these are present in the DRP. These are: 

Alluvial plains and floodplains permanent and temporary streams with channels to 15 m 

deep, alluvial plains with minor drainage lines and swamps, some small elevated areas (to 

3 m), extensive scalds, some pans, dunes to 10 m, some dunes and rises in channel loops; 

Playas and basins small to very large lakes, channels and floodouts, playas (shallow 

closed depressions occasionally filled with water), salt lakes, claypans and swamp basins, 

feeder channels, levees, lunettes to 10 m, low lying back plains; 

Rolling downs and lowlands undulating or low rounded ridges and some higher remnant 

hills, broad to narrow drainage lines, rounded pans to 1 km wide, relief to 20 m; and 

Plains deposited sediments with many small drainage sinks, broken drainage lines, 

floodouts, swamps, floodplains and sandplains, some lunettes, relief to 3 m. 

Additional landforms occur in the portion of the DRP outside of the northern floodplains 

study area. Some are described within the descriptions of provinces and land units (Section 

2.6). 

2.3.3 Soils 

The soils of the DRP have been mapped at a broad scale resolution (1:2 000 000) by DLWC. 

The mapping, current to 1988 (Map 18), shows the spatial arrangement of 10 broad soil 

groupings. 

Grey, brown and black cracking clay soils cover the 70% of the bioregion in the lower lying 

plains and depressions. The areas of higher elevation result from prior stream deposits with 

41


coarse red sediments deposited as levees during periods of high flow. This has produced the 

texture contrast soils, which have a well-drained coarser surface soil over red clays. Severe 

scalding is common on these soils that have been extensively and often heavily grazed. 

Scalding results from loss of the surface soils exposing the underlying red clays. 

Deep red earths have formed on coarse-grained sediments in two areas in the north of the 

region and calcareous red and yellow earths have formed from the aeolian sands in the west. 

In the northern floodplains study (Smith et al. 1998) in the north west of the bioregion, soils 

were described as: 

water deposited sediments on the alluvial plains and floodplains - mostly cracking clays, 

often deep and sometimes crabholey, areas of texture contrast soils (often on rises), noncracking 

clays on elevated areas, sands and sandy-earths on dunes; 

water deposited sediments on playas and basins - brown and grey cracking clays (heavy in 

lakes, more compact in channels and floodouts, saline in playas), often surrounded by red 

country; 

shallow to deep soils, often loamy and red, on rolling downs and lowlands - may be gritty 

or gravelly especially on upper slopes, grade into sandy red earths in drainage lines, clays 

in lakes and pans; and 

water-deposited sediments including moderate to deep red earths on plains - red-brown 

texture contrast soils, and grey or brown clays (non-cracking, cracking or gilgaied). 

The Macquarie catchment and marshes generally have rich alluvial soils but they vary 

between high quality soils from basic parent rocks and poorer soils formed from the more 

acid granite materials. The soils are highly weathered and leached of the soluble nutrients and 

the brown to red-brown subsoil also contains concretions (Wolfgang 1998). 

2.4 HYDROLOGY 

2.4.1 Surface waters: rivers, catchments and wetlands 

The DRP bioregion contains the Darling River, its tributaries and their catchments. Each of 

these catchments has unique flooding patterns and depositional characteristics and many 

rainfall events affecting these rivers originate outside the bioregion. Map 19 and Map 20 

show the rivers, major wetlands, floodplains and catchments within the Barwon-Darling 

basin. 

Three broad river reaches can be identified along the Barwon-Darling River system within 

New South Wales (Map 19). The river between Mungindi and Walgett is largely influenced 

by, and constrained within, the Cobar structural ‘lineament’. From Walgett to Bourke it is not 

constrained by any structural ‘lineaments’ but is influenced by the mega scale alluvial fan 

morphology of the Gwydir, Namoi and Macquarie River systems. South from Bourke the 

river is again constrained by a structural ‘lineament’ - the Darling ‘lineament’ which 

continues into the Murray River basin (Lloyd et al. 1994). 

Rivers 

The Namoi, Gwydir, MacIntyre Rivers (and associated rivers) rise in the Great Dividing 

Range (North East Tablelands Bioregion) and flow across the Nandewar Bioregion. 

Relatively high and reliable summer rainfalls feed these waterways. The Macquarie River 

also originates in reliable rainfall regions of the Great Dividing Range and flows into the DRP 

42


from the South Eastern Highlands, Brigalow Belt South and South Western Slopes 

Bioregions. These rivers are predominantly fed by winter rainfall and flooding is more likely 

to occur in winter-spring. 

Under a natural flow regime, the Barwon-Darling system receives an average of 35% of its 

water from the border rivers (MacIntyre, Dumaresq, and Boomi), 25% from the Namoi River, 

20% from the Condamine-Culgoa, 5% from the Macquarie-Bogan and 10% from the Gwydir. 

Modelling by DLWC has estimated that flows from the Namoi have been reduced by 70%, 

from the Condamine-Culgoa by 45% and from the Border Rivers by 45%. Total irrigation 

diversions from the Barwon-Darling system and tributaries exceed the natural median flow at 

Menindee (Thoms et al. 1995). 

The highly variable rainfall within the bioregion is reflected by flow variability, a feature of 

the Darling-Barwon system. Annual variations in flow range from 0.04% to 911% of the 

long-term mean, and discharges from the major rivers in the basin are highly skewed with a 

large proportion of average flows being recorded in very wet years and during major floods. 

This river system mostly floods in summer but flow is intermittent downstream of Louth 

(Lloyd et al. 1994). The Macquarie River has the most variable flow of 18 selected rivers in 

the Murray-Darling Basin. Annual flows vary from 2% to 940% of the mean, and only about 

one third of the flow entering the Macquarie Marshes flows through to the end of the system, 

except during floods (Kingsford & Thomas 1995; DWR 1991). 

Flooding is an important natural process that replenishes the floodplain with water and allows 

the large scale cycling of nutrients and biota. Inundation of the floodplain boosts invertebrate 

populations, breeding activity in waterbirds and fish, initiates growth and regeneration of 

riverine vegetation and creates extensive areas for colonisation by aquatic plants. Floodplains 

generally contain a mosaic of habitats ranging from those that are permanently wet to those 

that are rarely inundated. These all have different defining attributes and support distinctive 

communities. They are critical habitats for the biota in the floodplain and rivers (Lloyd et al. 

1994). 

Flood behaviour in the Barwon-Darling is complex with no two floods being the same and 

with a variety of localised forms of flooding. The relative contribution of the tributaries to 

this river system varies between floods. Mostly, the largest inflow is from the Namoi River 

but in the 1990 floods, the greatest inflow was from the Bogan River (most of this water was 

carried overland to the Bogan from the Macquarie River in the flood period). The Castlereagh 

River carries the Namoi and Barwon overflows as well as runoff from its own catchment to 

the Macquarie that then flows into the Barwon River. In 1998 extensive floodplain inundation 

occurred along the Darling between the Bogan and Warrego River junctions (DLWC 1999). 

Wetlands 

There are 4 810 defined wetlands covering 533 439 hectares in the DRP (Table 2.2). 

Wetlands are highly significant for the maintenance of biodiversity, regularly supporting 

significant breeding populations of waterbirds. They are also important refuges when drought 

occurs in other parts of arid and semi-arid Australia (Pressey, 1988). Parts of three wetlands 

within the DRP have been recognised by the Convention of Wetlands of International 

Importance (Ramsar Convention): the Gwydir wetlands west of Moree (Gingham 

watercourse and Lower Gwydir wetland), the Macquarie Marshes north of Warren and the 

Narran Lake system north-west of Walgett. In addition to these wetlands, the Menindee 

Lakes, Talyawalka Anabranch and Teryawynia Creek, Morella watercourse-Boobera lagoon- 

43


Pungbougal lagoon, Great Artesian Basin springs, and the Culgoa River floodplain are 

recognised as wetlands of importance in Australia (Environment Australia 2001d). The 

wetlands and rivers of the DRP also feed two river Ramsar sites downstream in South 

Australia; ie Riverland Ramsar site adjacent to the Murray River and Coorong and Lakes 

Alexandrina and Albert Ramsar site at the mouth of the Murray River (Ellis, M., NPWS, pers. 

com. Dec. 2001). 

Other wetlands occur throughout the bioregion including some 200 defined within the 

Walgett to Bourke section of the Darling-Barwon River alone (DLWC 1999). The 

significance of these smaller wetlands has not been fully assessed but they are critical for the 

movement of waterbirds between larger habitats. Much of the bioregion is characterised by 

smaller temporary to permanent wetlands, often known as cowals. 

Table 2.2 Wetlands identified within each catchment of the DRP 

(Source: Kingsford et al. 1999) 

Catchment Wetland type Number of Wetland 

wetlands area (ha) 

Named wetlands within DRP % within 

NPWS 

estate 

Castlereagh Floodplain wetlands 35 16 451 Broadsheet Lagoon 

Reservoir 105 33 879 Yarraman Lagoon, Merrah Dam 

Castlereagh totals 140 50 330 0 

Gwydir Floodplain wetlands 261 55 592 Collytootela Lagoon 

Reservoir 172 11 501 Bluebush Swamp 

Gwydir totals 433 67 093 0 

Macintyre Floodplain wetlands 62 91 868 Gooroo Lagoon, Poopoopirby Lagoon 

Freshwater lake 1 7 

Reservoir 54 2 468 

Macintyre totals 117 94 343 0 

Macquarie Floodplain wetlands 817 53 260 The Big Waterhole, The Big Lagoon, 29% 

Paddys Cowal, Moonachie Cowal, Meryon 

Cowal, Gewah Cowal, Dragon Cowal, Dead 

Gum Lake, Bay of Biscay Swamp 

Freshwater lake 35 1 492 0 

Reservoir 98 2 175 Sandy Creek, Meringo Cowal, Ewenmar 0 

Creek, Euloon Cowal, Boothaguy Creek 

Macquarie totals 950 56 927 7% 

Namoi Floodplain wetlands 82 39 710 

Reservoir 102 1 866 

Namoi totals 184 41 576 0 

Western Floodplain wetlands 2 902 134 834 Yambie Lagoon, Well Lake, Saltbush 19% 

Waterhole, Nartooka Lake, Louth 

Freshwater lake 52 87 755 

Waterhole, Kangaroo Lake, Jims Lake, Four 

Mile Lake, Dead Horse Lake, Copi Hollow 

Lake Are, Collins Lake, Paradise Tank, 4% 

Travellers Lake, Wintlow Lake, Lake 

Bintullia, Lake Eurobilli, Malta Lake, 

Coonimby Lake, Lake Speculation, 

Pollioillaluke Lake, Cawndilla Creek, 

Angledool Lake, Packers Lake, Bijijie Lake, 

Jinki Lake, Emu Lake, Balaka Lake, 

Nettlegoe Lake, Tandure Lake, Lake 

Woytchugga, Gunyulka Lake, Coocoran 

Lake, Wongalara Lake, Pamamaroo Lake, 

Narran Lake, Lake Cawndilla, Poopelloe 

Lake, Lake Menindee 

Reservoir 32 582 0% 

Western totals 2 986 223 170 13% 

DRP TOTALS 4 810 533 439 8% 

44


Catchments 

There are six major river catchments within the DRP (Map 19, Table 2.3). The Western and 

Macquarie River catchments together cover 67% of the DRP and contain most of the 

wetlands. 

Table 2.3 River catchments intersecting the DRP 

Catchment Area within % total % DRP 

DRP (ha) catchment area 

Western including Barwon, Birrie, Bokhara, Culgoa, 3 472 620 

Darling, Little Weir, Moonie, Narran, Paroo and Warrego 

Rivers 

12% 38% 

Macquarie River including Barwon, Bogan, Darling, and 2 710 519 

Little Bogan Rivers 

36% 29% 

Gwydir River including Barwon, and Mehi Rivers 910 366 34% 10% 

Castlereagh River 853 068 49% 9% 

Namoi River 779 814 19% 8% 

Macintyre River including 

Barwon, Boomi, Doondoona, and Dumaresq Rivers. 

522 455 22% 6% 

Western Catchment 

The Condamine-Culgoa River system in south-central Queensland feeds the Culgoa and 

Bokhara Rivers of the western catchment. Beardmore Dam at St George regulates these 

rivers and an increase in water diversion for cotton irrigation has substantially reduced the 

river flow from Queensland into New South Wales. These rivers are mostly fed by summer 

floods from cyclonic depressions and are strongly seasonal. 

The Narran River is also part of this system but it does not feed into the Darling system, 

terminating instead at Narran Lake and associated wetlands. It is unregulated with minimal 

water extraction occurring. It also receives flows from the Balonne River during periods of 

high flow, although the Balonne is regulated by Beardmore Dam and water is also extracted 

to on-farm water storages, affecting the flows into the Narran system. 

The Narran Lakes are a large terminal lake system at the end of the Condamine - Balonne 

River system (Map 20). The Narran River has a small shallow main channel with a 

contiguous floodplain and several lakes lie along the floodplain. During a large flood event 

the Narran branches to fill Clear Lake while simultaneously flowing to and filling Narran 

Lake. Once Clear Lake has filled it overflows to fill Back Lake and the Long Arm and more 

water flows into Narran Lake (Ramsar 2000). 

Flooding mostly occurs in summer and autumn, but floods have been recorded in winter and 

spring. Annual inflows are highly variable and more than one flood per year has occurred 

during a quarter of the recorded flood events. Once inundated, Narran Lake can hold water 

for up to 2 years, but in years of low flow water may not reach Lake Narran at all. Back and 

Clear Lakes, which are within Narran Lake Nature Reserve, will usually retain water for 

about 4-6 months after a single inundation. As a terminal system the lakes usually empty only 

by evaporation and seepage but during exceptional events the Lakes can overflow to the 

Barwon River. These lakes have an average inundation frequency of one per two years and 

this is more frequent than for other inland wetlands in New South Wales (Ramsar 2000). 

45


Narran lakes was a major meeting and ceremonial centre for Aboriginal people and supported 

a large, semi-permanent Aboriginal population (Martin 1979; NPWS 2000a). The Narran 

Lake area is a highly productive area which played a vital role in the Aboriginal settlement 

pattern of the region (NPWS 2000a). 

Teryawynia Lake is at the southern edge of the DRP and is one of a series of lakes which 

floods sequentially as high flows travel along the Talyawalka Anabranch of the Darling 

River. This wetland system includes Teryawynia, Dry, White Water, Eucalyptus / Waterloo, 

Victoria, Brummeys, Dennys, Brennans, Sayers, Gum, Boolaboolka, North and Ratcatchers 

Lakes and associated wetlands. The Talyawalka Anabranch and Teryawynia Creek wetlands, 

when inundated, provide important habitat for large numbers of waterbirds. Aboriginal 

middens are located within the dunes of the area (Withers 1996; Environment Australia 

2001d). 

These wetlands are mostly located on Western Lands leases and are characterised by a series 

of braided channels across the floodplain, interspersed with seasonally inundated lakes. 

Some lakebed cropping occurs occasionally, when sufficient moisture is available. 

The floodplain of the Balonne and Culgoa Rivers at Byra just north of the New South 

Wales/Queensland border, supports a variety of wetland and floodplain vegetation. These 

wetlands are listed as nationally significant in the Directory of Important Wetlands of 

Australia (Environment Australia 2001d). They are mostly within the Culgoa National Park 

and support the largest contiguous Eucalyptus coolabah woodland remaining in NSW. They 

can be flooded for periods of up to four months with water depths reaching 10 metres. The 

Culgoa River floodplain is of traditional and social significance to the local Aboriginal 

people, the Gandugari group of the Morowari people.. English (1997) found strong evidence 

of extensive Aboriginal use of the sandy rises on the floodplain of the Culgoa River for camp 

sites, especially near water sources. This indicates the importance of long-term water sources 

to the local Aboriginal people. 

The Menindee Lakes consist of Lake Pamamaroo, Lake Menindee, Lake Cawndilla, Lake 

Wetherell, Lake Tandou, Lake Balaka, Lake Malta, Tandure Lake, and Lake Bijji and cover 

approximately 45 000 ha (Environment Australia 2001d). Part of these wetlands fall within 

Kinchega National Park, with the remainder on Crown land and Western Lands Lease. The 

large number of Aboriginal sites within Kinchega National Park indicate the changing pattern 

of Aboriginal occupation of this area. Sites include middens, camps and hearths where the 

remains of freshwater mussels and yabbies can be found. Aboriginal scarred trees occur 

along the Darling River within the Menindee Lakes area (NPWS 1996). 

Macquarie River Catchment and Macquarie Marshes 

The Macquarie River is regulated by Burrendong dam, built in 1967 for flood mitigation and 

for irrigation. Windamere Dam, built in 1984, also regulates the flow in this river system and 

there are many weirs and storage dams built for town water supplies and other extractive 

purposes. Irrigation occurs extensively in the centre of the catchment with 50 - 60% of flows 

being used for cotton (Macquarie 2100 Plan 1999). Water flows can also be diverted to the 

Bogan from the Macquarie to provide adequate water supplies for Nyngan and Cobar. This 

river regulation has reduced flows to the Macquarie Marshes and in an attempt to compensate 

for this, a guaranteed level of water flows for the Marshes has been established. This is 

known as an environmental flow and is intended to maintain the diversity and productivity of 

46


the wetland habitat. The allocation is generally insufficient to stimulate breeding so is timed 

to occur with natural triggers such as rainfall events (Kingsford & Thomas 1995). 

The Macquarie Marshes are one of the largest inland semi-permanent wetlands in southeastern 

Australia (Map 20). They cover approximately 200 000 hectares when flooded and 

are about 100 km long and 30 km wide. They have a flow through system rather than being a 

terminal basin. Water quality is increased by the anabranch flow, which acts as a filtration 

system and promotes a diverse and productive biological system (Wolfgang 1998). In 1818 

when Oxley was exploring the area, the Macquarie Marshes were probably at least twice the 

size they are today. In 1863 a newspaper reported that ‘The whole of the country between the 

Merri Merri [Creek, 24 to 41 km east of the Macquarie River] and the Macquarie [River] was 

one sea of water with scarcely a dry foot of ground’ (quoted in Kingsford & Thomas 1995). 

The 1874 flood was reportedly even larger, but the largest on record was in 1955. These 

marshes contain extensive reed beds, Eucalyptus camaldulensis (red gum) swamps, open 

lagoons and Muehlenbeckia florulenta (lignum) covered gilgaied floodplains. 

A range of significant Aboriginal sites have been recorded within the Macquarie Marshes 

including oven mounds. The Macquarie Marshes is the only area where oven mounds have 

been recorded outside the Murray Valley. Aboriginal culture in the area was influenced by 

the changing water regimes of the Macquarie Marshes (NPWS 1993). 

The impact of rising salinity levels will be localised in areas where evaporation concentrates 

the salts into pools or depressions. At the point where the Macquarie River enters the 

Marshes, the expected average salinity for the year 2100, is 2 110 EC, well above the 

acceptable ANZECC (1999) trigger levels (DLWC 2000). Monthly salinity data from the 

Macquarie River at Narromine indicate that in 1998 the river had a 4% chance of exceeding 

the 1 500 EC threshold but extrapolation of this data indicates that this threshold will have a 

23% chance of being exceeded in 2100, mostly during low flow periods. This could have a 

serious effect on in-stream biota and recruitment of biota into and between wetlands. This 

would result in a loss of species diversity and declines in abundance of species (MDBC 

1999). 

Gwydir River Catchment and Gwydir Wetlands 

The Gwydir River is regulated by Copeton Dam which supplies irrigation water for the cotton 

industry. The Gwydir Valley is the largest cotton producing area in Australia and water 

supplies from Copeton Dam are over allocated. The dam rarely has sufficient supplies to meet 

demand resulting in significantly reduced water flows in the river and a subsequent increase 

in the usage of off-river storage to capture water during periods of high flow (EPA 1997). 

Downstream of Moree the Gwydir divides into two major arms, the Gingham in the north and 

the Lower Gwydir in the south (Figure 2.16). Towards the end of these watercourses the 

water forms a delta with intermittent and semi-permanent wetlands. The distribution of flows 

into these wetlands is naturally dynamic. Prior to 1936 most small floods flowed into the 

Lower Gwydir and only the large flows reached the Gingham. This has changed with the 

development of the Gwydir Raft near the Tyreel Regulator. The raft is an accumulation of 

deposited timber debris and sediment which began to form in the early 1900s and effectively 

blocked the original river channel. The raft has continued to steadily accumulate and now 

extends for about 30 km. By the mid-1940s water flowed more readily to the north, increasing 

flows into the Gingham system (McCosker & Duggin 1993). 

47


(Keyte 1994) 

Figure 2.16 Lower Gwydir Wetlands 

The construction of Copeton Dam has resulted in a substantial reduction in the number of 

major floods through this system and stabilisation of the raft. A new raft has formed on the 

Gingham Channel a few kilometres downstream of the head of the old raft and this may affect 

the distribution of future floodwaters. The formation of these rafts (accumulations of timber, 

debris and sediment) is thought to result from the combination of human activities such as the 

clearing of the upper catchment and natural depositional processes. Currently, with flows of 

between 2 500 and 40 000 ML/day, 70% of the Gwydir flows into the Gingham and 30% into 

the Lower Gwydir. Flows of 40 000 ML/day or more produce over-bank flows and the water 

divides evenly into each watercourse (McCosker & Duggin 1993; Keyte 1994). 

Significant flooding of the watercourse is irregular and occurs most frequently in January and 

February. Secondary floods occur in winter. Long term residents recall the Gwydir River 

entering the wetlands ‘until the River emptied’ but most of the flow is now diverted for 

irrigation and domestic use before reaching the wetlands. Before regulation the Gwydir 

wetlands would have received flows sufficient to inundate their core and watercourse 

wetlands (20 000 ha) in 192 months during a 93 year period or 17% of the time and large 

flows would have been a maximum of three years apart. With regulation, flows large enough 

to fully inundate the wetlands occur only 5% of the time, a 70% reduction (McCosker & 

Duggin 1993; Keyte 1994). 

The Gwydir wetlands are a flow through system and are likely to be affected by salinity in a 

similar way to the Macquarie Marshes. The estimated average salinity in the Gwydir as it 

enters the wetlands is expected to rise to 740 EC in 2100, and the probability of exceeding the 

threshold of 1 500 EC (this threshold is considered to be where direct biological effects are 

48


likely to occur in river, stream and wetland ecosystems) is likely to change from 3% in 1998 

to 12% in 2100 at Pallamallawa. The impact of periods of high salt levels will be similar to 

that predicted for the Macquarie Marshes, with possible salt scalding where the saline waters 

become highly concentrated (MDBC 1999). 

Macintyre, Namoi and Castlereagh River Catchments 

The Macintyre River (with tributaries known as the border rivers) receives most of its 760 

Gl per year of flow from its catchment within New South Wales. Pindari dam in NSW, and 

Coolmundie and Glenlyon dams in Queensland are major water storages in the Macintyre 

catchment. About 222 GL per year are drawn from this river, less than for the Gwydir 

(300 GL/year) and Namoi Rivers (248 GL/year) (DITAR 1996). 

The Morella Watercourse, Boobera Lagoon and Pungbougal Lagoon wetlands are the 

remnants of a previous course of the Macintyre River. They are permanent water bodies and 

provide important habitat for many waterbirds. Boobera Lagoon has great significance to the 

local Aboriginal people, the Kamilaroi, and is considered to be an exceptionally important 

Aboriginal site in south-eastern Australia as the local Aboriginal people, the Kamilaroi, 

believe that Boobera Lagoon is the resting place of the rainbow serpent. Boobera Lagoon 

plays an important role in the teaching of Aboriginal culture (Environment Australia 2001d). 

The Namoi River is dammed by Lake Keepit, constructed in 1960. Trials for cotton 

production began in the Narrabri / Wee Waa area soon after this. Cotton is now extensively 

grown in the area and 54% of the natural median flow of this river is used for irrigation. This 

regulation has resulted in the loss of natural variation in flow levels, with periods of low flow 

very rare, and a reduction in overall flow volume (Inland Rivers Network 1999; EPA 1997). 

The Castlereagh River rises in the Warrumbungle Ranges in the Brigalow Belt South 

bioregion, an area of comparatively high rainfall. Most of the upper catchment is sandy and, 

along some of its length, the river flows through the sand to reappear as pools further 

downstream. This is one of the least regulated rivers in the bioregion, with no dams and only 

a few weirs and limited use for irrigation (EPA 2001). 

2.4.2 Groundwaters 

There are two sources of groundwater within the bioregion, the Great Artesian Basin and 

several alluvial aquifers. 

The Great Artesian Basin 

The Great Artesian Basin (GAB) aquifer is a multi-layered, confined system with a large 

synclinal structure. Much of the artesian water in New South Wales originates in Queensland, 

but a significant amount is contributed through the Pilliga Sandstones, the primary intake area 

in New South Wales (Watkins & Meakin 1996, Figure 2.17). The artesian water has total 

dissolved solids of 500 to 1 500 mg/l, making it suitable for stock and domestic uses but the 

sodium-bicarbonate-chloride chemistry of this water makes it unsuitable for irrigation 

(NWCMC 1996). 

49


Figure 2.17 Groundwater features of the Coonamble Embayment of the Great Artesian Basin 

(Watkins & Meakin 1996) 

One thousand, four hundred bores tap the deeper aquifers of the GAB in New South Wales 

but nearly half of these have ceased to flow as a result of artesian pressure having decreased 

markedly over the past 100 years. About 250 of the bores operating in New South Wales have 

uncontrolled flow (DLWC & AFF 2000). 

The Great Artesian Basin Mound Springs are wetlands found mostly within the Mulga Lands 

bioregion but some occur within the DRP. Mound springs in the Great Artesian Basin 

provide important habitat for more than 40 species of freshwater snails which are endemic to 

these springs and some which are endemic to an individual spring (Environment Australia 

2000d). About one third of the mound springs have dried up as a result of the decreased 

artesian flows. 

Alluvial aquifers 

The Namoi catchment alluvial aquifer is the most extensive and most intensively developed 

aquifer system in New South Wales. It accounts for nearly 40% of all good quality, high yield 

groundwater extracted. This is mainly used for irrigation and is currently over-allocated 

(Table 2.4). Alluvial aquifers are also of great importance in the Gwydir and the Macquarie 

50


catchments. The alluvial aquifer near Narromine has yielded 10 litres/second and is being 

tapped extensively for crop irrigation between Narromine and Warren (NWCMC 1996). 

Table 2.4 Groundwater resources of the Lower Namoi Catchment 

(NWCMC 1996) 

Total area of alluvium (km 2 ) 5 100 

Volume of storages (ML) 20 million 

Volume available for extraction (ML) 6.6 million 

Estimated recharge (ML/yr) 82 500 

Entitlements (ML/yr) 208 000 

About 5.4 million hectares of land in New South Wales have groundwater at or near the 

surface; this is mostly on the western slopes (MDBC 1999). There are estimates that up to 

12.3 million hectares, about 20% of the Murray-Darling Basin in New South Wales (a more 

extensive area than the DRP) may be experiencing rising groundwater tables. In addition, an 

estimated 40% to 80% of the individual catchments east of the Bogan and Darling Rivers, 

which make up the majority of the DRP bioregion, have rising groundwater levels. There 

have been very few detailed groundwater studies in the DRP (DLWC 1999). 

The area of land with high water tables and which could become salt affected has not been 

precisely estimated, but a waterlogged area of between five and seven million hectares is 

considered to be realistic. Serious salination is predicted to affect between two and four 

million hectares (MDBC 1999). Salt loads in the Darling River also appear to be enhanced by 

the inflow of saline groundwater, which originates in the Cainozoic valley-fill aquifers of the 

Bourke Graben (Mount 1995). Sturt (1833), on his expeditions into the interior of southern 

Australia describes the Darling River as follows: “as a river it ceased to flow; the only supply 

it received was from brine springs, which, without imparting a current, rendered its waters 

saline and useless”. This suggests that salinities within the Darling River are affected by 

naturally saline ground water. 

2.5 LAND CONDITION 

2.5.1 Land degradation 

The north east portion of the bioregion, the alluvial fans of the Darling tributaries, has been 

extensively cleared with remnant vegetation now often only found in woodland ‘islands’ on 

infertile or non-arable land. Goldney and Bowie (1990) have described this region as “islands 

of woodlands and forests in a sea of agricultural land”. Land clearing began with the early 

settlement in the 1830s. The plains of the lower Namoi catchment were originally covered by 

grasslands and open woodlands and the black cracking clays of these plains are now mostly 

used for cropping. In this area there is an average tree cover of nine percent (NWCMC 1996). 

Important causes of land degradation in the bioregion include: 

soil erosion; 

streambank erosion; 

tree decline; 

rising groundwater and dryland salinity; 

51


soil structure decline; 

soil acidity; 

decline in water quality; and 

contamination of water and soil by sheep dips, pesticides and wastes. 

Morgan and Terry (1992) identify the following land degradation indicators: 

scalding of rises in the Bogan-Macquarie, Castlereagh-Barwon, Culgoa-Bokhara, 

Warrambool-Moonie and Narran-Lightning Ridge provinces; 

scalding of floodplains in the Louth Plains, Wilcannia Plains and Menindee provinces; 

dieback in Eucalyptus camaldulensis (river red gum) in the Bogan-Macquarie province; 

sheet and gully erosion on the ridges of the Narran-Lightning Ridge province; and 

wind and gully erosion in the Menindee province. 

2.5.2 River and wetland degradation 

Streambank and gully erosion, turbidity and sedimentation, high nutrient levels, blue-green 

algal blooms, exotic plants and contamination by rising salinity are degradation issues posing 

a threat to wetlands and rivers in the DRP. During the last 15 years, levels of blue green algae 

were generally above acceptable safe swimming levels in the Macquarie River. Escherichia 

coli exceeded acceptable levels for swimming at times in the Macquarie River, and phosphate 

levels were also sometimes high. 

River regulation and water extraction for irrigation have had a detrimental effect on wetlands 

within the bioregion. In 1996 the Gwydir wetlands were filled with the first substantial flow 

for twelve years, less than the estimated natural average of three years (McCosker and 

Duggin 1994). Environmental flows are an essential requirement for the survival of these 

wetlands and a key element in wetland health is the natural wetting and drying cycle 

produced by irregular flooding. 

Slumping of riverbanks as a result of increased flows due to river regulation, uncontrolled 

stock access, no buffer zones, big wets following long drys causing flow diversion, increased 

turbidity, the presence of European carp (Cyprinus carpio) and poor water quality (caused by 

the location of garbage and septic systems) have been identified as problems within the 

Macquarie system. More than 1 300 km of streambank erosion along the Macquarie River 

occurs upstream of Narromine (Macquarie 2100 Plan 1999). 

Aquatic biodiversity has been lost because weirs and dams impede the movement of various 

species to their spawning grounds. Fish ladders have been constructed on some weirs but the 

success of these is questionable as some have not been used. Control of river flows by dams 

has also changed the river level and flow requirements of many species for successful 

breeding (Thoms et al. 1995). 

An infestation of Eichhornia crassipes (water hyacinth), a highly invasive aquatic weed, was 

first observed in the Gingham watercourse during the 1950s, spreading to cover an area of 

more than 7 000 ha by the mid 1970s. An integrated control program was established in 1976 

with physical, chemical and biological control measures implemented. The management 

program included construction of diversion banks across the many natural off takes to prevent 

water inflow to the wetlands during the control period. The seed bank could not survive the 

resultant drying and when the area was later flooded any seed germination was controlled by 

52


herbicides and subsequent drying out before seed set (McCosker and Duggin 1993). The 

infestation had been monitored and controlled regularly until two large floods through the 

wetlands in the summer of 2000-01, when the previously dormant seedbank of Eichhornia 

crassipes germinated and quickly became established throughout much of the wetland area. 

2.5.3 Salinity 

Dryland salinity occurs in non-irrigated areas. Salinity is the result of a build up of salt in the 

soil, usually caused by a rising watertable. Evaporation of saline water at the soil surface 

tends to concentrate salts to the point where they affect the environment (DLWC 2001a). In 

the Macquarie River catchment (approximately 7 500 000ha) dryland salinity affects at least 3 

850 ha, mostly in areas with extensive vegetation clearing (1 560 ha) and in areas with saltinduced 

sheetwash (627 ha) and bare scalds (1664 ha). Saline scalds are most common in the 

drier lower floodplain of the Macquarie (Taylor 1994). In the coarser red soils of the more 

elevated land, grazing has caused the compaction or loss of surface soil, producing patches of 

scalded red clay. 

Salinity from irrigation is caused by supplying water excess to crop requirements, inefficient 

water use, poor drainage, irrigation of unsuitable or "leaky" soils, allowing water to pond for 

long periods and seepage from irrigation channels, drains and storages. Introduced land 

management practices (such as irrigation) generally have different water use characteristics 

than native vegetation and allow more rainfall to enter the groundwater. If more water is 

being added than can be accommodated in the groundwater aquifer, the groundwater level 

will rise. As the watertables reach the land surface, the soil becomes waterlogged. The 

significant difference between dryland and irrigation salinity is that the application of 

irrigation water to land can exaggerate the leakage of surplus water past the root zone to 

groundwater (recharge), increasing the rate at which the watertable rises (DLWC 2001a, EPA 

1997). 

River salinity is caused by the movement of saline water from areas of dryland, irrigation and 

urban salinity into creeks and rivers. As salinity in a catchment worsens, the rivers become 

increasingly saline (DLWC 2001a). 

The salinity levels and predicted changes in the salinity of the rivers in the DRP have been 

assessed in a salinity audit for the Murray-Darling Basin. The salt loads study carried out as a 

part of the salinity audit has estimated the potential salinity levels for 2020, 2050 and 2100 

for each of the river valleys supplying water to the Murray and Darling Rivers. The average 

salinity levels for the Macquarie, Namoi and Bogan have been estimated as being likely to 

exceed the 800 EC threshold of the World Health Organisation for acceptable drinking water 

within 20 years and the Castlereagh within 50 years under current management practices 

(Table 2.5). These predicted salinity levels have serious implications for both agriculture and 

the supply of drinking water for the population centres (MDBC 1999), as well as for the 

region’s biodiversity. The predicted salinity levels for the Darling River are not yet available 

but generally the salinity level of the Darling is currently less than 800 EC throughout its 

length. At Menindee the salt levels are predicted to increase from about 250 EC in 1998 to 

500 EC in 2100 (MDBC 1999). 

53


Table 2.5 Actual and predicted average salinity levels for major rivers in the DRP 

(MDBC, 1999) 

River valley 1998 2020 2050 2100 

Bogan River 730 1 500 1 950 2 320 

Macquarie River 620 1 290 1 730 2 110 

Castlereagh River 640 760 1 100 1 230 

Namoi River 680 1 050 1 280 1 550 

Gwydir River 560 600 700 740 

Trends in the levels of salt concentrations in the rivers have indicated that within the DRP 

they are increasing by 2-4 tonnes per km per annum in the Castlereagh / Macquarie systems, 

and more than 1 tonne per km per annum in the Namoi River. The amount of salt mobilised to 

the land surface in the Murray Darling Basin is predicted to double from five million tonnes 

annually in 1998 to 10 million tonnes annually in 2100. The predictions are significant for the 

river catchments within the DRP (Table 2.6) (MDBC 1999). 

Table 2.6 Predictions of the tonnes of salt mobilised to the land surface per year for river catchments 

of the DRP 

(MDBC 1999) 

Catchment 1998 2020 2050 2100 

Macquarie River 240 000 490 000 660 000 790 000 

Castlereagh River 161 000 180 000 320 000 330 000 

Namoi River 60 000 100 000 120 000 150 000 

Gwydir River 7 000 20 000 50 000 60 000 

Macintyre River 80 000 80 000 80 000 80 000 

The economic impact of rising watertables and salinity has been estimated for the Little and 

Talbragar Rivers in the Upper Macquarie catchment. The estimated annual cost of rising 

water tables and salinity for the Talbragar River catchment was $1 612 421, with the major 

costs for repairs, maintenance and preventative works being borne by farmers (MDBC 1999). 

In the lower Macquarie area water tables are rising at 0.3m/year in some areas and between 

15 and 20 thousand hectares have water less than three metres below the surface. Water will 

be unsuitable for irrigation in this area as a result of high salinity loads by 2100 (Macquarie 

2100 Plan 1999). 

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2.6 BOUNDARIES WITHIN THE DRP 

The land within the DRP has been described and subdivided using a variety of criteria and 

scales. Some descriptions most widely used by land managers are the province and regional 

descriptions by Morgan and Terrey (1992) and land system descriptions of the Western 

Division by Walker (1991). 

2.6.1 Provinces 

In NSW nine provinces have been described for the DRP (Morgan & Terrey 1992). Five of 

these cover each of the northern alluvial fans, one is an interfluve of the weathered sandstones 

near Collarenebri and three are different types of alluvial deposits along the Darling River, 

south from Bourke (Map 21). Within Queensland the northern extent of the DRP is described 

as two distinct provinces of the Brigalow Belt South Bioregion (Sattler & Williams 1999). 

Northern Alluvial Fans 

The catchment characteristics of each of the northern alluvial fans have resulted in variation 

in the flood patterns and alluvial deposits between each province. 

Bogan-Macquarie Province 

This alluvial complex formed by the Bogan and Macquarie Rivers lies in the south east of the 

bioregion. The province has a large catchment extending beyond the DRP bioregion south 

east of Bathurst and east to the Liverpool Range. Quaternary alluvials are underlain mostly by 

Paleozoic sediments and small areas of basalt and sandstone. The coarser-textured high red 

ridges and Eucalyptus populnea subsp. bimbil (poplar box) woodlands dominate the eastern 

portion of this province. Grey and brown clays dominate on the plains and depressions, 

alluvial soils on levees and river channels with texture contrast soils occurring on the low and 

gently undulating rises. 

The wetlands and low-level floodplains of the Macquarie River dominate the central areas of 

the province. Much of this area has been cleared, although the wettest areas within the 

Macquarie Marshes Nature Reserve retain significant areas of native vegetation. The western 

parts of this province are associated with the Bogan River and receive high level overflows 

from the Macquarie River. Flooding is infrequent and the finer soils of low scalded rises and 

clay plains are dominant. 

Castlereagh-Barwon Province 

Extensive plains of quaternary alluvials with a strong basaltic influence form the Castlereagh- 

Barwon province. This is the most intensively developed province of the bioregion, including 

both dryland and irrigated cropping. It includes the alluvial fans of the Castlereagh, Namoi, 

Gwydir and Macintyre Rivers and the broad plains of the Barwon and upper Darling Rivers. 

Seasonal and semi-permanent wetlands are present on the major tributaries including the 

significant wetlands of the Gwydir. 

The landform contains three co-dominant formations: river channels, levees and lower 

floodplains with riparian woodland vegetation; upper floodplains predominantly covered by 

Astrebla lappacea (curly Mitchell grass); and wooded low rises with some higher gently 

undulating areas. Soils range from grey clays of the floodplains to texture contrast soils, 

55


occasional sands and brown clays on low rises. A broad, complex floodplain dominated by 

high-level grey clay plains lies between the confluence of the Barwon and Macquarie Rivers 

and Bourke. 

Culgoa-Bokhara Province 

Grasslands or forbfields occur on the plains of quaternary alluvium of the Culgoa and 

Bokhara Rivers. Grey clays predominate on the floodplains, with some texture contrast soils 

on low rises. These low level flood plains and channels contain extensive areas of Astrebla 

(Mitchell grass) grasslands, much of which has been heavily grazed and cultivated. In many 

areas the Astrebla grasslands have become degraded and are now replaced by opportunistic 

weed species such as Sisymbrium (mustard weed). 

Warrambool-Moonie Province 

This province contains no major river but is cris-crossed by a complex of distinct channels 

(the Big Warrambool). The channels are usually dry but are filled periodically by high level 

overflows of the Moonie and Balonne Rivers to the north. The channels are usually dry. The 

landform varies from low-level floodplains and channels to high-level floodplains, low rises 

and high-flow channels. Grey clay soils occur on the floodplains, and texture contrast soils 

and sands occur on low rises. The vegetation of this province is generally quite open with 

Eucalyptus coolabah (coolibah) and Eucalyptus populnea subsp. bimbil woodlands on the 

higher areas. Much of the land is heavily grazed and some areas are cultivated. The low red 

rises are generally severely scalded. 

Narran-Lightning Ridge Province 

A dominant feature of this province is a north-south ridge of Cretaceous sediments, adjacent 

to low-level Quaternary alluvials on the floodplains. The Narran River, which lies to the west 

of the ridge, receives flow from low-level floods in the Balonne-Maranoa River system in 

Queensland. Water from this system mostly flows around the ridge and is retained in a large 

number of basins formed around the lower slopes. The largest of these basins is Narran Lake, 

the terminal basin for the Narran River. The Narran wetlands are terminating basins with little 

or no flushing. They also receive a large quantity of local runoff from the adjacent 

sedimentary ridge. During high flows this basin overflows to the west and the Narran River 

overflows to join the Big Warrambool (Province 4). 

The two most common landforms in this province are low rounded ridges and some rocky 

hills with Eucalyptus melanophloia (silver-leaf ironbark) open woodland and level to gently 

undulating floodplains, low rises and sand dunes with a riparian woodland. There are also 

depressions and backplains, lunettes, salinas and levees where grasses, forbs and some 

riparian plant communities occur. The soils on the ridge vary from red earths to lithosols and 

grey clays are again dominant on the plains. 

Collarenebri Interfluve Province 

This province is the southern-most tip of the Northern Surat Basin, an extensive region of 

coarse-grained deeply weathered Cretaceous sediments in south-eastern Queensland. This 

narrow area of land west of the Barwon River is slightly undulating, with low rounded hills. It 

separates the parts of the DRP bioregion that receive drainage from Queensland from those 

fed mainly by drainage from the slopes and tablelands of New South Wales. The loamy deep 

red earths of this area are easily compacted and susceptible to water and wind erosion 

following clearing of the Eucalyptus populnea subsp. bimbil woodlands in this province. 

56


Darling Alluvials 

Between Bourke and Wilcannia Paleozoic sediments underlie the Quaternary alluvials 

associated with the Darling River. The river is mostly confined to a narrow meandering belt 

with broad alluvial plains. Near Tilpa, high-level flows are restricted by bedrock and some of 

the river flow is directed into the Paroo overflow. 

Louth Plains Province 

The Louth Plains Province contains broad, relatively uniform alluvial plains. This province 

stretches along the northern part of the Darling River and in addition to the flows from the 

northern alluvial provinces is fed by flows from central southern Queensland via the Warrego 

River, outside the DRP bioregion. The dominant landforms are high-level floodplains and 

small channels with grey clays, and fringing areas of dunes and old red alluvials. In the south 

there are dunefields typical of the northern part of the Murray-Darling Depression bioregion 

and the bedrock ranges and ancestral alluvials of the Cobar Peneplain bioregion. Astrebla 

grasslands were once widespread through this province but are now generally degraded. 

Wilcannia Plains Province 

This province contains a broad complex riverine plain. It contains the river channel, small 

lakes and anabranches on the high level floodplain, with low rises, dunes, and pans. Soils 

range from grey clays of the river channel and floodplain, to texture contrast soils on low 

rises and occasional sands. In addition to the flows along the Darling River the province can 

receive water from south west Queensland when the Paroo is in flood. 

Menindee Province 

The Menindee Province contains broad alluvial complex dominated by rises and plains. In 

this province the Darling River begins to flow more slowly and form anabranches and 

associated overflow lakes. The province contains an intricate system of flood channels, 

floodplains, back plains and dunes. The province includes the Darling River floodplain with 

the main channel, billabongs, swamps and occasional low sandhills, higher alluvial plains and 

dunes, large overflow lakes and basins, and associated lunettes. Soils are varied, from grey 

clays and sands of the Darling River floodplain, to sands, texture contrast soils and clays of 

undulating plains and dunes, and clays, texture contrast earths and sands of overflow lakes 

and basins. 

Provinces in Queensland 

The provinces in Queensland are the Balonne-Culgoa Fan (Province 35) and the Macintyre- 

Weir Fan (Province 36). The Balonne-Culgoa Fan is the larger of these two provinces and 

contains extensive quaternary alluvial sediments along the Balonne and Culgoa Rivers. The 

alluvial plains and wetlands of this province have texture contrast soils with Eucalyptus 

coolabah grassy woodlands on areas subject to periodic flooding and Eucalyptus populnea 

subsp. bimbil with Eucalyptus melanophloia and Casuarina cristata (belah) on higher 

ground. The Macintyre Weir Fan features predominantly alluvial plains and associated 

riverine landforms. The mean annual rainfall in this province is higher (550 mm) than in the 

more western province (450 mm) and the general elevation is also a little higher (200 m 

compared with 150 m). 

Regional ecosystems have also been described by Sattler and Williams (1999). Two of these 

are of particular interest as they are restricted in Queensland to the Balonne-Culgoa province, 

and their conservation status is poor. The fringing woodland of Eucalyptus coolabah with 

Acacia stenophylla (river cooba) and Muehlenbeckia florulenta (lignum) found on the heavy 

57


soils of swampy stream channels, occurs only in the extreme south-west of this province. 

About 40% of this ecosystem has been cleared and the remaining 60% is subject to total 

grazing pressure and ringbarking. The other ecosystem of concern is also in the south west of 

this province and is extensively grazed. It is low open woodland of Flindersia maculosa 

(leopardwood) and Atalaya hemiglauca (whitewood) with Acacia omalophylla, Acacia 

cambagei (gidgee) and Tripogon loliiformis (five-minute grass). 

2.6.2 Land systems 

Land systems are an area or group of areas throughout which there is a recurring pattern of 

topography, soil and vegetation (Walker 1991). Ninety-one of the land systems defined and 

mapped by Walker cover 46% of DRP. These land systems are listed in Appendix B, which 

includes a brief description of topography and dominant vegetation. The percentage of the 

DRP covered by each land system ranges from 4.5% (Nelyambo - floodplains with 

Eucalyptus coolabah), less than one precent (45 landsystems each cover less than one percent 

of the DRP) (Appendix B). Several land systems occur almost entirely within the DRP and 

thirty-five have less than 10% of their total area within the DRP. The distribution of the land 

systems which each cover more than 1% of the area is illustrated on Map 22. Approximately 

90% of the mapped area contains land systems described as playas and basins or alluvial 

plains. 

2.7 SUMMARY AND PROPOSED FURTHER WORK 

2.7.1 Summary 

The DRP lies almost entirely in a semi-arid climatic zone, with only a small portion in the 

temperate zone in the east and the south-western arm of the bioregion in an arid zone. There 

is a substantial variation in conditions throughout the bioregion. Rainfall varies both spatially 

and temporally with annual averages being of only limited value for understanding the 

requirements and responses of the vegetation and fauna. In the north there is a summer 

dominance in mean monthly rainfall but in the south it is evenly distributed throughout the 

year and the mean monthly temperatures, both maxima and minima, are lower than in the 

north. 

The native geology, topography and soils of the DRP demonstrates that this is a derived, 

water driven environment. The geological substrate is of alluvial origin, the topography is 

generally low in relief with most areas of higher elevation being the product of deposits from 

prior streams, and the soils are predominantly clays typical of alluvial fans and floodplains. 

The Collarenebri Interfluve is the most obvious exception to this. Rivers and wetlands are 

significant features of the DRP as it consists of the lower fans and floodplains of six 

catchments. Wetlands and riverine corridors are critical components of this bioregion. 

Morgan and Terrey (1992) have subdivided the DRP into smaller units (provinces) and 

Walker (1991) has mapped land systems and land units for the western third of the bioregion. 

These two classifications need to be compared and the boundaries of the provinces refined. 

Since European settlement the DRP has been subjected to high levels of disturbance with the 

impact of clearing and introduced pests combining with extreme climatic conditions in the 

1890s and the middle of this century to destroy much of the original vegetation. The extent 

and rate of land degradation must be taken into account if effective biodiversity conservation 

58


measures are to be developed. Increasing levels of salinity in the rivers, wetlands, sub-surface 

waters and the soil, and river regulation are some of the most significant problems affecting 

this bioregion in addition to the loss of extensive areas of forests and woodlands and 

consequent loss of habitat. 

2.7.2 Proposed further work 

Further work needed in relation to abiotic features of the DRP includes the following: 

detailed climatic analysis to develop an understanding of the impact of irregularity and 

unreliability of rainfall through the bioregion and through time; 

more detailed assessment of boundaries of the DRP and the provinces using detailed 

mapping of the basic abiotic features and vegetation communities; 

development of maps of land condition and the disturbance history of the bioregion; 

mapping of landunits across the bioregion; and 

mapping of landsystems over the 54% of the bioregion not currently mapped for 

landsystems. 

59


3 VEGETATION 

3.1 VEGETATION IN 1750 AND SUBSEQUENT MODIFICATION 

Prior to European settlement, the vegetation of the bioregion is likely to have been mostly 

open woodland on alluvial fans and riverine corridors, with woodland in the eastern margins 

of the bioregion and large areas of grassland. Since European settlement, this has changed to 

a predominance of grassland as a result of extensive clearing of the woodlands. An estimated 

50% of the DRP has been cleared and 28% converted to intensive agricultural production 

(DEST 1996). 

Carnahan (1976) mapped the presumed 1750 vegetation of the DRP at a scale of 1:5 000 000, 

indicating that most of the fans and the riverine corridor to near Wilcannia was a eucalypt 

woodland (10 - 30 m height,


cover had decreased for only a few sites and less than half the sites had a decrease in grass 

cover (Denny 1994). This study suggests that vegetation modification has been most 

extensive on the eastern alluvial fans of the DRP and less along the Darling River south of 

Bourke. 

The initial impact of cutting trees for timber and the effects of stock grazing, drought and 

rabbits on land condition in western NSW has been well documented. As a case study, Palmer 

(1994) describes historical changes in land condition on Teryawynia Station, south of 

Wilcannia. The manager of Teryawynia Station told the Royal Commission of 1901 that: 

‘... 100 000 acres (of a total of 463 000 acres), is as bare as the floor in spite of the 

great rains which they have had. About 50 miles of fencing has been silted up by the 

sand. All the stockyards are filled in (with sand). There is a stockyard seven feet high 

on Abermarle Station ... in less than 18 months (after erection) he drove a buggy over 

the top of the yards.’ (cited in Palmer 1994). 

In 1945 these same yards had about 50 cm of the rails above the sand and in 1983 at the time 

the drought broke, there was only about 2 cm of sand in the bottom as a result of the 

revegetation of the surrounding country. In the 1950s this Station covered 600 000 acres and 

was carrying at least 60 000 sheep with five or six watering points in addition to Darling 

River frontage. Some of the watering points had to provide water for some 20 000 sheep 

each, denuding the surrounding area for a radius of several kilometres (Palmer 1994). 

Teryawynia has now been broken up with the area of each new property being 60 000 acres 

and each carrying 5 000 sheep, with 15 or more watering points. In the 1940s most of this 

station was bare of Maireana pyramidata (black bluebush), except for scattered individuals. 

Today the same area is covered with M. pyramidata spaced between two and ten metres all 

over (Palmer 1994). This suggests that there has been a notable recovery of the vegetation in 

at least portions of the Western Division in recent times, however, M. pyramidata is generally 

regarded as a coloniser species of degraded land, particularly land which has been overgrazed 

(Lewer, S., DLWC, pers. com. Dec. 2001). If Denny had undertaken his assessment in 1950 

rather than in the early 1990s he is likely to have found a much higher percentage of sites 

with a loss of vegetation cover. 

Intensive grazing of the plant communities by domestic stock has caused a decrease in 

numbers of some species, increases in numbers of some species and has aided in the 

proliferation of exotic species. Decreasing species are those highly palatable and nutritious to 

stock and which stock grazed in preference to other species, and which became depleted in 

the plant community - for example Atriplex nummularia (old man saltbush) and A. vesicaria 

(bladder saltbush). Increasing species are those not preferentially eaten by stock, or those that 

respond positively to grazing such as Maireana spp. (bluebushes), Sclerolaena spp. 

(copperburrs), Aristida spp. (wiregrasses) and unpalatable woody shrubs. Woody shrubs were 

also advantaged by the reduction in the frequency of fire associated with grazing. Invasion of 

native plant communities by exotics has been extensive. For example, Marrubium vulgare 

(horehound) became very common on Bogan River runs only 10 years after occupation. 

There has been a rapid change in plant communities from those dominated by chenopod 

shrublands to disclimax grasslands. A disclimax community is one where recurring 

disturbances, such as grazing or periodic burning exert the predominant influence in 

maintaining the structure and composition of the steady-state vegetation. The Acacia pendula 

61


(myall) community, for example, has greatly diminished as a community and is not well 

conserved (Mitchell 1991). 

The pre-1750 vegetation of the DRP bioregion has been substantially modified but not in a 

consistent way or degree throughout the bioregion. In the eastern portion, clearing of the 

forests and woodlands on the productive alluvial plains has left an extensively changed 

landscape, one dominated by agricultural uses and containing only small patches of remnant 

native vegetation communities. In the western semi-arid portion of the bioregion the initial 

effects of overgrazing were extreme, but with changes in management there has been some 

recovery of the vegetative cover. In general terms there has been a shift from woodland to a 

larger proportion of grassland but of different and predominantly introduced species. 

3.2 VEGETATION MAPPING AND DESCRIPTION IN THE DRP 

Vegetation mapping covering the DRP is limited to very broad-scale datasets, with some 

detailed mapping of small areas. Only the Murray Darling Basin Commission basin-wide 

mapping of structural and floristic attributes of the vegetation (M305) covers the entire DRP 

(MDBC 1991) (Map 24). This M305 mapping indicates that only 6.2% of the DRP is now 

covered with woody vegetation. In the Macquarie catchment 6.4% of the area is covered with 

woody vegetation (M305). Eucalyptus populnea subsp. bimbil (bimble box) communities are 

dominant, but are in poor health, with the grassy/herbaceous E. populnea subsp. bimbil 

woodland of the relic floodplains being severely fragmented through cropping, while the 

more shrubby E. populnea subsp. bimbil woodlands have been largely affected by grazing, 

thinning, ring-barking and cropping (Lewer, S., DLWC, pers. com. Dec. 2001). Understorey 

species have almost completely disappeared and less than 13% of the region retains natural 

pastures (MDBC 1991; Macquarie 2100 report). The value of the M305 vegetation mapping 

is limited, as it omits native grasslands and shrublands with less than 20% woody cover and 

provides no specific indication of species composition or community health. 

The precision, scale, methodology and coverage of mapping with floristic interpretation 

varies throughout the region. Other broad-scale vegetation datasets are listed in Table 3.1. 

Table 3.1 Existing broad-scale vegetation mapping in the DRP 

Dataset Scale of 

mapping 

Notes / references 

62 

% of DRP 

covered 

The Vegetation of Australia 1:10 000 000 Beadle (1981) 100% 

AUSLIG Atlas of Australian 1:5 000 000 AUSLIG (1990) 100% 

Resources: Vegetation 

The Natural Vegetation of 1:1 000 000 Pickard and Norris (1994) 21% 

North-Western 

Wales 

New South 

Murray Darling Basin 1:100 000 Broad Landsat structural and floristic interpretation 98% 

Commission M305 Datalayer (nominal) 

of woody/non-woody vegetation in the Murray- 

Darling Basin (MDBC 1991). 

Conservation Atlas of Plant Point data used to Specht et al. (1995) not available in electronic form 100% 

Communities 

estimate locations – published only in hard copy. 

of vegetation 

Natural Vegetation of the 

communities 

1:250 000 Sivertsen and Metcalfe (1995) 57% 

Southern Wheatbelt


The eastern 57% of the bioregion has been mapped as part of the NPWS wheatbelt mapping 

project (Sivertsen & Metcalfe 1995). This includes systematic site survey data and includes 

updated mapping layers which incorporate information about clearing of native vegetation, 

covering the period from 1987 to 1998 (Sivertsen & Metcalfe 1999). This mapping identifies 

woody vegetation of greater than 5% cover and a remnant patch sizes of greater than 10 

hectares. 

The lower reaches of the Macquarie and Bogan Rivers have been surveyed and mapped 

during a number of studies. Beadle (1948) mapped the area in the west and Biddiscombe 

(1953,1963), the east. These maps outline the vegetation communities of the area but do not 

indicate the densities of woody vegetation cover. Steenbeeke (1996) mapped the lower 

Macquarie floodplain, upstream of the Macquarie Marshes using aerial photography; Peasley 

(1999) mapped Moree Plains and East Walgett; and Sawtell (undated) mapped the West 

Walgett and Brewarrina Regional Vegetation Committee (RVC) areas. Two additional 

surveys did not included mapping. These were the survey of native vegetation in the lower 

Macquarie valley irrigation area by Hassall and Associates (1996); and the vegetation survey 

of stock routes in the central west by Nowland (1997). The survey report by Hassall and 

Associates (1996) outlines the health of native vegetation and discusses the distribution and 

decline in woody vegetation cover since European settlement. The spatial distribution of 

recent fine-scale vegetation mapping indicates a gap in floristic community information in the 

centre of the DRP (Map 25). Lee (1925) includes excerpts from the diary of the botanist on 

Oxley’s expedition from Condobolin to the Bogan River describing the vegetation of the area. 

Surveys of the natural pastures were undertaken of the north-west slopes of New South Wales 

by Williams (1979). 

Several authors have provided general descriptions of plant communities in the DRP. In their 

descriptions of the provinces defined for the DRP, Morgan and Terrey (1992) described 

briefly the dominant plant communities. These descriptions are very broad but cover the 

entire bioregion. Plant communities in the portion of the bioregion within the western 

division of New South Wales have also been described by Walker (1991) and Cunningham et 

al. (1992), and the plant communities of the northern floodplains are described in Smith et al. 

(1998). None of these descriptions has been based on quadrat sampling or detailed plant 

community analysis. 

The Sivertsen and Metcalfe (1995) mapping also contributed to the description of plant 

communities within the eastern portion of the DRP which overlaps with the majority of the 

Macquarie catchment within the DRP, and the entire area of the Macintyre, Gwydir, Namoi 

and Castlereagh catchments within the DRP. Howling (1997) described seven woodland 

communities for the Central West catchment (including Macquarie, Bogan and Castlereagh 

Catchments), highlighting the importance of riparian, wetland, shrubland and native grassland 

communities. 

63


3.3 PLANT COMMUNITY DESCRIPTIONS 

The distribution of plant communities in the DRP is influenced by climate, landform, 

drainage and soil/substrate attributes. This distribution has been extensively modified as a 

result of European settlement and land use, the introduction of rabbits and other pest species, 

and modification of drainage regimes due to the rapid expansion of irrigation since the 1930s. 

In particular, distribution and floristic composition of grassy or herbaceous communities has 

been profoundly affected by disturbance, particularly from grazing by domestic stock and 

rotational cropping (Walker & Hodgkinson 1999; Kirkpatrick 1997; Lewer, S., DLWC, pers. 

com. Dec. 2001). 

In this section, broad descriptions of vegetation types from reports covering the DRP have 

been integrated in an attempt to provide an overview of the dominant vegetation communities 

and the changes across the landscape resulting from landform variation, increasing aridity 

from east to west and north-south climatic influences. These descriptions generally include 

the dominant species in the overstorey, shrub layer and grass cover and while they are too 

broad to indicate local variation and subtle habitat changes, they provide a general picture of 

the landscape. The vegetation descriptions are taken from Plants of Western NSW 

(Cunningham et al. 1992); land systems descriptions by Walker (1991); vegetation 

descriptions provided by Morgan and Terrey (1992); the eight communities defined for the 

northern floodplains (Smith et al 1998); and descriptions of the riverine plains of the Namoi 

catchment (NWCMC 1996). The province diagrams taken from Morgan and Terrey (1992) 

(Figure 3.1 through to Figure 3.11) indicate in more detail some of the plant communitylandform 

associations throughout the DRP. The key conservation areas are described in 

section 8.4.1. 

co-dominant co-dominant sub-dominant 

Land Profile 

Geology Medium and coarse Quaternary alluvials Fine Quaternary alluvials. Quaternary alluvials 

Landform and Soils Low, gently undulating rises. Red Plains with shallow depressions and Creek and river channels, levees 

texture contrast soils 

channels. Brown and grey clays. and immediate flood plain. 

Vegetation Woodland to open woodland of Open woodland and grasslands, 

Alluvial soils. 

River cooba, eurah, black box, 

leopardwood, wilga, budda, native includes myall, black box, belah, belah, lignum with coolabah 

orange, warrior bush with bimble box eurah, leopardwood, whitewood and becoming common in the west. 

woodland on higher areas and occasional wilga, lignum, flowering River red gum lines larger 

occasional white cypress on deeper lignum. May be prominent channels, cumbungi on 

soils. Understorey includes salt bushes understorey of old man saltbush. waterlogged areas. White cypress 

and copper burrs. Occasional rosewood Occasional areas of curly Mitchell and bimble box on coarse 

and whitewood, and, in the south, grey 

box, yellow wood and Blakely’s red 

gum. 

grass. 

textured levee deposits 

Condition Usually heavily thinned with severe Usually heavily thinned and heavily Heavily grazed. Some cropping. 

scalding. Some cropping on coarser 

soils. 

grazed. Cropping in the south. Dieback in river red gums. 

Reservation None Minor areas in Macquarie Marshes Macquarie Marshes NR 

NR 

(18 211ha) 

Key Areas 1, 2, 3 

Figure 3.1 Profile of the Bogan-Macquarie Province 

(adapted from Morgan & Terrey 1992) 

64


Land Profile 

Geology Quaternary alluvials Quaternary alluvials Quaternary alluvials 

Landform and Soils River channels, levees and lower Upper floodplains. Light grey clays Low rises and high, gently 

floodplains. Grey clays. 

and brown clays. 

undulating areas. Texture contrast 

soils, occasional sands and brown 

clays 

Vegetation Coolabah low open woodlands and Predominantly grassland of curly Bimble box woodland, with wilga, 

woodlands. Occasional myall, cooba, Mitchell grass, with occasional native orange and leopardwood; and 

whitewood and belah with areas of whitewood, coolabah, and wilga, and with whitewood, belah and 

lignum and mimosa bush. River red bimble box on low rises. 

occasional brigalow on lower areas. 

gum on larger tributaries, billabongs 

White cypress on higher, coarser 

and depressions. Occasional black 

soils in the east with silver-leaf 

box in the west. 

ironbark. Moreton Bay ash and 

occasional bloodwood on sands 

Condition Largely cultivated, particularly in the Some cultivation, usually heavily Some cultivation, largely thinned and 

east 

grazed with annual becoming heavily grazed. Scalding 

predominant 

widespread. 

Reservation None None Midkin NR (359ha) 

Boronga NR (195ha) 

Boomi West NR (149ha) 

Boomi NR (156ha) 

Key Areas 4, 5, 3, 6, 7 

Figure 3.2 Profile of the Castlereagh-Barwon Province 


Land Profile 

Land Systems Upper Darling, Long Meadow Goodooga, Wombiera Rostella, Wongal 


Landform and Soils Low level flood plains, channels. High level flood plains, occasional Low rises, some high flow channels. 

Grey clays 

Vegetation Coolabah open woodland, with 

occasional lignum, river cooba, eurah, 

golden goosefoot, whitewood, black 

co-dominant co-dominant co-dominant 

sub-dominant co-dominant 

co-dominant 

box. River red gum fringing channels. 

low rises. Grey clays. 

Grassland of Mitchell grasses and 

annuals, occasional lignum, coolabah 

and whitewood. Areas of gidgee in 

the west. 

Clays and texture contrast. 

Forblands dominated by saltbushes. 

Areas of gidgee, occasional wilga, 

leopardwood, warrior bush. Bimble 

box in the north-east. 

Condition Heavily grazed Heavily grazed, some cultivation Severe scalding and loss of tree cover 

in most areas. 

Reservation None None None 

Key Areas 8 

Figure 3.3 Profile of the Culgoa-Bokhara Province 


65


Land Profile 

Land Systems Llanillo, Upper Darling (Moonie Jomara, Gingie (in the south only) Rugby 

Geology 

River only) 

Quaternary alluvials Quaternary alluvials Quaternary alluvials, prior stream 

Landform and Soils Low level floodplain, channels. Grey 

clays 

Vegetation Coolabah, eurah, river cooba and 

lignum on wetter areas with river red 

gum on larger channels. Occasional 

bimble box and belah on higher areas. 

Areas of high grassland. 

High level floodplains, shallow 

drainage lines. Grey clays 

Coolabah open woodland with belah 

and myall. Bimble box on higher 

areas. Occasional whitewood, wilga 

and leafless cherry. 

deposits. 

Low rises, minor dunes, raised 

channels. Texture contrast soils and 

sands. Minor grey clay. 

Bimble box woodland with budda and 

wilga. White cypress on coarser soils, 

belah on finer soils. Coolabah on 

enclosed channels, usually with belah. 

Condition Heavily grazed, some cultivation Usually thinned, some cultivation Usually thinned, some clearing. Often 

severe scalding 


Key Areas 9, 10 

Figure 3.4 Profile of the Warrambool-Moonie Province 


Land Profile 

Land Systems Lightning Ridge Rotten Plain, Narran Upper Darling, Wombiera, Goodooga, Long 

Meadow, Llanillo, Nigery, Rostella, Tatala. 

Geology Fine and medium-grained Quaternary alluvials Quaternary alluvials 

Cretaceous sediments 

Landform and Soils Low rounded ridges with some 

rocky hills. Red earths and lithosols 

Vegetation Open woodland with silver leaf 

ironbark. White cypress, western 

bloodwood and mulga on coarser, 

shallower soils and bimble box on 

loamier soils and lower slopes. 

Occasional rough-barked apple, 

supplejack, warrior bush, kurrajong 

and beefwood. 

Condition Generally thinned and grazed. 

Sheet and gully erosion widespread. 

Frequent dense regrowth of cypress 

and mulga. 

co-dominant co-dominant co-dominant 

co-dominant sub-dominant co-dominant 

Extensive depressions and 

backplains, minor lunettes, 

salinas and levees. Grey clays 

Grasses and forbs within 

depressions with areas of lignum. 

River red gum fringes in wetter 

areas with river cooba, while 

coolabah fringes seasonal 

swamps with eurah. 

Level to gently undulating floodplains, low 

rises and low sand dunes. Grey clays, 

texture contrast soils and sands 

Coolabah, river red gum and occasional 

black box fringing main channels with 

scattered coolabah, myall, whitewood and 

flowering lignum on floodplains. Bimble 

box, wilga, budda, belah and occasional 

leopardwood on low rises. Supplejack, 

white cypress and wild lemon on dunes. 

Largely cultivated Generally thinned and grazed. Higher areas 

usually scalded. Coolabah regrowth dense in 

some areas. 

Reservation Kurrajong (9,000ha) None None 


Figure 3.5 Profile of the Narran-Lightning Ridge Province 


66


Land Profile 

Land Systems Araluen 

Geology Cretaceous sediments, deeply weathered 

Landform and Soils Slightly undulating with low rounded hills. Predominantly deep red earths 

Vegetation Woodlands and open forests dominated by bimble box and white cypress with budda and wilga and occasional belah 

and leopardwood 

Condition Heavily grazed with some thinning and logging. Small areas of clearing 

Reservation None 

Key Areas 13 

Figure 3.6 Profile of the Collarenebri Interfluve Province 

(Morgan & Terrey 1992) 

Land Profile 

Land Systems Mid Darling Nelyambo, minor Dunoak 

Geology Quaternary alluvials Quaternary alluvials 

Landform and Soils Main river channel and adjacent low level flood plains. 

Grey clays 

Vegetation Open forests and woodlands of coolabah and river red 

gum. Occasional black box and river cooba 

sub-dominant dominant 

High level flood plains with small channels. Small 

fringing areas of dunes and old red alluvials. Grey clays, 

minor sands and texture contrast soils 

Forbfields and grasslands, coolabah and black box on 

channels, canegrass or lignum in small pans. Higher 

fringing areas with occasional black box, rosewood and 

bimble box 

Condition Heavily grazed, some scalding Heavily grazed, scalding, minor cultivation in the north 

Reservation None None 

Key Areas 14 

Figure 3.7 Profile of the Louth Plains Province 

(Morgan & Terrey 1992) 

67


Minor 

Land Profiles 

Land Systems Mid Darling Nelyambo, areas of Thackenbe, Budda, Acres 

Billabong 

Dunoak in the north, Denian in 

the south 


Landform and Soils Main river channel and 

adjacent low level flood 

plain. Grey clays 

Vegetation Coolabah and river red 

gum fringing channels. 

Occasional black box and 

river cooba on the flood 

plain 

Condition Heavily grazed, some 

High level floodplain patterned by small lakes, low 

rises and dunes, and high level anabranches. Grey 

clays, areas of sands and texture contrast soils 

Forbfields; black box and coolabah fringing lakes and 

bases of dunes, river red gum on anabranches, lignum 

in lakes, shrubs on low rises and dunes with 

occasional rosewood. 

scalding 

Heavily grazed. Scalding common especially on 

coarser soils. 



Figure 3.8 Profile of the Wilcannia Plains Province 


Plains with low rises, pans and 

low dunes. Texture contrast soils. 

Bimble box and black box 

fringing low rises and in 

depressions, rosewood and shrubs 

on low rises. Black bluebush 

common in the south. 

Heavily grazed and scalded 

Land Profile 

Land Systems (in part) Darling Denian, Canally Teryawynia, Minor Acres Travellers, Gunnaramby, Sayers, 

Billabong 

minor Thackenbe. 

Geology Quaternary alluvials, Quaternary alluvials Quaternary alluvials Quaternary alluvials and aeolians 

minor aeolian 

Landform and Soils Darling River flood 

plain with main 

channel, billabongs, 

swamps and occasional 

low sandhills. Grey 

clay and sands 

Vegetation Black box woodlands 

and open woodlands 

with river cooba and 

areas of lignum. River 

red gum on levees. 

Condition Heavily grazed and 

scalded 

Reservation Kinchega NP 

(44 182ha) 

Key Areas To be determined 

sub-dominant dominant 

minor sub-dominant 

and aeolians 

Undulating plains 

and dunes, and 

higher alluvial 

plains. Sands, 

texture contrast soils 

and clays. 

Lower areas fringed 

by black box. Areas 

of prickly wattle, 

bluebush and woody 

shrubs. 

Local severe 

scalding and wind 

erosion 

Floodplains, backplains 

and distributary channels. 

Heavy clays, some texture 

contrast and sands. 

Scattered black box, areas 

of lignum and canegrass, 

occasional old man 

saltbush. River red gum, 

river cooba and occasional 

coolabah on larger 

channels 

Large overflow lakes and basins 

and associated lunettes. Clays, 

texture contrast earths and sands. 

Lignum on lake beds with black 

box fringing. Bluebush, sandhill 

canegrass and sparse belah and 

acacias on lunettes. 

Heavily grazed and scalded Wind and gully erosion of lunettes. 

Water levels manipulated in several 

areas for off-river storage. 

Cultivation of lake beds. 

Kinchega NP None Kinchega NP 

Figure 3.9 Profile of the Menindee Province 


dominant sub-dominant 

68


Land Profile 

Land Systems Anabranch Travellers 

Geology Quaternary alluvials Quaternary alluvials and aeolians 

Landform and Soils Floodplains, channels, billabongs and plains. Grey Large overflow lakes, lunettes and plains. Grey clays and 

clays, minor texture contrast 

Vegetation Black box open woodland with occasional river 

cooba and areas of lignum. River red gum on 

channels. 

co-dominant co-dominant 

sands 

Lignum and occasional black box on lake margins. Belah, 

white cypress and prickly wattle on lunettes. 

Condition Heavily grazed, local severe scalding Lunettes heavily grazed. Scalding and wind erosion 

Reservation None Nearie Lake NR (4 347ha) 


Figure 3.10 Profile of the Great Darling Anabranch Province 


Land Profile 

Land Systems Darling, minor Canally and Wentworth 

Geology Quaternary alluvials, minor aeolian 

Landform and Soils Floodplain, main channels, billabongs, swamps, back channels and low dunes. Grey clays and sands 

Vegetation Black box open woodland with river cooba and areas of lignum. River red gum on major channels. 

Condition Heavily grazed, areas of severe scalding 

Reservation None 


Figure 3.11 Profile of the Pooncarie-Darling Province 


The most common plant communities within the DRP are open woodlands dominated by 

Eucalyptus coolabah (coolibah), Eucalyptus largiflorens (black box) and Eucalyptus 

camaldulensis (river red gum) with significant areas of Eucalyptus populnea subsp. bimbil 

(bimble box) woodlands and grasslands and minor areas of shrublands (Cunningham et al. 

1992; NWCMC 1996). On the northern fans there is a variety of communities including 

mulga, northern floodplain community, gidgee and brigalow, bimble box and white cypress 

pine and Mitchell grass plains. Along the Darling River from Bourke to the Menindee Lakes, 

communities change from a dominance of Northern Floodplain plant communities to 

Southern Riverine Woodlands, with belah and bluebush communities becoming increasingly 

common to the south (Walker 1991). Walker’s descriptions contain greater detail than other 

reports about plant species composition in the break down of the land systems into land units 

for the Western Division. 

69


3.3.1 Forests and woodlands 

Eucalyptus populnea subsp. bimbil (bimble box) - Callitris glaucophylla (white cypress 

pine) woodlands 

These woodland communities are widespread on level to undulating lands with red and red 

brown earths, including the coarse textured ridges (levee deposits) formed by prior streams in 

the Bogan-Macquarie and Castlereagh-Barwon provinces of the bioregion, much of which is 

now cleared. The relative abundance of the two dominant species varies from almost pure 

stands of each to co-dominance. Eucalyptus populnea subsp. bimbil can occur with 

Eucalyptus largiflorens (black box) on low rises fringing the floodplain in the Wilcannia 

Plains province within the Bogan River catchment, often occurring as an ecotonal community 

on the relict floodplains, and on the outer floodplains of the Macquarie Marshes area within 

the Bogan-Macquarie province. 

Along the edge of the northern Darling River floodplain this community consists of open 

woodlands, woodlands and open forest with canopy trees ranging from four to 12 m in height 

and a canopy cover of two to 40%. Dominant tree species are Eucalyptus populnea subsp. 

bimbil, Acacia aneura (mulga), Acacia excelsa (ironwood) and Grevillea striata (beefwood). 

Common shrub species: Eremophila mitchellii (budda), Eremophila sturtii (turpentine), 

Dodonaea viscosa subsp. angustissima (narrow-leaf hopbush), Acacia aneura, Senna form 

taxon ‘filifolia’ and Geijera parviflora (wilga). Ground cover species include Monachather 

paradoxa (bandicoot grass), Eriachne mucronata (mountain wanderrie grass), Austrostipa 

spp., Sclerolaena convexula (tall copperburr), Rhodanthe floribunda (common white sunray), 

Calotis cuneifolia (purple burr-daisy), Brachyscome spp. (daisies), and Cheilanthes 

lasiophylla (mulga fern). Atalaya hemiglauca (whitewood) and Exocarpus cupressiformis 

(native cherry) are associated in Warrambool-Moonie province. 

On the red ridge country around the town of Lightning Ridge these woodlands are more 

diverse, occurring as open woodlands and woodlands with canopy height from six to 14 m 

and canopy cover from three to 20%. Dominant trees are Callitris endlicheri (black cypress 

pine), Callitris glaucophylla, Eucalyptus coolabah, Eucalyptus populnea subsp. bimbil and 

Acacia aneura. Common shrub species include Geijera parviflora, Eremophila mitchellii, 

Acacia aneura and Exocarpus aphyllus (leafless cherry). Ground cover species include 

Chloris truncata (windmill grass), Eragrostis eriopoda (woollybutt), Enneapogon spp., 

Einadia nutans (climbing saltbush), Enchylaena tomentosa (ruby saltbush), Chenopodium 

curvispicatum (cottony saltbush), Sclerolaena muricata (black roly-poly), Sclerolaena 

tricuspis (streaked poverty-bush), Sclerolaena convexula (tall copperburr), Dissocarpus 

biflorus (twin-horned copperburr), Capparis lasiantha (nepine), Marsilea drummondii 

(nardoo) and Calotis cuneifolia. 

On dunes in the Narran-Lightning Ridge province Ventilago viminalis (supplejack) and 

Canthium spp. can occur with Callitris glaucophylla and occasional Angophora floribunda 

(rough-barked apple), Ventilago viminalis, Apophyllum anomalum (warrior bush) and 

Brachychiton populneus (kurrajong).Grevillea striata (beefwood) are found with Eucalyptus 

populnea subsp. bimbil on the loamier soils and lower slopes. 

70


Casuarina cristata (belah) - Alectryon oleifolius (rosewood) woodlands 

These communities vary structurally and are widely distributed across western New South 

Wales. They generally occur on solonised brown soils or calcareous red earths as open 

forests, woodlands and open woodlands with canopy height ranging from eight to 20 m and 

cover from five to 65%. On the northern floodplains the dominant tree species is Casuarina 

cristata, which occasionally co-exists with Geijera parviflora, Eucalyptus populnea subsp. 

bimbil or Myoporum platycarpum (sugarwood). Among the common shrub species are 

Alectryon oleifolius, Nitraria billardierei (dillon bush), Dodonaea viscosa subsp. 

angustissima, Olearia pimeleoides (showy daisy-bush), Olearia muelleri (Muller’s daisybush) 

and Eremophila sturtii. Groundcover species may include Atriplex stipitata (bitter 

saltbush), Enchylaena tomentosa (ruby saltbush), Rhagodia spinescens (thorny saltbush), 

Sclerolaena diacantha (grey copperburr), Sclerolaena obliquicuspis (limestone copperburr), 

Maireana spp. (bluebushes), Austrostipa spp. (spear grasses), Zygophyllum apiculatum (gallweed) 

and Vittadinia cervicularis (a daisy). Associated species in other areas include Acacia 

loderi (nelia), Acacia homalophylla (yarran), Enneapogon spp. (bottle washers) and herbs. 

Dense monotypic forests of Casuarina cristata occur on heavy clay soils of floodplains in the 

eastern portions of western NSW. 

Eucalyptus largiflorens (black box) woodlands 

E. largiflorens common on the massive and self-mulching clay soils of floodplains, and as 

fringing communities around ephemeral lakes. In the north and west of the Bogan-Macquarie 

and Castlereagh-Barwon provinces, this community merges with Eucalyptus coolabah 

woodlands and these two species can be co-dominant. Acacia stenophylla (river cooba), 

Acacia pendula (myall), Acacia salicina (cooba), Acacia oswaldii (miljee), Eremophila 

bignoniiflora (eurah), Casuarina cristata, Muehlenbeckia florulenta, Eremophila polyclada 

(flowering lignum) and Exocarpos aphyllus are scattered throughout the community. Ground 

cover ranges from forbs and perennial grasses such as panic grasses and Paspalidium spp., to 

pasture species. 

Along the Barwon River canopy trees range from eight to 16 m in height with a canopy cover 

of ten to 60%. In addition to Eucalyptus largiflorens, dominant trees include Eucalyptus 

coolabah, Casuarina cristata, Eucalyptus populnea subsp. bimbil and Atalaya hemiglauca. 

Common shrub species are Muehlenbeckia florulenta, Chenopodium nitrariaceum and 

Eremophila mitchellii. Groundcovers include Astrebla elymoides (hoop Mitchell grass), 

Astrebla lappacea (curly Mitchell grass), Tripogon loliiformis (five-minute grass), 

Paspalidium jubiflorum (warrego summer-grass), Atriplex nummularia (old man saltbush), 

Atriplex leptocarpa (slender-fruited saltbush), Sclerolaena calcarata (red copperburr), 

Sclerolaena muricata, Dissocarpus biflorus (twin-horned copperburr), Capparis lasiantha, 

Marsilea drummondii, Centipeda cunninghamii (common sneezeweed) and Vittadinia 

cuneata (fuzzweed). 

The floodplains of the Menindee province, which represent the most southern and western 

extremity of the bioregion, are dominated by Eucalyptus largiflorens woodlands and open 

woodlands with some Acacia stenophylla. Eucalyptus camaldulensis can occur with 

Eucalyptus largiflorens on the levees and patches of Acacia victoriae (prickly wattle) grow 

on the higher alluvial plains. 

71


Eucalyptus coolabah (coolibah) woodlands 

Eucalyptus coolabah woodlands are common on clay soils in areas subject to flooding in the 

north, becoming mixed with Eucalyptus largiflorens in similar habitats in the south. Other 

tree and shrub species are uncommon, but include Eucalyptus camaldulensis, Eremophila 

bignoniiflora, Casuarina cristata, Acacia stenophylla, Atalaya hemiglauca, Capparis 

lasiantha and Exocarpos aphyllus. The groundcovers are similar to those in Eucalyptus 

largiflorens communities. In the Bogan-Macquarie and Castlereagh-Barwon provinces 

Eucalyptus coolabah can be associated with Acacia pendula (myall) Muehlenbeckia 

florulenta and Acacia farnesiana (mimosa bush). Chenopodium auricomum (golden 

goosefoot) is associated with this community in the Culgoa-Bokhara province. 

Species associated with this community vary with topography. For example, Muehlenbeckia 

florulenta occurs in wetter areas and Casuarina cristata and Acacia pendula are found on the 

higher level floodplains. 

On the floodplains of the Culgoa and Narran Rivers, Eucalyptus coolabah is found as closed 

and open forest, woodland and open woodland with tree canopy height ranging from six to 15 

m and canopy cover from five to 70%. Eucalyptus coolabah is found with varying densities 

of Acacia stenophylla, Eucalyptus camaldulensis, Eucalyptus largiflorens and Eucalyptus 

populnea subsp. bimbil. Common shrub species are Muehlenbeckia florulenta, Eremophila 

bignoniiflora, Eremophila sturtii, Myoporum montanum (western boobialla), Geijera 

parviflora and Alstonia constricta (quinine bush). Groundcover species include Paspalidium 

jubiflorum, Cyperus concinnus (trim sedge), Eleocharis pallens (pale spike-rush) and 

Muehlenbeckia florulenta. 

Eucalyptus camaldulensis (river red gum) open forests and woodlands 

These communities predominantly occur as ribbons along rivers, swamps, billabongs and 

ephemeral sandy creeks. They are widely distributed across western New South Wales and 

can be grouped as open forests, woodlands and open woodlands with canopy trees up to 20 m 

in height and a canopy cover of 40 to 50%. In addition to Eucalyptus camaldulensis, tree and 

shrub species can include Eucalyptus largiflorens, Eucalyptus coolabah, Eucalyptus 

melliodora (yellow box), Corymbia tessellaris (carbeen), Acacia stenophylla, Acacia salicina, 

Acacia oswaldii and Muehlenbeckia florulenta and ground cover frequently contains grasses, 

sedges, forbs and some low shrubs such as Enchylaena tomentosa and Chenopodium spp. 

Common shrub species on the northern floodplains include Nicotiana glauca (wild tobacco), 

Swainsona greyana (darling pea), Eremophila longifolia (emu bush), Eremophila 

bignoniiflora, Eremophila mitchelli and Muehlenbeckia florulenta, and groundcover 

Myriocephalus sturtii (poached eggs), Enneapogon avenaceus (common bottle washers), 

Capparis lasiantha and Marsilea drummondii. 

Eucalyptus melanophloia (silver-leaf ironbark) woodlands 

These woodlands typically occur in the north of the region on skeletal soils of gravelly to 

stony ridges, and on deep red sandy earths on sandplains. Associated tree and shrub species 

can include Acacia aneura, Grevillea juncifolia (honeysuckle spider flower), Hakea spp., 

Acacia excelsa, Alstonia constricta, Brachychiton populneus, Ventilago viminalis, Geijera 

parviflora, Capparis lasiantha and Callitris glaucophylla. Corymbia tessellaris can co-occur 

on the higher coarser soils and with Corymbia dolichocarpa (bloodwood) on sandy soils in 

72


the east of the Castlereagh-Barwon province and with Corymbia terminalis (western 

bloodwood) and Acacia aneura in the coarser, shallower soils of the Narran-Lightning Ridge 

province. Perennial grasses dominate the groundcover, with Triodia mitchellii var. breviloba 

(buck spinifex) common in the north, and Monachather paradoxa, Eragrostis eriopoda 

(woolybutt) and others prominent elsewhere. 

Geijera parviflora (wilga) - Flindersia maculosa (leopardwood) woodlands 

This community is mostly restricted to the Bogan-Macquarie area, occurring on red-brown 

earths that are often scalded and on low gently undulating rises away from the main 

watercourses. Communities can vary from being monotypic stands of either species to a 

mixture. Other species include Atalaya hemiglauca, Eremophila mitchellii, Capparis 

mitchellii (native orange), Apophyllum anomalum, Eucalyptus populnea subsp. bimbil (on 

higher areas) and occasional Callitris glaucophylla, Alectryon oleifolius Eucalyptus 

microcarpa (grey box) and Eucalyptus blakelyi (Blakley’s red gum) in the south. Understorey 

includes saltbushes and Sclerolaena spp. (copper burrs). This community can intergrade with 

the Eucalyptus largiflorens community on plains with shallow depressions and channels and 

Eucalyptus populnea subsp. bimbil on the higher slopes. 

On the low rises of the Culgoa-Bokhara province Geijera parviflora, Flindersia maculosa, 

Apophyllum anomalum and Acacia cambagei occur together. 

Acacia pendula (myall) woodlands 

These occur as open to dense woodlands on clay and clay loam textured soils of the river 

floodplains. Casuarina cristata, Acacia stenophylla, Acacia oswaldii, Senna artemisioides 

ssp. circinnata (spring-pod cassia), Capparis lasiantha, Acacia victoriae, Acacia 

homalophylla and Alectryon oleifolius may also occur with the Acacia pendula. The 

groundcover species include saltbushes, grasses and forbs such as Sclerolaena spp.. 

Acacia harpophylla (brigalow) woodlands 

Monotypic stands of Acacia harpophylla form on red clays and red earths with sandy clay 

loam topsoils. Shrubs are rare to absent, and the groundcover consists of saltbushes, 

Sclerolaena spp. and annual forbs. This shrubland is found in the north of the bioregion and 

in lower parts of the landscape can mix with the species of the Flindersia maculata and 

Geijera parviflora community in the Castlereagh-Barwon province. 

3.3.2 Shrublands 

Tall Acacia Shrublands 

Acacia loderi (nelia) shrublands 

This community exists on sandy calcareous red earths and sandy accumulations on broad 

plains of solonised brown soils in the west of the region. Associated trees include Acacia 

aneura in the north and Casuarina cristata in the south. Shrubs include Maireana sedifolia 

(pearl bluebush), Templetonia egena (desert broombush), Eremophila sturtii and Senna form 

taxon ‘filifolia’ (punty bush). 

Saltbush Shrublands 

This community is widely distributed across western New South Wales as forblands, open 

chenopod shrublands, chenopod shrublands and sparse shrublands. Common shrubs include 

73


Nitraria billardierei, Maireana pyramidata (black bluebush), Atriplex vesicaria (bladder 

saltbush), Atriplex nummularia, Enchylaena tomentosa, and Chenopodium nitrariaceum. 

Groundcover species include Sclerolaena diacantha, Sclerolaena obliquicuspis, Austrostipa 

spp., Calotis erinacea (tangled burr-daisy), Atriplex vesicaria, Atriplex leptocarpa (slenderfruited 

saltbush), and Atriplex lindleyi (eastern flat-top saltbush), Disphyma crassifolium ssp. 

clavellatum (pigface), Medicago minima (medic) and Sonchus oleraceus (common 

sowthistle). 

Atriplex vesicaria (bladder saltbush) shrublands 

Within the DRP this community occurs on alluvial plains with grey and brown clays and 

shallow-surfaced red-brown earths. It is often a treeless community, or has scattered 

Eucalyptus largiflorens or Acacia pendula, and occurs interspersed with wetland 

communities, watercourses and sand ridges. Associated chenopods can include Atriplex 

nummularia, Maireana pyramidata, Maireana aphylla (cottonbush), and occasionally 

Nitraria billardieri. Grasses and forbs grow between the shrubs. 

Maireana pyramidata (black bluebush) -Maireana sedifolia (pearl bluebush) shrublands 

This bluebush community exists on solinized brown soils on plains and dunefields in the 

DRP, with composition ranging from monospecific stands of either species to a mixed 

community. It often intergrades into the Atriplex vesicaria community. Grasses and forbs 

grow between the shrubs. These saltbush shrublands become more common in the south-west 

of the bioregion, occurring extensively across the southern Wilcannia Plains and the 

Menindee provinces. 

3.3.3 Grassland and wetland communities 

Astrebla spp. (Mitchell grass) perennial grasslands 

This community is common in the northern part of the bioregion, occurring on grey clay soils 

of the floodplains and is usually treeless. Other grass species found with the Astrebla spp. are 

Eragrostis setifolia (neverfail) and Dichanthium sericeum (Queensland bluegrass), as well as 

many annuals such as Iseilema spp. (Flinders grass) and Dactyloctenium radulans (button 

grass) after wet seasons. Pastoral landuses such as grazing of stock has significantly altered 

this community (Fisher 1999). 

Eriochloa australiensis (Australian cupgrass) and Eriochloa crebra (tall cupgrass) are often 

co-dominant in Astrebla lappacea (curly Mitchell grass) closed grasslands in the Bogan- 

Macquarie province. These communities also have a number of common forbs including 

Boerhavia dominii (tarvine), Hibiscus trionum (bladder ketmia), Cullen tenax (emu foot), and 

Brachyscome heterodonta (lobed-seed daisy) (Lewer, S., DLWC, pers. com. Dec. 2001). 

Astrebla lappacea occurs on upper floodplains with Atriplex nummularia and occasional 

Atalaya hemiglauca, Eucalyptus coolabah and Geijera parviflora in Bogan-Macquarie and 

Castlereagh-Barwon provinces. In the Culgoa-Bokhara province Muehlenbeckia florulenta 

and Acacia cambagei can be found in Astrebla grasslands, especially towards the west. 

Triodia mitchellii var. breviloba (buck spinifex) grasslands 

This spinifex community is restricted to the deep sands of the sandplains in the north of the 

region, often mixing with the Eucalyptus melanophloia community. Common shrubs include 

74


Grevillea juncifolia, Grevillea albiflora (white spider-flower), Acacia murrayana (sandplain 

wattle) and Acacia johnsonii (gereera wattle). 

Austrostipa aristiglumis (plains grass) grasslands 

Grey and brown clays of floodplains of major rivers support this community. Associated 

species include other grasses, perennial forbs and, following winter rains, annual grasses and 

forbs. 

Austrostipa spp. (variable speargrasses) and Enneapogon spp. (bottle washers) grassland 

This grassland community also often forms the groundcover of the Casuarina cristata - 

Alectryon oleifolius and Acacia loderi shrubland communities. It is found on solonized brown 

soils, calcareous red earths and desert loams and occurs with other grasses, chenopods, 

perennial forbs, and after winter rains, annual forbs. The dominance of Austrostipa variabilis 

is favoured by winter rains and Enneapogon spp. by summer rains. 

Floodplain communities 

A sparse to open chenopod shrubland and open grassland is found on the floodplains, playas 

and basins within the northern floodplains region. The height of this community ranges from 

0.5 to three metres and cover from five to 50%. Most common shrubs are Muehlenbeckia 

florulenta, Chenopodium auricomum (golden goosefoot), and occasionally regeneration of 

Eucalyptus camaldulensis. Ground cover species include Agrostis avenacea (blown grass), 

Eragrostis setifolia, Eleocharis pallens (pale spike-rush), Pycnosorus chrysanthus (golden 

billy-buttons), Atriplex pseudocampanulata (mealy saltbush) and Pimelea simplex (desert 

riceflower). 

Muehlenbeckia florulenta and Chenopodium nitrariaceum can form distinct communities 

although their boundaries can be indistinct depending on the degree, frequency and reliability 

of flooding. 

The Muehlenbeckia florulenta community occurs on alluvial areas with cracking grey soils 

and periodic flooding. It can be a treeless community, or have scattered Eucalyptus 

largiflorens, Eucalyptus camaldulensis, Eucalyptus coolabah or Acacia stenophylla. 

Associated shrub species include Eragrostis australasica, Leptochloa digitata (umbrella 

canegrass), Chenopodium nitrariaceum and Typha spp. (cumbungi). After floodwaters 

recede, a pasture of Marsilea drummondii, Eleocharis spp. (spike-rushes) and Eragrostis 

setifolia (neverfail) often grows between shrubs. 

Muehlenbeckia florulenta grows on the beds of the large overflow lakes and basins of the 

Menindee province, fringed by Eucalyptus largiflorens, Maireana pyramidata and Zygochloa 

paradoxa (sandhill canegrass) and sparse Casuarina cristata and acacias on the lunettes. 

The Chenopodium nitrariaceum community is found on the grey clay soils of the beds of 

periodically flooded lakes and flooded alluvial sites along major rivers. Trees are usually 

absent and complementary shrub species include Eragrostis australasica, Leptochloa digitata 

and Muehlenbeckia florulenta. Pastures similar to those found in the Muehlenbeckia 

florulenta communities occur after flooding. 

75


Eragrostis australasica (cane grass) and Leptochloa digitata (umbrella canegrass) community 

Eragrostis australasica (cane grass) swamps occur in pans in sand dune country and on 

lakebeds with compact clay soils that are subject to periodic inundation. Few species are 

associated with this community except for scattered Eremophila bignoniiflora. 

Swamp or marsh communities 

These communities occur on sites with permanent, or effectively permanent, still or slowmoving 

shallow water. Vegetation is commonly composed of Phragmites australis (common 

reed), Typha spp. and other aquatic species, with or without emergent Eucalyptus 

largiflorens, Eucalyptus camaldulensis and Eucalyptus coolabah. 

3.3.4 Plant communities of major DRP wetlands 

Mapping and survey of plant communities in some of the major wetlands within the DRP 

indicates that there are distinct differences between them. These distinctive features suggest 

that each of the wetlands is significant in its own right, as well as being critical in the 

interconnecting, but diminishing, network of wetland habitats which support waterbird 

movements. The wetlands of the DRP are dynamic and strongly influenced by the irregular 

and uneven distribution of rain events and rainfall intensity in their catchments. They are 

adapted to this variability, with the relative proportions of particular wetland vegetation 

associations varying in relation to the prevailing climatic conditions. 

The frequency and duration of flood events mostly determine the distribution, composition 

and structure of wetland plant communities. The regulation of river flows has changed the 

dynamic nature of this system, stabilising and enlarging the area of the drier plant 

communities while reducing the core wetlands and causing long term community changes 

through the loss of conditions suitable for the recruitment of some tree species (Kingsford & 

Thomas 1995). Table 3.2 below gives a brief summary of the dominant plant communities 

within the major wetlands of the DRP. 

Plant 

community 

Forests and 

woodlands 

Shrublands 

Grasslands 

and 

reedlands 

Table 3.2 Dominant plant communities of major wetlands of the DRP 

Dominant species Major wetlands of Area within each 

DRP 

major 

(ha) 

wetland 

Eucalyptus populnea subsp. bimbil woodlands Macquarie Marshes 10 023 

Eucalyptus largiflorens woodlands Macquarie Marshes 15 800 

Eucalyptus coolabah woodlands 

Macquarie Marshes 8 040 

Gwydir Wetlands 50 000 

Gingham Wetlands 150 000* 

Eucalyptus coolabah – Eucalyptus camaldulensis woodlands Gingham Wetlands 2 000 

Eucalyptus camaldulensis woodlands 


Narran Lakes nd 

Eucalyptus camaldulensis – Eucalyptus coolabah – Narran Lakes nd 

Eucalyptus largiflorens – Acacia stenophylla woodlands 

Casuarina cristata woodlands Gingham Wetlands 

Acacia pendula shrublands Macquarie Marshes 8 600 

Acacia stenophylla shrublands Macquarie Marshes 3 270 

Acacia stenophylla and Muehlenbeckia florulenta shrublands Gingham Wetlands 42 000* 

Muehlenbeckia florulenta shrublands 


Narran Lakes nd 

Phragmites australis and Typha spp. Reed beds Macquarie Marshes nd 

Marsh club-rush Bulboschoenus fluviatilis, Eleocharis plana, 

Paspalum distichum and Juncus aridicola communities 

Gwydir Wetlands 10 000 

Paspalum distichum and Eleocharis spp. communities Gingham Wetlands 13 500* 

Grasslands Macquarie Marshes 108 000 

76


* estimated area prior to construction of Copeton Dam on the Gwydir River 

nd = no data 

Macquarie Marshes 

The plant communities of the Macquarie Marshes include 108 000 ha of grassland, 10 023 ha 

of Eucalyptus populnea subsp. bimbil woodland, 8 600 ha of Acacia pendula, 2 840 ha of 

Muehlenbeckia florulenta, 15 800 ha of Eucalyptus largiflorens, 8 040ha of Eucalyptus 

coolabah, 3 270ha of Acacia stenophylla and 39 500 ha of Eucalyptus camaldulensis forest 

(Bray 1994b). Slow flowing channels have Vallisneria gigantea (ribbon reed), Potamogeton 

crispus (curly pondweed), Azolla filiculoides (red azolla), duckweeds, rushes and Paspalum 

distichum (water couch). Typha sp. occurs in the more permanently wet channels within reed 

beds. The Macquarie Marshes contain the most northern occurrence of extensive reed beds of 

Phragmites australis (Wolfgang 1998). 

In the Macquarie Marshes, tree health has been affected by variation in flood regimes, raised 

water tables and salinisation, herbicide spray drift, tree senescence, fire damage, pathogens 

and insects. The area of wetland vegetation in the Marshes has declined as a result of river 

regulation which has reduced the frequency of large and medium flows. This has, in turn, led 

to a change to a vegetation association more suited to a drier environment. Reed beds were 

formerly dominant in south marsh, but this area has recently been colonised by chenopods 

(Atriplex and Sclerolaena spp.). Weeds are also prevalent. Large areas have been cleared for 

farming, with the area of Eucalyptus camaldulensis in the southern marshes having been 

reduced from an estimated 1 406 ha in 1931 to 636 ha in 1981 (Wolfgang 1998). 

Lower Gwydir Wetlands 

The Lower Gwydir supports about 24 000 ha of semi-permanent wetland and floodplain plant 

communities, including 7 500 ha of Paspalum distichum and Juncus aridicola (tussock rush) 

and a 700 ha stand of Bolboschoenus fluviatilis (marsh club-rush), the largest area of 

Bolboschoenus fluviatilis known in New South Wales. One third of this area (2 500 ha) in the 

west is highly degraded. Intermittent wetland areas of the lower Gywdir wetlands include 4 

000ha of lignum (Muehlenbeckia florulenta) and river coobah (Acacia stenophylla). 

Approximately 4 880ha of coolibah (Eucalyptus coolabah) occurs on the floodplain of the 

lower Gywdir Wetland. Other significant plant species in this wetland include Eleocharis 

plana (ribbed spike-rush), Eleocharis sphacelata (tall spike-rush), Juncus aridicola (tussock 

rush) and Typha spp. (cumbungi) (Johnson 2001; Ramsar 1999). 

The main wetland area contains stands of dead Eucalyptus coolabah killed by prolonged 

inundation from the 1955 and 1970 floods and the release of water from Copeton Dam for 

spillway modifications in the 1970s. The dominant species in the seven distinct landform 

types within the wetland are shown on Figure 3.12 and listed in Table 3.3 (Keyte 1994). 

77


(Keyte 1994) 

(Keyte 1994) 

Figure 3.12 Profile of land units within the Lower Gwydir Wetlands 

Table 3.3 Dominant plant species in the Lower Gwydir Watercourse 

Land unit Common name Species name Nature of species 

Ridge 

windmill grass Chloris truncata 1 

curly windmill grass Enteropogon acicularis 1 

High floodplain mimosa bush Acacia farnesiana 2 

native millet Panicum decompositum 1 

curly windmill grass Enteropogon acicularis 1 

Floodplain 

warrego summer grass Paspalidium jubiflorum 1 

nutgrass Cyperus victoriensis 1 

ribbed spike-rush Eleocharis plana 1 

soft roly poly Salsola tragus 2 

Flood channel river cooba Acacia stenophylla 1 

lignum Muehlenbeckia florulenta 1 

water couch Paspalum distichum 1 

lippia Phyla canescens 2 

Watercourse tussock rush Juncus aridicola 1 

water couch Paspalum distichum 1 

soft roly poly Salsola tragus 2,3 

black roly poly Sclerolaena muricata 2,3 

black thistle Cirsium vulgare 2,3 

nardoo Marsilea drummondii 1 

lippia Phyla canescens 2 

Bathurst burr Xanthium spinosum 2,3 

Core wetland water couch Paspalum distichum 1 

sag Bolboschoenus fluviatilis 1 

black thistle Cirsium vulgare 2,3 

wild lettuce Lactuca saligna 3 

Bathurst burr Xanthium spinosum 2,3 

78


Key 

1 natural wetland species 

2 invasive species 

3 terrestrial species 

Gingham Wetlands 

The plant communities of the Gingham Wetland prior to the construction of Copeton Dam 

have been mapped using historical photos (McCosker & Duggin 1993). The communities and 

the area they covered were: 

about 2 000 ha of mixed Eucalyptus coolabah and Eucalyptus camaldulensis forests and 

woodlands at the head of the watercourse near the Gwydir Raft. Much of this forest only 

became established in the 1950s as the raft progressed and caused more extensive 

flooding in the area; 

13 500 ha of semi-permanent swamps and low wetland areas with Paspalum distichum 

and Eleocharis spp. which only dried out in exceptionally dry years; this area included 

several open water bodies; 

42 000 ha of semi-permanent core wetlands that are surrounded by Acacia stenophylla 

and Muehlenbeckia florulenta, critical habitat for waterbirds; and 

150 000 ha of open Eucalyptus coolabah woodlands which was only inundated during 

major floods. 

By 1993 about 1 000 ha of healthy Eleocharis spp. and Paspalum paspalodes (water couch) 

remained, and a further 7 000 ha still supported these plant species but insufficient flooding 

resulted in the loss of wetland vigour and weed invasion. The remaining 5 500 ha of former 

core wetland has lost almost all aquatic and semi-aquatic vegetation (McCosker & Duggin 

1993). Phyla canescens and terrestrial weeds such as Silybum marianum and Xanthium 

spinosum (Bathurst burr) occur extensively over this land. Little, if any, of the Acacia 

stenophylla and Muehlenbeckia florulenta remained in a healthy state, having not been 

flooded between 1984 and 1996. Muehlenbeckia florulenta bushes were reduced to clumps 30 

cm high while the Acacia stenophylla showed signs of extreme stress. Some areas of dead 

Eucalyptus coolabah may have resulted from prolonged inundation during the 1950s. 

Casuarina cristata and Eucalyptus coolabah are also present in the western part of the 

watercourse. Remnant lines of Casuarina cristata and numerous rotting Casuarina cristata 

logs suggest these trees were once much more abundant (McCosker & Duggin 1993). 

Narran Lakes 

There are six dominant vegetation communities in the Narran Lake Nature Reserve in 

addition to the wetland associations. These are: chenopod low open shrublands; ephemeral 

herbs; mixed low woodlands; riparian low open forest; and spinifex grassland. Other 

associations are found outside the Reserve, in other parts of the Lakes system. Extensive 

areas of river red gum with lignum occur to the south of the reserve and a large area of river 

red gum occurs to the north-east of Clear Lake. The most detailed mapping of plant 

communities has been done within the Nature Reserve. 

The wetland communities within Narran Lakes Nature Reserve are: 

sedges, grasses and ephemeral herbs on the playa lakes and the main lake beds after 

floodwaters recede; 

Muehlenbeckia florulenta in dense shrublands in extensive areas in and around Clear 

Lake and Back Lake; 

79


Phragmites australis in small patches amongst the Muehlenbeckia florulenta; 

Eucalyptus camaldulensis, Eucalyptus coolabah, Eucalyptus largiflorens and Acacia 

stenophylla association fringing the Narran River and wetland channels with 

Muehlenbeckia florulenta, Myoporum sp., Alstonia constricta, Acacia brachystachya 

(umbrella mulga) Paspalidium jubiflorum; and 

aquatic plants such as Azolla filiculoides following the inundation of wetland areas 

(NPWS 2000a). 

The sandy lakeshore and dune areas are generally treeless as a result of past grazing. Areas 

with minimal erosion support a scattered cover of Chloris truncata (windmill grass), 

Eragrostis eriopoda, Eragrostis dielsii (mallee lovegrass) and chenopods such as Sclerolaena 

spp. 

3.4 CONSERVATION STATUS OF VEGETATION COMMUNITIES IN THE 

DRP 

Three plant communities found in the bioregion have been listed as Endangered Ecological 

Communities in New South Wales under Schedule 1 of the Threatened Species Conservation 

Act (TSC Act) 1995 (New South Wales NPWS 2001a). These are: the Corymbia tessellaris 

(carbeen) open forest community; the Acacia loderi shrublands; and, the artesian springs 

ecological community. Two additional communities occurring in the DRP listed as 

endangered under the federal Environment Protection and Biodiversity Conservation (EPBC) 

Act, 1999 are: Acacia harpophylla (brigalow) (dominant and co-dominant) (this also has a 

preliminary determination under the TSC Act); and, the community of native species 

dependant on natural discharges of groundwater from the Great Artesian Basin. 

Benson (1989) considers Acacia pendula woodland with an Atriplex nummularia understorey 

to be a very poorly conserved and endangered by clearing but it has not been listed under the 

TSC Act nor the EPBC Act. 

Several communities in the Narran Lakes area are considered to be endangered, poorly 

conserved or of conservation interest (Benson 1989; Ramsar 2000). These are: 

Muehlenbeckia florulenta shrublands, with one of the largest and healthiest expanses of 

this community in New South Wales occurring at Narran Lakes; 

Eucalyptus melanophloia, Brachychiton populneus subsp. trilobus (kurrajong), Geijera 

parviflora and Grevillea striata (beefwood) woodland on sandy ridge country; 

Triodia mitchelli (spinifex) and Acacia murrayana (sandplain wattle), which are restricted 

to deep sandy soils; 

Atriplex nummularia shrubland; 

Eucalyptus populnea subsp. bimbil woodland; 

Grevillea striata and Acacia aneura shrubland; 

Eremophila maculata (native fuchsia) shrubland; 

Acacia cambagei; 

Phragmites australis sedgeland; 

Eucalyptus camaldulensis woodlands and open forests; 

Eucalyptus melanophloia woodland; and 

Acacia excelsa (ironwood) and Callitris glaucophylla shrubland. 

80


3.4.1 Corymbia tessellaris (carbeen) open forest 

Corymbia tessellaris open forest is listed as an endangered ecological community under the 

TSC Act. This community occurs on siliceous sands, earthy sands and clayey sands on the 

riverine plains of the Meehi, Gwydir, Macintyre and Barwon Rivers in the DRP and Brigalow 

Belt South bioregions. It was originally an open forest but is now more likely to be found as 

woodland or remnant trees. In addition to Corymbia tessellaris, Callitris glaucophylla, 

Corymbia dolichocarpa, Eucalyptus populnea subsp. bimbil, Eucalyptus camaldulensis, 

Casuarina cristata and Allocasuarina leuhmannii are characteristic tree species. Other plant 

species characterising the community are: 

Abutilon oxycarpum Acacia excelsa 

Acacia salicina Alectryon oleifolius 

Alstonia constricta Aristida calycina 

Atalaya hemiglauca Austrostipa scabra ssp. scabra 

Capparis mitchellii Chloris truncata 

Crinum flaccidum Cymbidium canaliculatum 

Einadia nutans Eremophila mitchellii 

Geijera parviflora Panicum decompositum 

Petalostigma pubescens Rhagodia spinescens 

Sclerolaena birchii 

The complete plant species list is larger than this but many species may be only present at one 

or two sites or have a very low abundance. The species composition of a site will be 

influenced by the size of the site and its recent disturbance history (NPWS 2001a). 

This community has been extensively cleared for grazing and cropping and is further 

threatened by clearing for agriculture, grazing, inappropriate fire management, land grooming 

for irrigation and weed invasion. The remaining stands are typically fragmented and isolated 

(NPWS 2001a). 

3.4.2 Acacia loderi (nelia) shrublands 

Acacia loderi shrublands are listed as an endangered ecological community under the TSC 

Act. The Acacia loderi shrublands are found in south western New South Wales, from 

Hillston to White Cliffs with large stands between Broken Hill, Ivanhoe and Wilcannia. 

Isolated stands are found in other areas. These shrublands grow on the solonised brown and 

duplex soils on level to undulating plains or on calcareous red earths. Most remnants are on 

pastoral lands but there are also some in Kinchega and Mungo National Parks (NPWS 

2001a). 

Acacia loderi is the dominant species and occurs with Acacia aneura, Acacia oswaldii, 

Callitris gracilis, Casuarina pauper and Flindersia maculosa. The mistletoes Amyema 

quandang and Lysiana exocarpi frequently infest A. loderi. 

81


Understorey species include: 

Aristida contorta Atriplex spp. 

Atriplex angulata Atriplex holocarpa 

Atriplex stipitata Brachyscome spp. 

Dissocarpus paradoxus Dodonaea viscosa 

Enchylaena tomentosa Enneapogon avenaceus 

Eremophila maculata Eremophila sturtii 

Grevillea huegelii Haloragis glauca forma glauca 

Ixiolaena tomentosa Lotus cruentus 

Lycium australe Maireana georgei 

Maireana pyramidata Maireana sclerolaenoides 

Maireana sedifolia Myoporum deserti 

Pimelea microcephala Plantago drummondii 

Ptilotus atriplicifolius Pycnosorus pleiocephalus 

Rhodanthe floribunda Sauropus trachyspermus 

Sida fibulifera Sclerolaena spp. 

Sclerolaena divaricata Sclerolaena obliquicuspis 

Sclerolaena patenticuspis Senna artemisioides 

Austrostipa spp. Swainsona formosa 

Templetonia egena Tetragonia tetragonioides 

Teucrium racemosum Zygophyllum simile 

3.4.3 Artesian springs ecological community 

The artesian springs ecological community is listed as an endangered ecological community 

under the TSC Act. This community is restricted in New South Wales to artesian springs at 

the southern and western margins of the Great Artesian Basin (GAB) in the north-west of the 

state, in the Mulga Lands, DRP and Cobar Peneplain bioregions. The Artesian Springs 

Ecological Community varies between springs, as they differ in shape, water flow, 

topographic position and geographic location (NPWS 2001a). Typical plant species may 

include: 

Abutilon otocarpum Acacia victoriae 

Alternanthera denticulata Alternanthera angustifolia 

Atriplex spp. Boerhavia coccinea 

Calandrinia ptychosperma Centipeda minima 

Centipeda thespidioides Chamaesyce drummondii 

Chenopodium cristatum Chenopodium melanocarpum 

Chloris pectinata Cyperus bulbosus 

Cyperus iria Cyperus laevigatus 

Cyperus squarrosus Dactyloctenium radulans 

Diplachne fusca Dodonaea viscosa subsp. angustissima 

Einadia nutans subsp. nutans Eragrostis spp. 

Eremophila deserti Eucalyptus largiflorens 

Geijera parviflora Marsilea spp. 

Oxalis spp. Portulaca oleracea 

Sclerostegia spp. Sporobolus caroli 

Stemodia florulenta Trianthema triquetra 

Eremophila sturtii Eucalyptus populnea subsp. bimbil 

82


Glinus lotoides Myoporum montanum 

Pimelea microcephala subsp. microcephala Sclerolaena spp. 

Solanum esuriale Sporobolus mitchellii 

Swainsona spp. 

Mounds of salt and sediment resulting from the evaporation of artesian water as it emerges 

through rock, are the features on which this community depends. The community often 

supports unique aquatic invertebrate and vertebrate fauna, including freshwater snail and fish 

species that may occur at one spring only. Threats include trampling and grazing by stock and 

feral animals, and the alteration of flow or unsustainable extraction of artesian water leading 

to reduce flows at mound springs. Some mound springs have dried in the past 100 years, 

probably causing the extinction of undescribed aquatic invertebrates (NPWS 2001a). 

3.4.4 The community of native species dependent on natural discharge of 

groundwater from the Great Artesian Basin. 

The community of native species dependent on natural discharge of groundwater from the 

Great Artesian Basin is listed as a threatened ecological community on the EPBC Act. This 

community includes natural surface discharge points within the GAB discharge area of 

aquifers in the Triassic, Jurassic and Cretaceous sedimentary sequence. The native species in 

this community depend on the discharge of groundwater for their existence and include some 

wide-ranging species as well as locally endemic species (restricted to one or more GAB 

spring). Examples of these species include: 

Jardinella sp. (endemic snail) 

Utricularia sp. (aquatic forb) 

Cyperus laevigatus (flora) 

Eucalyptus camaldulensis (flora) 

Myoporum desertii (flora) 

Chlamydogobius sp. (fish) 

Schoenoplectus pungens (flora) 

Cyperus gymnocaulos (flora) 

Eriocaulon carsonii (aquatic herb – 

endemic to mound springs of Peery Lake) 

Heliotropium curassavicum (flora) 

Sclerostegia sp. (flora) 

This community has become threatened through excessive extraction of groundwater from the 

GAB, leading to the extinction of some springs and a reduction in flow at remaining springs. 

Other threats include grazing and trampling by livestock and feral animals, mechanical 

modification such as dam construction and the introduction of exotic pasture species 

(Environment Australia 2001b). 

3.4.5 Acacia harpophylla (brigalow dominant or co-dominant) 

The Acacia harpophylla community is listed as threatened under the EPBC Act and a 

preliminary determination has been made to list this community as an endangered ecological 

community under the TSC Act. It has suffered a severe decline in extent since clearance of 

land for agriculture. Less than 10% of its original extent remains (Environment Australia 

2001a). Within NSW there are several species associations. These are Acacia harpophylla 

with Casuarina cristata (belah) and Geijera parviflora (wilga) or yellow wood, with wilga, 

with vine thickets of ooline or mixed species or softwoods, with Eucalyptus populnea subsp. 

bimbil (bimble box) and Eucalyptus pilligaensis (Pilliga box), with Eucalyptus coolabah 

(coolibah), with gidgee and other acacias and occur as regenerated brigalow (Pulsford 1984). 

83



3.5.1 Summary 

The vegetation of the DRP has been described in a variety of ways and at several levels of 

detail. There have been some attempts to describe the pre-European vegetation at both a 

landscape level and for smaller portions of the bioregion. However, detailed survey and 

mapping has been very limited. Broadscale mapping has mostly been from aerial photo 

analysis, which is limited to a crude structural analysis and naming of the dominant tree 

species, but this has not been extensively ground truthed. There has also been variation in the 

scale of vegetation mapping between the east and the western portions of the bioregion with 

smaller quadrat sizes being used in the east. 

In broad terms the original vegetation of the DRP is thought to have been open woodland on 

alluvial fans and riverine corridors. The height and density of the overstorey decreased from 

east to west and the grassy ground cover was dominated by Mitchell grasses (Astrebla 

species). Since European settlement the proportion of grassland has increased and is 

dominated by introduced species. Description of the pre-European vegetation is of most value 

in determining the rate and extent of change that may have occurred as a result of European 

settlement of the bioregion. The 1750 mapping by Carnahan (1976) indicates that the lower 

reaches of the Darling floodplains within the bioregion were Astrebla grasslands. This region 

then suffered from a period of extreme conditions as a result of drought in association with 

rabbit infestation and sheep grazing resulting in almost total denudation of the landscape. 

This area has now recovered and is dominated by black bluebush communities. Carnahan’s 

mapping indicates that there has been a change in the dominant plant community after the 

recovery of the landscape or that the area is at a seral stage in the re-establishment of the 

vegetation. Any attempts to map pre-European vegetation based on existing remnants should 

consider these possibilities and ensure that detailed analyses of historical documents are also 

incorporated. 

The existing broad vegetation communities within the DRP have been defined by several 

authors. These descriptions show a high degree of consistency and fifteen communities can 

be described. These include seven forest/woodland communities, tall Acacia shrublands, 

saltbush shrublands, grasslands with varying dominant genera (Astrebla, Triodia or 

Austrostipa) and wetland, swamp and marsh communities. While these community 

definitions are not based on systematic floristic surveys and could be considered subjective, 

their consistency indicates that they provide a sound broad definition of the plant 

communities of the bioregion. The fundamental importance of riverine and alluvial landforms 

is clearly demonstrated by the dominance of water tolerant communities. 

Variation within these broad plant communities has not been mapped across the bioregion but 

the mapping of land units by Walker (1991) in the Western Region and the relationship 

between topographic variation and vegetation associations indicated by Morgan and Terrey 

(1990) for all provinces provide an indication and could be analysed further. The more 

detailed vegetation descriptions for small areas within the bioregion could be used to verify 

these descriptions. 

Of the plant communities occurring within the DRP, the Corymbia tessellaris open forest, 

Acacia loderi shrublands, and the Artesian Springs community are listed under the TSC Act. 

84


In addition, the Brigalow communities and community of native species dependant on natural 

discharge of groundwater from the Great Artesian Basin have been listed under the EPBC 

Act. The Brigalow community has also been given a preliminary determination by the NSW 

Scientific Committee for listing under the TSC Act. There are other communities considered 

to be endangered, poorly conserved or of conservation interest but they have not yet been 

nominated for listing under the TSC Act. There has been no analysis of declining plant 

communities that may require monitoring and assessment. 


Further work required related to vegetation in the DRP includes the following: 

mapping of the defined broadscale plant communities across the whole bioregion in 

NSW; 

determination and mapping of ‘1750’ pre-European vegetation across the whole bioregion 

in NSW using indicators from extant vegetation and abiotic factors and validation from 

historical descriptions; 

integration of other vegetation descriptions and mapping that covers portions of the DRP 

in more detail with the broad descriptions; 

development of a systematic sampling regime to build on the existing vegetation data and 

definition in more detail of the variation within the broad communities; 

development of profiles and descriptions of plant communities present in the DRP; 

review of the conservation status of defined plant communities and, if considered to be 

under threat, preparation of nominations for listing under the TSC Act. This review will 

include assessing changes in extent of each vegetation community since European 

settlement and determining declining and threatened plant communities; 

assessment of the response of the defined vegetation communities to disturbance and 

threats present in the DRP; 

identification of threats to plant communities and preparation of nominations for listing of 

key threatening processes under the TSC Act; and 

assessment of the spatial configuration of remnants within the landscape. 

85


4 FLORA 

4.1 AVAILABLE INFORMATION 

4.1.1 Sources of data 

Plant species records from the DRP have been extracted from the databases of the Royal 

Botanic Gardens (NSW), National Herbarium, NPWS Wildlife Atlas and other vegetation 

surveys within the DRP. Other herbaria may also have plant records from the DRP but this 

information will be obtained as part of the DRP vegetation mapping, biodiversity survey and 

conservation assessment projects. 

Threatened species under the TSC Act, Schedule 13 species listed under the National Parks 

and Wildlife Act, 1974 (NSW), and ROTAP (Rare and Threatened Australian Plants) species 

were taken from the complete list. The provenance, distribution of the remaining plant species 

and most recent common names were determined from Harden (1990-94) and exotic species 

were then removed from this list and placed in a separate database. Records of questionable 

accuracy or those species not described by Harden were further investigated using the Royal 

Botanic Gardens Plants of NSW Database. Distribution and current common names were 

checked. Species still considered or a questionable reliability were deleted from the list. 

Separate lists of historical records (pre-1970) and extinct flora were also created. 

Systematic surveys 

Only a limited number of systematic floristic surveys have been conducted in the DRP and 

these are listed in Table 4.1 Not all of these surveys have full floristic sampling or precise 

location information (such as AMG reference) and some of the studies included sites from 

outside the DRP. 

86


Table 4.1 Summary of floristic surveys conducted within the DRP 

Dataset 

Site selection Survey methods No. Survey period Full 

author & date 

sites 

floristic 

Natural Vegetation of the Stratified - based on API, 20x20m, 

530 Oct 1991-Feb Yes 

Southern Wheatbelt 

replications within each cover/abundance, 

1992 

(Sivertsen & Metcalfe 1995) veg type, no private land geomorphology, 

structure 

veg 

Vegetation of Wombeira Land Stratified - based on API, 3 20x40m, 

65 30/10/90 – Yes 

System 

replications within each cover/abundance, 

10/11/90 

(Dick 1993) 

veg type 

geomorphology, 

structure 

veg 

Floristic Description of Sites stratified on 20x20m, 

152 20/2/99 – 8/5/99 Yes 

Grasslands of the Moree vegetation types 

cover/abundance, 

& 12/7/99 – 

Plains 

geomorphology, veg 10/8/99 

(Hunter & Earl 1999) 

structure 

Natural Resources Study – Sites geographically 30 x 30m, 272 2/9/96 – 31/1/97 Yes 

Murray-Darling action plan spread 

cover/abundance, 

(Centre of Environmental 

geomorphology, veg 

Management 1998) 

structure 

Vegetation survey of riparian 

3 03/10/95 - 

zones within the Namoi River 

16/05/96 

catchment, north-west New 

South Wales (Beckers 1996) 

Macquarie Marshes 

20 x 20m, 251 01/04/92 - 

Vegetation Mapping 

(Wilson 1992) 

cover/abundance 

30/10/92 

Vegetation Mapping of the Sites selected randomly 20 x 20m, cover / 90 9/96 – 11/96 Yes 

Lower Macquarie Floodplain 

abundance, 

(Steenbeeke 1996) 

geomorphology 

The survey by Dick (1993) of the vegetation of the Wombeira land system on the floodplains 

of the Culgoa, Birrie and Narran Rivers in northern NSW is one of the more intensive surveys 

undertaken to date in the DRP. This was a quadrat-based survey with structural and floristic 

data collected from sixty-five sites. 

4.1.2 Plant species diversity of the DRP 

A total of 1 129 plant taxa (species, subspecies and varieties) have been recorded from the 

DRP. Native species are listed in Appendix C and the 229 exotic plant species are listed 

Appendix D. 

Plant species records in the Wildlife Atlas are unevenly distributed across the bioregion (Map 

26) (NPWS 1999c). On a coarse scale (1:100 000 mapsheets), much of the eastern section of 

the DRP has a relatively moderate number of records (101-1000) compared with other 

regions in NSW. The southern portion of the arm of the DRP along the Darling River has few 

records. The mapsheet of the Culgoa floodplain contains the greatest number of records in the 

DRP. 

The survey by Dick (1993) recorded 175 plant species, with the species richness per 20x40 m 

quadrat ranging from an average of 25.3 species on parts of the floodplain without channels 

to 20 species in the channels and 19 species on slight rises. With the inclusion of previous 

records a total of 230 species is known from the Wombeira landsystem (Dick 1993). The 

families Asteraceae, Chenopodiaceae and Poaceae contributed the largest number of species 

87


in this survey. Introduced species were uncommon with only 17 species recorded from 32% 

of quadrats. 

4.2 SPECIES OF CONSERVATION CONCERN 

4.2.1 Threatened and ROTAP species 

Nineteen threatened species (listed in the schedules of the TSC Act) have been recorded in the 

DRP, nine of which are endangered (E1) and ten are considered vulnerable (V) (Table 4.2). 

Nine of these species are also listed as threatened on the EPBC Act. The majority of 

threatened species records are from the Menindee area with the remainder scattered 

throughout the bioregion (Map 27). Twenty species are also included on the ROTAP list 

(Briggs and Leigh 1996, Table 4.2) and four are protected by the National Parks and Wildlife 

Act 1974 (Table 4.2). 

Listed endangered species recorded from the Culgoa River floodplain are Capparis 

loranthifolia var. loranthifolia (narrow-leaf bumble), and Euphorbia sarcostemmoides 

(climbing caustic). Regionally rare species occurring on the floodplain include Aristida 

longicollis (bull wiregrass), Acacia coriacea (wirewood), Pluchea dentex (bowl daisy), 

Phyllanthus carpentariae (hairy spurge) and Pimelea penicillaris (sandplain riceflower) 

(Environment Australia 2001d). Goodenia macbarronii has been located recently in the 

Narran Lakes Nature Reserve (Hunter 1999). 

Table 4.2 Plant species of conservation concern recorded in the DRP 

Family Scientific name Common name Legal 

Status 1 

Number of 

records 

Brassicaceae Lepidium monoplocoides Winged 

*E (3ECi) 5 WLA (1), RBG (1), 

Peppercress 

NH (1), NLNRVS(2) 

Capparaceae Capparis loranthifolia var 

E 6 WLA (4), RBG (1), 

loranthifolia 

NH (1) 

Fabaceae 

Desmodium campylocaulon Creeping Tick-trefoil E 14 WLA (1), NH (1), 

(Faboideae) 

Moree(12) 

Fabaceae 

Indigofera leucotricha E 16 WLA (1), RBG (6), 

(Faboideae) 

NH (9) 

Convolvulaceae Ipomoea diamantinensis E 7 WLA (2), RBG (2), 

NH (3) 

Euphorbiaceae Phyllanthus maderaspatensis E 22 WLA (1), NH (3), 

Moree(18) 

Thymelaeaceae Pimelea elongata E 10 WLA (1), RBG (4), 

NH (5) 

Malvaceae Sida rohlenae E 9 WLA (3), RBG (2), 

NH (3), Namoi(1) 

Fabaceae 

(Faboideae) 

Swainsona adenophylla E 2 WLA (1), NH (1) 

Solanaceae Solanum karsense *V (3VCa) 58 WLA (29), RBG (14), 

NH (15) 

Surianaceae Cadellia pentastylis *V (3RCa) 2 WLA (1), NH (1) 

Fabaceae 

(Faboideae) 

Swainsona pyrophila *V (3RCa) 118 WLA 

Poaceae Bothriochloa biloba *V (3V) 3 RBG (1), NH (2) 

Sterculiaceae Rulingia procumbens *V (3V) 3 RBG (1), NH (2) 

Haloragaceae Haloragis exalata *V (3VCa) 9 WLA 

Fabaceae 

(Mimosoideae) 

Acacia carneorum Needle Wattle *V (3VCi) 14 NH (5), WLA (9) 

Fabaceae Swainsona plagiotropis *V (3VCi) 3 WLA (2), RBG (1) 

Dataset 2 

88


Family Scientific name Common name Legal 

Status 1 

(Faboideae) 

Number of 

records 

Goodeniaceae Goodenia macbarronii V (3VC-) 4 NLNRVS(4) 

Fabaceae 

(Faboideae) 

Swainsona murrayana V (3VCi) 1 Moree(1) 

Poaceae Echinochloa lacunaria 2K 9 WLA (5), RBG (4) 

Apiaceae Actinotus paddisonii 3K 7 WLA (3), RBG (4) 

Chenopodiaceae Atriplex morrisii 3K 2 WLA 

Proteaceae Persoonia cuspidifera 3K 1 BBSpil2(1) 

Chenopodiaceae Sclerolaena blackiana 3K 4 WLA (2), RBG (2) 

Rutaceae Philotheca ericifolia 3RC- 2 RBG (2), NH (2) 

Lomandraceae Lomandra patens 3RCa 1 WLA 

Rutaceae Phebalium obcordatum Club-leaved 

Phebalium 

3RCa 1 WLA 

Rutaceae Boronia rubiginosa P13 

(2RCa) 

4 WLA 

Casuarinaceae Casuarina cunninghamiana River Oak, River P13 8 WLA (6), NWB(1), 

ssp cunninghamiana 

Sheoak 

Namoi(1) 

Orchidaceae Cymbidium canaliculatum Tiger Orchid P13 125 WLA(116), NWB(8), 

BBSpil2(1) 

Fabaceae 

(Faboideae) 

Swainsona formosa Sturt's Desert Pea P13 2 WLA 

Dataset 2 

1 Identified status of species on Threatened Species Conservation Act (E1 - endangered, E4 - extinct, V - vulnerable), Environmental 

Protection and Biodiversity Conservation Act (those species listed indicted by *), National Parks and Wildlife Act 1974 (protected species - 

P13) and Rare and Threatened Australian Plants (ROTAP) (for definition of ROTAP codes see Briggs and Leigh 1996) 

2 Key 

WLA Atlas of NSW Wildlife 

NH National Herbarium, Canberra 

RBG Royal Botanic Gardens, Sydney 

BBSPil Brigalow Belt South Study - Pilliga State Forest 

BBSSF Forestry survey of the Pilliga forests 

Moree Moree Plains Grasslands survey of Moree Plains Shire and Walgett Shire east of the Barwon River 

NWB Northern Wheatbelt Vegetation Survey 

Wombeira Wombeira Landsystem Vegetation Survey 

NLNRVS Narran Lake Nature Reserve Vegetation Survey. 

MMVS Macquarie Marshes Vegetation Survey 

WFS Walgett fauna survey sites 

BrigOut Brigalow Outlier (NE of Bourke) Vegetation Survey 

Brigfauna Fauna sites for the Brigalow second survey, related to the Brigalow dataset from 1991. 

BBSPil2 Pilliga State Forest Survey - part of Brigalow Belt South Bioregional Assessment 

BBSSF&NR Brigalow Belt South Study - State Forest and Nature Reserves of the Dubbo region. 

Namoi Vegetation survey of riparian zones within the Namoi River catchment, north-west New South Wales 

4.2.2 Predicted threatened species 

Six endangered plant species, one extinct species, two vulnerable species (TSC Act 1995) and 

one ROTAP species have not been recorded, but are predicted to occur in the DRP bioregion 

on the basis of bioclimatic analysis (Table 4.3). 

Table 4.3 Plant species of conservation concern predicted to occur in the DRP 

Family Plant species Legal Status 1 

Chenopodiaceae Osteocarpum scleropterum E1 

Euphorbiaceae Monotaxis macrophylla E1 

89


Family Plant species Legal Status 1 

Fabaceae (Mimosoideae) Acacia notabilis E1 

Sapindaceae Dodonaea microzyga var. microzyga E1 

Asteraceae Leptorhynchos waitzia E1 

Poaceae Austrostipa wakoolica *E1 

Asteraceae Senecio behrianum E4 

Euphorbiaceae Bertya sp. A (Cobar-Coolabah) *V 

Brassicaceae Lepidium aschersonii *V 

Aizoaceae Glinus orygioides 3K 

1 Status codes as for Table 4.2 

4.2.3 Extinct species and historical records 

Four species now regarded as extinct in NSW (TSC Act) have been recorded from the DRP 

(Table 4.4). 

Table 4.4 Extinct plant species in New South Wales previously recorded from the DRP 

Family Scientific name Legal 

status 1 

Number of 

records 

Dataset 2 

Last date 

recorded 

Asteraceae Acanthocladium dockeri *E4 1 WLA 1788 

Proteaceae Grevillea nematophylla E4 2 WLA (1), RBG (1) 1788 

Chenopodiaceae Maireana lanosa E4 1 WLA 1800 

Brassicaceae Stenopetalum velutinum E4 2 WLA (1), RBG (1) 1903 

1 - Legal status codes as for Table 4.2 

2 - Database sources as for Table 4.2 

An additional ten listed plant species are only known from historical (pre-1970) records 

(Table 4.5). The current status of these species in the DRP is unknown and it is possible some 

may be regionally extinct. 

Table 4.5 Plant species of conservation concern known historically from the DRP but with no recent 

records 

Family Scientific name Legal 

status 1 

Number of 

records 

Last date 

recorded 

Adiantaceae Cheilanthes sieberi ssp. E1 

pseudovellea 

2 RBG (1), NH (1) 1952 

Chenopodiaceae Atriplex infrequens *V (2V) 4 WLA (1), RBG (1), NH (2) 1861 

Myrtaceae Thryptomene hexandra 3RC- 2 RBG 1913 

Rutaceae Zieria granulata *E1 1 RBG 1899 

Fabaceae 

(Faboideae) 

Indigofera efoliata *E (2E) 1 NH 1955 

Fabaceae 

(Faboideae) 

Swainsona murrayana *V (3VCi) 10 WLA (3), RBG (3), NH (4) 1955 

Fabaceae 

Swainsona recta *E1 5 WLA (1), RBG (2), NH (2) 1911 

(Faboideae) 

(3ECi) 

Eriocaulaceae Eriocaulon carsonii *E1 (3E) 2 RBG (1), NH (1) 1888 

Cyperaceae Cyperus conicus E1 2 RBG (1), NH (1) 1968 

Poaceae Dichanthium setosum *V 2 WLA (1), NH (1) 1892 

1 - Legal status codes as for Table 4.2 

2 - Database sources as for Table 4.2 

Dataset 2 

90


4.2.4 Regionally endemic species and significant populations 

There are no listed threatened populations of these species on the TSC Act 1995 and there has 

been no assessment of declining populations or regionally threatened populations. Regionally 

threatened populations are to be included in Regional Vegetation Management Plans and 

other management strategies. 

There has been no evaluation of regionally endemic species within the DRP. 

4.3 WEED AND INTRODUCED SPECIES 

There are many introduced plant species in the DRP and these are often in high densities. A 

total of 229 exotic species have been recorded (Appendix D). Some native species also 

respond very favourably to change in environmental conditions, including disturbance, and 

become agricultural weeds. The abundance of both native and weed species will vary from 

season to season depending on rainfall. Some of the most abundant ‘weeds’ include: 

blackberry Rubus fruticosus species complex 

prickly pear Opuntia stricta 

Paterson’s curse Echium plantagineum 

African boxthorn Lycium ferocissimum 

lippia Phyla canescens 

*galvanised burr Sclerolaena birchii 

variegated thistle Silybum marianum 

mimosa bush Acacia farnesiana 

water hyacinth Eichhornia crassipes 

tiger pear Opuntia aurantiaca 

* = native species which are not endemic to the DRP 


4.4.1 Summary 

Floristic surveys of the DRP have been very patchy with large areas having never been 

systematically surveyed, especially in the western half of the bioregion. The lower portion of 

the Darling River (south from Bourke to just north of Menindee) has few records in the 

NPWS Wildlife Atlas (Map 26), with most 1:100 000 scale mapsheets having only one to ten 

records. This area should be a priority for flora survey. The most detailed systematic floristic 

surveys have been conducted in the eastern and northern portions of the bioregion, such as the 

northern floodplains (Dick 1993), Moree (Hunter 1999) and the wheatbelt (Sivertsen & 

Metcalfe 1995). 

Thirty-one species of conservation concern (TSC Act, EBPC Act, ROTAP) have been 

recorded from the DRP, another ten are predicted to occur in the bioregion, four are 

considered extinct and ten have not been recorded since 1970. Very little is known about the 

distribution and abundance of these species or the processes threatening their survival. 

Targeted searches for these species are needed if they are to be managed effectively and if 

recovery plans are to be prepared. No threatened plant species listed under the TSC Act 

91


known from the DRP have a completed recovery plan. Most threatened species records are 

concentrated around Menindee (Map 27). 

A large number of introduced plant species have been recorded from the bioregion but there 

is little information about their abundance, distribution or environmental impact. The 

diversity and abundance of introduced species can be used as an indicator of community 

disturbance (Commissioner for the Environment 2000). The result of the survey by Dick 

(1993) indicated a low abundance of these species in the Wombeira landsystem but relative 

abundances of these species may be higher on the eastern alluvial fans and wetlands of the 

bioregion. Research into this area is of high priority given the extent of occurrence of some 

weed species, such as Eichhornia crassipes, Phyla canescens and Lycium ferocissimum. The 

impact of native woody weed species on the distribution and abundance of fauna is currently 

being investigated. 


Further work required in relation to flora within the DRP includes the following: 

collation and analysis of all datasets from previous surveys in the DRP; 

systematic floristic surveys across the DRP using a stratified sampling procedure based on 

a gap analysis of existing data (such as map sheets with less than ten records), to provide 

information about the patterns of plant distribution and abundance at the bioregional 

level; 

targeted surveys to locate species of conservation concern unlikely to be recorded in 

systematic surveys as a result of factors such as low abundance, seasonal conditions and 

habitat preferences; 

assessment of the status of each species and populations to identify those that may require 

listing under the TSC Act; 

identification of declining species, assessment of their rate of decline and measures 

required to prevent them becoming threatened species; 

preparation of species profiles for priority species (including threatened and declining 

species) to identify distribution and abundance, status and threats; 

population viability analysis and predictive habitat modelling for selected priority plant 

species; 

identification of areas of significance for threatened species and populations; 

preparation and implementation of recovery plans for threatened species and populations 

not already being prepared; and 

research into the abundance, impact and control of exotic plant species in the DRP. 

92


5 TERRESTRIAL 

VERTEBRATE FAUNA 

5.1 AVAILABLE INFORMATION 

5.1.1 Sources of data 

Datasets 

Records of terrestrial vertebrate fauna from the DRP have been obtained from the Atlas of 

NSW Wildlife (NPWS), Australian Museum, CSIRO, Australian Bird and Bat Banding 

Scheme, Birds Australia and various fauna survey reports. Not all of these datasets cover all 

faunal groups. Records from other sources were not included in this initial analysis and all 

records were subjected to expert review to identify dubious records. Any records considered 

to be dubious have been removed from the database used in this analysis. Records for which 

the location information appears correct but which appear doubtful are identified in the list of 

native fauna in Appendix E. 

Surveys 

Fauna surveys using systematic techniques that have been carried out in the DRP prior to this 

study are listed in Table 5.1. This table lists the study area, methods of site selection and 

fauna survey, the number of sites and the survey period for each of these studies. 

Table 5.1 Summary of systematic fauna surveys conducted within the DRP 

Dataset Site selection Survey methods 

Number of Survey period 

(* = incidental data) sites 

Midkin Nature Reserve Flora Fauna Stratified based on Elliots, pitfalls, spotlighting, 6 26/5/93 – 30/5/93 

Survey 

veg types identified bird census 

Hunt (1993b) 

through 

photography 

aerial 

Boronga Nature Reserve Biodiversity Stratified based on Elliots, cages, pitfalls, harp 14 16/9/93 – 20/9/93 

Survey 

veg types identified traps, bird census, 

Hunt (1993a) 

through 

photography 

aerial spotlighting 

Lumeah – Biodiversity and Resource Systematically Elliots, cages, pitfalls, bird 5 19/10/98 – 28/10/98 

Survey 

selected based on census*, spotlighting, herp 

Henderson (1998) 

veg types search* 

Boomi and Boomi West Nature Stratified based on Elliots, pitfalls, bird census, 6 6/12/96 – 14/12/96 

Reserves Biodiversity Survey veg types identified herp searches 

Butler (1996) 

through 

photography 

aerial 

93


Dataset Site selection Survey methods 

Number of Survey period 

(* = incidental data) sites 

Native Small Mammals and Reptiles in targeted surveys at Elliots*, pitfalls* 10 Sep-Oct 1992 & Oct 

Cropped and Uncropped Parts of specific locations 

1993 

Lakebeds 

for mammals and 

Briggs (1996) 

reptiles only 

Fauna Survey for the Gwydir Systematically Elliots, hair sampling, cages, 7 15/9/97 – 26/9/97 

Watercourse 

selected based on bird census, habitat search, 

Spark (1998) 

veg types call playback, spotlighting, 

herp search, pitfall, noc 

search, anabat 

trap* 

and harp 

Trangie Agricultural Research Centre Stratified based on Elliots, bird census*, 5 26/3/98 – 29/3/98 

– Faunal Biodiversity Survey 

Kerle (1998) 

land conditions spotlight*, pitfall, harp trap* 

Vertebrate Fauna of the Narran River Survey range of Elliots, cages, bird census, 10 3/1992 - 4/1992 

Floodplain 

Smith (1993) 

habitats 

spotlight*, pitfalls, harp traps 

Natural Resources Study – Murray- Based on veg Elliots, cages, bird census, 14 (4) 2/9/96 – 31/1/97 

Darling Water Management Action types, habitat, spotlight, pitfall, herp search, 

Plan 

disturbance & harp trap 

Centre of Environmental Management geography 

(1998) 

An Overview of the Vertebrate Fauna Stratification based Pitfall, mistnets, harp traps 13 (2) 10/1991 

of the Brigalow Belt North East of on veg types, 

Bourke, NSW 

biophysical 

Ellis and Wilson (1992) 

attributes 

Fauna of Western New South Wales - Stratification based Elliots, cages*, bird census*, 12 1994-1996 

Northern Floodplains 

on veg types, call playback*, spotlight*, 

Smith et al (1998) 

biophysical pitfall, herp search*, harp 

attributes 

trap* 

Fauna Survey in the Floodplain of the Variety of Elliots, bird census*, 4 27/3/94 – 6/4/94 

Great Anabranch of the lower Darling vegetation spotlight*, pitfall 

River 

Read (1995) 

communities 

Ecological Management of Lakebed 6 major habitats Elliots, bird census, pitfall, 8 winter & spring 1994 

Cropping on Great Anabranch 

Jenkins and Briggs (1995) 

surveyed 

Vertebrate Fauna Survey of Culgoa Range of habitats Hair sampling, cages*, 32 (approx 30/10/90-10/11/90, 

and Birrie River Floodplains 

covered 

Elliots, bird census, pitfall, 10 14/10/91-25/10/91 & 

Dick and Andrew (1993) 

herp search*, harp trap* systematic) 11/4/92 – 28/4/92 

Narran Lake Nature Reserve Targeted water Herp search*, pitfall* 7 8/11/99 – 13/11/99 

Amphibian Survey 

Henderson (1999b) 

bodies 

5.1.2 Species diversity of terrestrial vertebrates in the DRP 

Five hundred and six species of vertebrates have been recorded in the DRP in the datasets. 

These comprise 25 species of amphibian, 104 reptile species, 319 bird species and 58 

mammal species (Appendix E). Of these 65, species are listed by the NSW TSC Act, nine as 

extinct (Schedule 1, part 4), 11 as endangered (Schedule 1, part 1) and 45 as vulnerable 

(Schedule 2). The status of the species is indicated in the tables for each taxonomic group in 

addition to species of conservation concern, species listed on the JAMBA and CAMBA 

international agreements, species that have not been recorded since 1970 and exotic species. 

94


5.2 AMPHIBIANS 

5.2.1 Known species diversity and distribution 

There are 3 532 records of 25 amphibian species recorded from the DRP with both wetland 

and burrowing frogs being represented. The number of amphibian records in the DRP is 

lower than for all other vertebrate taxa and these records are unevenly distributed across the 

bioregion (Map 29). Record numbers per 1:100 000 mapsheet range from no records from 33 

mapsheets to 51 records for the mapsheet containing Narran Lake (Map 30) (NPWS 1999c). 

Eight broad herpetofaunal habitat types have been defined within the Darling Basin by Ayers 

et al. (in press), six of which are present in the DRP. These are: 

Channels - no frog species live entirely within the channels, all use the adjoining riparian 

zone as well; 

Riparian Zone - undisturbed riparian zones are generally diverse, rich and well watered 

habitats. Tree hollows and crevices, soil crevices and logs are important habitat elements. 

Species include Litoria caerulea (green tree frog) and Litoria peronii (Peron’s tree frog), 

which survive the drier times within tree hollows, and Limnodynastes tasmaniensis 

(spotted marsh frog), which shelters under logs and in soil crevices; 

Woodlands - these contain a high diversity of habitats (tree hollows, logs, soil crevices, 

temporary wetlands) and can support a high level of frog diversity; 

Shrublands – some species of burrowing frogs occur in the various shrublands, for 

example, Neobatrachus sudelli (common spadefoot toad) in Chenopod shrubland, 

Notaden bennettii (crucifix toad) in mulga communities; 

Grasslands - Canegrass contains burrowing species such as Neobatrachus sudelli 

(common spadefoot toad); and 

Wetlands - ground debris and fallen timber are used for shelter by species such as 

Limnodynastes salmini (salmon-striped frog) and Uperoleia rugosa. Several Litoria 

species rely on trees with deep hollows, spouts or hollow interiors for shelter, feeding and 

calling. 

Twenty frog species are known from the Northern Floodplain region (which includes areas 

outside the DRP), with 18 being recorded during the Northern Floodplains survey (NPWS 

1998a). Three species were also recorded from the Narran River floodplain (Smith 1993) and 

six during the Culgoa and Birrie floodplains survey (Dick & Andrew 1993). These species 

were found in all major habitats. 

Fourteen frog species have been recorded in the Gwydir wetlands with some very high 

densities, for example, 8 834 individuals of six species were caught at seven sites during 342 

pitfall trap-nights (Spark 1998). Seventeen species of frogs have been recorded in the 

Macquarie Marshes (Metcalfe et al. 1994). 

5.2.2 Species of conservation concern 

No frog species known or predicted to occur in the DRP are listed as threatened in New South 

Wales, but several have been identified as of conservation concern in the western division 

(Sadlier & Pressey 1994) and these could be found in the DRP. These are: 

Cyclorana novaehollandiae (wide-mouthed frog) 

95


Cyclorana verrucosa (warty water-holding frog) 

Litoria alboguttata (striped burrowing frog) 

Crinia deserticola 

Crinia parinsignifera. 


Seven amphibian species recorded in the DRP are either endemic to or have a majority of 

their distribution within the Darling Basin (Ayres et al. in press). These are Crinia 

parinsignifera and Crinia sloanei, Limnodynastes fletcheri (long-thumbed frog), 

Limnodynastes interioris (giant banjo frog), Neobatrachus sudelli, Notaden bennettii (crucifix 

toad) and Cyclorana verrucosa. 

No threatened populations of amphibians in the bioregion have been listed under the TSC Act 

(1995) but there has also been no detailed assessment of the status of populations of 

amphibians in the DRP. Areas such as the Gingham wetlands may be worthy of assessment. 

5.3 REPTILES 


There are 5 467 records of 104 reptile species in the datasets with dragons, skinks, goannas 

and geckoes being the most frequently reported. The distribution of reptile records from the 

Wildlife Atlas is uneven and record numbers are generally low across the whole bioregion 

(Map 31, Map 32) (NPWS 1999c). The density of records reflects the intensity of surveys 

with a high proportion of records from the Narran Lake, Culgoa floodplain and Menindee 

mapsheets. 

Seven of the eight broad reptile habitat types defined for the Darling Basin occur in the DRP 

(Ayers et al. in press). These are: 

Channels - Turtle species of the Darling River and tributaries are the only species that can 

be defined as true channel inhabitants. Several turtle species use the billabongs, oxbows 

and other associated wetlands. Turtles feed from and shelter in the channel, mating occurs 

in the water, and eggs are laid above the high water level on river and stream banks. 

Physignathus lesueurii (eastern water dragon) and Eulamprus quoyii (eastern water skink) 

have also been able to colonise the major drainage channels along the Darling River; 

Riparian Zone - Tree hollows, crevices, and hollow limbs provide a shelter for a variety of 

medium sized reptiles including Egernia striolata (tree skink), Oedura marmorata 

(marbled velvet gecko), Lophognathus gilberti (Gilbert’s dragon) and Varanus tristis 

(black-headed monitor). Gehyra dubia (northern dtella), Cryptoblepharus carnabyi 

(Carnaby’s wall skink) and Hoplocephalus bitorquatus (pale headed snake) live under 

bark while Morelia spilota variegata (carpet python) and Varanus varius (lace monitor) 

feed and shelter in trees and on the ground. Other microhabitats include logs and rocks 

harbouring fossorial reptiles such as legless lizards, blind snakes, small skinks and snakes, 

and geckoes, such as Heteronotia binoei (Bynoe’s gecko). Burrowing species include 

larger skinks of the genus Ctenotus; 

Woodlands - Arboreal reptile species are found in many woodland types and include 

Egernia striolata and Diplodactylus intermedius (eastern spiny-tailed gecko) which 

shelter in crevices and hollows or under bark. Large species such as Pogona barbata 

96


(bearded dragon) sit on trunks or limbs of trees well above ground. Litter dwelling skinks 

include Menetia greyii (Grey’s skink); 

Shrublands - Chenopod shrublands harbour Underwoodisaurus milii (thick-tailed gecko) 

and Pogona barbata. Many ground dwelling lizards occur in the woody weed shrublands 

including Rhynchoedura ornata (beaked gecko) and various Ctenotus species; 

Grasslands -Tympanocryptis lineata (lined earless dragon) and Diplodactylus tessellatus 

(tessellated gecko) are among the species that occur in canegrass habitat; 

Rocky outcrops - The DRP has few rocky outcrops, however these areas provide good 

shelter and sites for thermoregulation for reptiles such Antaresia stimsoni (Stimson’s 

python); and 

Wetlands - the rich diversity of aquatic and terrestrial habitats support turtles in 

permanent waterholes, and a variety of snake species such as Pseudechis porphyriacus 

(red-bellied black-snake), Denisonia devisi (De Vis’ banded snake) and Morelia spilota. 

Seventy-seven reptile species have been recorded from the Northern Floodplains region 

which includes areas outside the DRP. These species include four turtles, 12 geckos, five 

legless lizards, seven dragons, three goannas, 25 skinks, five blind snakes, two pythons, one 

rear-fanged snake and 13 front-fanged snakes (Smith et al. 1998). Sixty of these were 

recorded during the Northern Floodplains survey (Smith et al. 1998) and Smith (1993) found 

21 reptile species on the Narran River floodplain. Dick and Andrew (1993) list 23 species of 

reptiles (five geckos, one legless lizard, three dragons, two goannas, eight skinks and four 

snakes) from the Culgoa and Birrie floodplains and Coolibah woodlands with a grassy 

understorey contained the greatest diversity of reptile fauna. Fifty-two species of reptiles are 

known from the Macquarie Marshes (Metcalfe et al. 1994), including 14 snake species. In the 

Gwydir watercourse Spark (1998) recorded 26 reptiles including Morelia spilota and 

Chelodina expansa (broad-shelled turtle). 


Six species of reptiles recorded from the DRP bioregion are listed under the TSC Act (Table 

5.2). Another five species recorded within the bioregion are considered rare, insufficiently 

known or vulnerable under the IUCN criteria as defined by Cogger et al. (1993). Records of 

threatened reptile species in the DRP from the Wildlife Atlas are shown on Map 32. Twenty 

additional species not listed on the TSC Act have been identified as being of conservation 

concern in the western division of New South Wales (Sadlier & Pressey 1994) and those 

occurring in the DRP bioregion are listed in Table 5.2. 

Three additional listed species may occur in the DRP bioregion. Cyclodomorphus branchialis 

(Gunther’s skink) and Simoselaps fasciolatus (narrow-banded snake) are predicted by 

bioclimatic analysis to occur in the DRP. Cyclodomorphus branchialis has, however, recently 

been split into two taxa, and as such bioclimatic analysis may have to be undertaken on these 

two species separately to determine if either occur within the DRP (Ellis, M., NPWS, 

pers.com.. Dec. 2001). A turtle species Elseya belli (Namoi River elseya), is currently known 

from the Namoi and Gwydir rivers and may also occur in the DRP bioregion, with 

unconfirmed records of this species from the Macquarie Marshes (Cogger et al.1993). 

97


Table 5.2 Reptile species of conservation concern recorded within the DRP 

Common name Scientific name Conservation Number of Datasets 

status records 

broad-shelled river turtle Chelodina expansa R/IKCCSE, 22 AM (10), WLA (9), MD (2), Gwy 

RSP 

(1) 

eastern snake-necked Chelodina longicollis RWDSP 602 AM (5), WLA (576), CSIRO (15), 

turtle 

Lum, Tra (2), MD (2), Gwy (2) 

Murray turtle Emydura macquarii R/IKCCSE, 49 AM (33), WLA (11), CSIRO (1), 

IK/VWDSP 

MD (4) 

ocellated velvet gecko Oedura monilis RWDSP 15 AM (3), WLA (2), CSIRO (10) 

gibber earless dragon Tympanocryptis intima RSP 2 AM (1),WLA (1) (historic 

Anomalopus mackayi E1, VCCSE 4 

records) 

WLA 

skink Ctenotus ingrami RSP 26 AM (4), WLA (14), CSIRO (5), 

Bor (3) 

skink Ctenotus strauchii subsp 

RSP 

varius 17 AM (6), WLA (9), Bor (2) 

skink Egernia modesta RWDSP 2 AM (1), WLA (1) 

eastern water skink Eulamprus quoyii RWDSP 23 AM (8), WLA (6), MD (9) 

skink Lerista xanthura DPWDSP 28 AM (14), WLA (14) 

skink Proablepharus kinghorni RSP 19 AM (2), WLA (11), CSIRO (4), 

Cul (2) 

western 

lizard 

blue-tongued Tiliqua occipitalis V 1 WLA 

blind snake Ramphotyphlops proximus RWDSP 10 AM (5), WLA (5) 

woma Aspidites ramsayi V 2 AM (1), WLA (1) 

Stimson's python Liasis stimsoni V 2 AM (1), WLA (1) (last recorded 

in 1969 in Wilcannia) 

carpet python Morelia spilota variegata IK/EWDSP 5 WLA (4), Gwy (1) 

green tree snake Dendrelaphis punctulata RWDSP 5 AM (2), WLA (3) 

common death adder Acanthophis antarcticus R/IKCCSE, 

RWDSP 

2 AM (1), WLA (1) 

Denisonia maculata VCCSE 1 AM (last recorded in 1788 in 

Wee Waa) 

pale-headed snake Hoplocephalus bitorquatus V 16 AM (11), WLA (4), CSIRO (1) 

eastern tiger snake Notechis scutatus RWDSP 1 WLA 

fierce snake Oxyuranus microlepidotus E4 1 WLA (last recorded in 1881) 

spotted black snake Pseudechis guttatus RWDSP 42 AM (17), WLA (20), CSIRO (1), 

Gwy (4) 

red-bellied black snake Pseudechis porphyriacus RWDSP 117 AM (43), WLA (68), CSIRO (2), 

Gwy (4) 

ringed brown snake Pseudonaja nuchalis RSP 18 AM (13), WLA (3), CSIRO (1), 

MD (1) 

black-headed snake Suta spectabilis RSP 4 WLA (3), Cul (1) 

bandy bandy Vermicella annulata R/IKCCSE 21 AM (9), WLA (10), CSIRO (2) 

Key 

V Vulnerable under schedule 2 TSC Act (1995) 

E1 Endangered under schedule 1 TSC Act (1995) 

E4 Extinct under Schedule 4 of the TSC Act (1995) 

R/IKCCSE rare or insufficiently known as defined by Cogger et al 1993 

VCCSE vulnerable as defined by Cogger et al 1993 

RSP rare in NSW as defined by Sadlier and Pressey 1994 

IK/RSP insufficiently known (possibly rare) in NSW as defined by Sadlier and Pressey 1994 

RWDSP rare in the western division of NSW as defined by Sadlier and Pressey 1994 

DPWDSP disjunct population in the western division of NSW as defined by Sadlier and Pressey 1994 

IK/EWDSP insufficiently known (possibly endangered) in western division as defined by Sadlier and Pressey 1994 

IK/VWDSP insufficiently known (possibly vulnerable) in western division as defined by Sadlier and Pressey 1994 

WLA Atlas of NSW Wildlife Dataset 

AM Australian Museum Dataset 

CSIRO CSIRO Dataset 

MD Murray Darling Water Management Action Plan – Natural Resources Study (note: some records may have been detected 

outside the DRP) 

Gwy Fauna Survey for the Gwydir Watercourse 

98


Threats to reptile populations mostly come from habitat modification resulting from clearing, 

grazing pressure, cropping, predation, urban development, pasture improvement and changed 

fire regimes (Cogger et al. 1993). 


Ten reptile species recorded in the DRP are either endemic to or have a majority of their 

distribution within the Darling Basin (Ayres et al. in press). These are: Emydura macquarii, 

Delma plebeia (leaden delma), Anomalopus leuckartii (two-clawed worm-skink), 

Anomalopus mackayi, Ctenotus allotropis, Ctenotus brachyonyx, Egernia modesta, 

Hemiaspis damelii (grey snake), Pseudechis guttatus and Simoselaps australis (coral snake). 

All except Ctenotus brachyonyx (only potential occurrence) have been recorded in the 

bioregion. 

No threatened populations of reptiles have been identified in the bioregion under the TSC Act 

but changes in the distribution of several reptile species in the DRP have been noted. Morelia 

spilota has been recorded from the vicinity of the Darling and Macquarie Rivers, however 

populations around Bourke may have become locally extinct as the last record for this species 

in this area was prior to 1909 (Shine 1994; Sadlier & Pressey 1994). The range of 

Anomalopus mackayi appears to have contracted eastwards, with no recent records from west 

of Moree (Cogger et al.1993). There has been no detailed assessment of the status of 

populations of reptiles in the DRP. 

5.4 BIRDS 


There are 2 412 100 records of 319 bird species in the DRP databases. Parrots, cockatoos, 

honeyeaters, wrens, crows and birds of prey are the most frequently recorded. The 

distribution of records since 1970 across the DRP is uneven and there are many mapsheets 

with few bird records when compared with coastal NSW (Map 34, Map 35) (NPWS 1999c). 

The number of bird records per mapsheet also declines from south to north across the state. 

The central Macquarie River, Menindee Lakes and the Culgoa River floodplain have the 

highest number of bird records. 

Eighty-two species were recorded in the northern floodplain biodiversity survey, with an 

additional 73 species having been previously known from this area (Smith et al 1998). In the 

Narran Lakes area, 105 species of land birds have been recorded including 85 species listed 

by Smith (1993). In the Gwydir watercourse, Spark (1998) recorded 75 bird species, 

including two threatened birds, the barking owl and black-chinned honeyeater. Many 

additional species, including several threatened species, are recorded on the NSW NPWS 

Atlas for the area (Spark 1998). Dick and Andrew (1993) recorded 112 species of native bird 

and one introduced species in their systematic surveys of fauna in the Culgoa and Birrie River 

floodplains. Like the Narran lakes, most bird species were from the woodland habitats. 

Waterbirds are a significant component of the bird fauna of the DRP and the wetland bird 

communities, particularly in the Macquarie Marshes and Narran Lakes, have been more 

intensively studied than terrestrial communities. Both these wetlands are significant sites for 

waterbird breeding in southern Australia and during the floods of 1990 supported the largest 

99


breeding colonies of ibis in the Murray-Darling basin (Smith 1993). In general, there are very 

few major colonial waterbird breeding sites in Australia, consequently those that exist are 

extremely important. Ibis breeding is localised and uncommon and is triggered by wetland 

flooding. In general terms, the bigger the flood, the bigger the breeding response (Maher 

1999). 

Estimated population sizes of the colonial nesting waterbird species in the three most 

significant wetlands in the DRP are: 

Ibis (three species): 100 000 to 150 000 Gwydir Wetlands; 75 000 to 80 000 Narran; 70 

000 to 75 000 Macquarie Marshes (800 glossy ibis, 2 000 Australian white ibis, more than 

12 000 straw-necked ibis); 

Large egret: 10 000 to 15 000 Gwydir Wetlands; 3 000 to 5 000 Macquarie Marshes; 

Intermediate egret: 17 000 Macquarie Marshes; 

Rufous night heron: 10 000 to 15 000 Gwydir Wetlands; 

Australian pelican: 1 000 to 1 500 Narran Lakes; 

Magpie geese: eight pairs Narran; 20 pairs Gwydir Wetlands; 20 pairs Macquarie 

Marshes; 

Royal spoonbill: 8 000 to 9 000 pairs in Narran Lakes; and 

Brolga: six to eight pairs Macquarie Marshes. 

These estimated numbers confirm the significance of these wetlands within NSW and the 

Murray-Darling Basin (Kingsford & Thomas 1995; Maher 1999). 

The Macquarie Marshes provide habitat for more than 70 species of waterbirds, including 42 

species that breed in the area, and 130 species of land birds. It is one of the few wetlands 

supporting breeding colonies of all four species of egret and three species of ibis. The 

threatened magpie goose has also bred in the wetlands. In 1984, the marshes supported at 

least 88 000 waterbirds, considerably more than any other wetland in the area (Kingsford & 

Thomas 1995). 

Sixty-five species of waterbirds have been recorded from the Narran wetlands and 46 species 

breed in the area (Ley 1998a; Ley 1998b; Henderson 1999a). The wetlands support the largest 

recorded breeding colonies in Australia of straw-necked ibis, little black cormorant and royal 

spoonbill and large numbers of sixteen other species (NPWS 2000a; Ramsar 2000). An 

estimated 200 000 pairs of ibis bred in the Narran Lake Nature Reserve in 1983, the largest 

breeding event ever recorded in Australia (Marchant & Higgins 1993). Smith (1993) lists the 

estimated number of breeding pairs of waterbirds at Narran Lake during the period 1971 to 

1991 as ranging from 50 to 200 000 pairs in any one year, and these numbers are largely 

dependant on inundation and water availability. Narran wetlands flood every two to three 

years on average, which is more frequent than most other wetlands in north western New 

South Wales (NPWS 2000a). 

Threatened species known to breed at Narran Lakes include the brolga (Grus rubicunda), 

blue-billed duck (Oxyura australis), freckled duck (Stictonetta naevosa) and the most western 

known breeding record of magpie geese in New South Wales. Breeding occurs in lakes and 

associated channels (Ley 1998a; NPWS 2000a). Large numbers of waders, including the 

threatened black-tailed godwit (Limosa limosa), also congregate on freshly exposed mudflats 

after flooding, and eleven of these species are listed under the JAMBA and CAMBA 

agreements (Ley 1998a). 

100


Lake Menindee, Lake Cawndilla and associated wetlands provide important waterfowl 

habitat, breeding sites and drought refuge in the New South Wales western division. 

Breeding species include cormorants, egrets, pelicans, spoonbills, darters and ibis. Annual 

aerial waterbird surveys have been undertaken by Kingsford et al. (2002) since 1983 over 

NSW. Major wetland areas within the DRP which are covered by this survey include 

Menindee Lakes (includes Lake Cawndilla, Lake Menindee, Emu Lake and Eurobilli Lake) 

and the Macquarie Marshes. A summary of waterbird counts for these wetlands is shown in 

Appendix F. This summary shows that the waterbird species with the highest counts recorded 

by Kingsford et al. (2002) during the survey period between 1983 and 2001 for the 

Macquarie Marshes were: 

grey teal - with 82 378 records overall and a yearly range from 84 records in 1991 to 48 

881 records in 1984; 

straw-necked ibis - with 47 706 records overall and a yearly range from 15 records in 

2001 to 11 269 records in 1984; 

pacific black duck - with 17 426 records overall and a yearly range from five records in 

1994 to 6 006 records in 1983; and 

Australian white ibis - with 15 227 records overall and a yearly range from three records 

in 2000 to 6 739 records in 1983. 

Appendix F also shows that the waterbird species with the highest counts recorded by 

Kingsford et al. (2002) during the survey period between 1983 and 2001 for the Menindee 

Lakes were: 

grey teal - with 48 997 records overall and a yearly range from two records in 1998 to 44 

923 in 1995; 

pink-eared duck - with 15 671 records overall and a yearly range from four records in 

1990 to 13 832 records in 1995; 

little black cormorant - with 8 096 records overall and a yearly range from two records in 

1990 to 3 164 records in 1984; and 

Eurasian coot - with 7 585 records overall and a yearly range from 14 records in 1998 to 

2 780 records in 1987. 


Eight endangered and 32 vulnerable bird species have been recorded in the DRP. These 

species and those listed on the international treaties, JAMBA and CAMBA, are listed in 

Table 5.3 and the post - 1970 records of threatened species have been plotted on Map 36. 

Some of the recorded threatened species include: from Narran Lake Nature Reserve - 

Australian bustard (Ardeotis australis), grey falcon (Falco hypoleucos), Major Mitchell’s 

cockatoo (Cacatua leadbeateri), barking owl (Ninox connivens) and masked owl (Tyto 

novaehollandiae) (NPWS 2000a); from Culgoa and Birrie River floodplains - grey falcon, 

Australian bustard, Major Mitchell’s cockatoo and painted honeyeater (Grantiella picta); and, 

from Kinchega National Park - freckled duck and Major Mitchell’s cockatoo (NPWS 1996). 

Eighteen threatened bird species and nine species protected by JAMBA and CAMBA 

agreements have been recorded in the Macquarie Marshes. 

101


Garnett and Crowley (2000) have evaluated the national conservation status of all Australian 

birds against the internationally recognised criteria developed by the International Union for 

the Conservation of Nature (IUCN). A number of taxa not currently recognised as threatened 

in New South Wales were identified, including several species and subspecies of birds 

currently thought to be in decline (see over page). Conversely, several listed threatened taxa 

in New South Wales (TSC Act), have not been identified as being threatened nationally. 

These species and their recommended status are listed in Table 5.3. Endangered species are 

those facing a very high risk of extinction in the wild in the near future, Vulnerable, those 

facing a high risk of extinction in the medium-term future and near-threatened species and 

those close to qualifying for vulnerable (IUCN 1994; Maxwell et al. 1996). Subtropical 

woodlands (in portions of the DRP, Brigalow Belt South, Nandewar and New England 

Tablelands bioregions) have been identified in Garnett and Crowley (2000) as key areas for 

the conservation of several threatened or near-threatened bird species. The conservation status 

of bird species from the western division of New South Wales has also been assessed by 

Smith et al. (1994) and species of concern in the DRP are listed in Table 5.3. 

Table 5.3 Bird species of conservation significance recorded from the DRP. 

Common name Scientific name Conservation Number of Dataset 

status 

records 

brown quail Coturnix ypsilophora PTWDSPS 14 AM (1), WLA (10), Cul (1), MD (2) 

malleefowl Leipoa ocellata E1, VGC, *VSPS 2 AM (1), WLA (1) 

red-chested button-quail Turnix pyrrhothorax PTWDSPS 18 BA (8), AM (1), WLA (9) 

brown booby Sula leucogaster J & C 1 BA 

red-tailed tropicbird Phaethon rubricauda V, NTGC 1 WLA 

magpie goose Anseranas semipalmata V, EvSPS 344 WLA (340), Narw (4) 

freckled duck Stictonetta naevosa V, *PTSPS 1,314 BA (25), AM (3), WLA (1285), CSIRO 

(1) 

cotton pygmy-goose Nettapus coromandelianus E1, NTGC 1 WLA 

blue-billed duck Oxyura australis V, PTWDSPS 457 BA (17), WLA (442), Narw (1) 

Lewin's rail Rallus pectoralis ExWDSPS 8 WLA 

great egret Ardea alba J & C 4,662 BA (339), AM (11), ABBBS (1), WLA 

(4134), Cul (5), Narw (168), MD (4) 

cattle egret Ardea ibis J & C 623 BA (16), WLA (604), Narw (2), Gwy 

(1) 

black bittern Ixobrychus flavicollis V, XSPS 1 BA 

little bittern Ixobrychus minutus NTGC 22 BA (7), AM (1), WLA (13), CSIRO (1) 

Australasian bittern Botaurus poiciloptilus V, VGC, *PTSPS 6,753 BA (15), AM (1), WLA (6737) 

black-necked stork Ephippiorhynchus asiaticus E1 13 BA (9), WLA (4) 

glossy ibis Plegadis falcinellus C 25,329 BA (134), AM (5), WLA (25153), 

CSIRO (1), Cul (2), Lum, Narw (34) 

brolga Grus rubicunda V, PTSPS 585 BA (126), AM (10), WLA (449) 

whimbrel Numenius phaeopus J & C 2 BA 

wood sandpiper Tringa glareola J & C 10 BA (1), WLA (9) 

common greenshank Tringa nebularia J & C 591 BA (42), WLA (544), Narw (1), MD (4) 

marsh sandpiper Tringa stagnatilis C 629 BA (21), WLA (132), Narw (475), MD 

(1) 

common sandpiper Actitis hypoleucos J & C 27 BA (8), WLA (19) 

Latham's snipe Gallinago hardwickii J & C, 254 BA (48), AM (1), WLA (205) 

bar-tailed godwit Limosa lapponica 

PTnWDSPS 

J & C 5 BA (3), WLA (2) 

black-tailed godwit Limosa limosa V (J & C) 136 BA (6), WLA (60), Narw (70) 

red knot Calidris canutus J & C 1 WLA 

sharp-tailed sandpiper Calidris acuminata J & C 8,263 BA (44), AM (2), WLA (7727), Narw 

(490) 

red-necked stint Calidris ruficollis J & C 212 BA (5), WLA (207) 

sanderling Calidris alba V (J & C) 2 WLA 

102



status 

records 

curlew sandpiper Calidris ferruginea J & C 12 BA (3), WLA (9) 

painted snipe Rostratula benghalensis V, VGC, *PTSPS 22 BA (8), AM (4), WLA (10) 

bush stone-curlew Burhinus grallarius E1, NTGC, VSPS 66 BA (21), WLA (45) 

lesser golden plover Pluvialis dominica J & C 1 BA 

grey plover Pluvialis squatarola J & C 1 WLA 

lesser sand plover Charadrius mongolus V (J & C 7 WLA 

white-winged black tern Chlidonias leucopterus J & C 553 BA (1), WLA (352), Narw (200) 

caspian tern Sterna caspia C 212 BA (25), WLA (131), Narw (11), MD 

(45) 

letter-winged kite Elanus scriptus PTSPS 6 BA (4), WLA (1), CSIRO (1) 

osprey Pandion haliaetus V 1 WLA 

black-breasted buzzard Hamirostra melanosternon V, PTSPS 22 BA (7), ABBBS (1), WLA (14) 

square-tailed kite Lophoictinia isura V, *PTSPS 42 BA (6), WLA (33), MD (3) 

turquoise parrot Neophema pulchella V, NTGC, *PTSPS 8 BA (2), AM (1), WLA (5) 

red goshawk Erythrotriorchis radiatus E1, VGC 1 WLA 

grey falcon Falco hypoleucos V, NTGC, *PTSPS 22 BA (9), AM (2), WLA(8), Cul(3) 

flock bronzewing Phaps histrionica E1, 

EvSPS 

NTGC, 3 WLA 

red-tailed black-cockatoo Calyptorhynchus banksii V, PTSPS 2,683 BA (117), AM (2), WLA (2559), 

CSIRO (5) 

glossy black-cockatoo Calyptorhynchus lathami V, (subsp lathami 112 

NTGC), *PTSPS 

BA (24), WLA (88) 

Major Mitchell's cockatoo Cacatua leadbeateri V, (subsp 529 BA (103), ABBBS (19), WLA (402), 

leadbeateri 

NTGC) 

CSIRO (1), Cul (4), Lum 

regent parrot Polytelis anthopeplus E1(subsp 1 BA (1) 

superb parrot Polytelis swainsonii 

monarchoides 

EGC), *VSPS 

*V, VGC, *VnSPS 323 BA (14), AM (5), ABBBS (4), WLA 

(173), CSIRO (2), Tra (125) 

Bourke's parrot Neopsephotus bourkii PTSPS 1 BA 

barking owl Ninox connivens V, (subsp 25 AM (3), BA (14), Bor, MD (1), Gwy (7) 

grass owl Tyto capensis 

connivens NTGC), 

PTWSDPS 

V 13 BA (1), WLA (12) 

fork-tailed swift Apus pacificus J & C 23 BA (12), WLA (9), Gwy (2) 

white-throated needletail Hirundapus caudacutus J & C 37 BA (22), WLA (4), MD (11) 

red-browed pardalote Pardalotus rubricatus PTSPS 11 BA (1), WLA (10) 

redthroat Pyrrholaemus brunneus V, PTSPS 1 CSIRO 

striated fieldwren 1 

Calamanthus fuliginosus V 1 BA 

speckled warbler Chthonicola sagittata V, NTGC 7 BA (5), ABBBS (1), WLA (1) 

noisy friarbird Philemon corniculatus PTWDSPS 98 BA (58), WLA (36), Bor, Boo, Cul (4), 

Lum 

black-chinned honeyeater Melithreptus gularis V (subsp gularis 54 BA (23), AM (2), WLA (17), Cul (2), 

NTGC), 

PTWDSPS 

MD (8), Gwy (2) 

painted honeyeater Grantiella picta V, NTGC, *PTSPS 22 BA (14), WLA (7), Cul (1) 

chestnut-breasted 

thrushquail- 

Cinclosoma castaneothorax *PTSPS 5 WLA 

grey-crowned babbler Pomatostomus temporalis V, NTGC 784 BA (415), AM (26), ABBBS (10), WLA 

temporalis 

(313), CSIRO (2), Cul (14), Tra (2), 

MD (1), Gwy (1) 

hooded robin Melanodryas cucullata V 312 BA (196), AM (10), ABBBS (3), WLA 

(80), Cul (13), Nar (7), MD (3) 

crested shrike-tit Falcunculus frontatus PTWDSPS 88 BA (39), AM (3), WLA (33), Cul (5), 

MD (8) 

Gilbert's whistler Pachycephala inornata V, PTSPS 6 BA (4), WLA (2) 

golden whistler Pachycephala pectoralis PTWDSPS 39 BA (21), AM (2), WLA (11), MD (5) 

olive-backed oriole Oriolus sagittatus PTWDSPS 93 BA (66), ABBBS (2), WLA (25) 

diamond firetail Stagonopleura guttata V, NTGC, 88 BA (26), AM (2), ABBBS (12), WLA 

PTWSPS 

(48), Lum 

103



status 

records 

Australian bustard Ardeotis australis E1, NTGC 70 BA (2), AM (5), WLA (62), Cul(1) 

1 Calamanthus fuliginosus has recently been split into two separate species, striated fieldwren Calamanthus 

fuliginosus, and the rufous fieldwren Calamanthus campestris (Christides and Boles 1994). The rufous 

fieldwren occurs in the DRP, with recent records from near Menindee (Map 36). To date the impact of this 

taxonomic revision on the schedules of the TSC Act and their interpretation have yet to be determined. 

Key 

V Vulnerable under schedule 2 TSC Act (1995) An asterix denotes those species which are also listed as nationally vulnerable under the EPBC 

Act. 

E Endangered under schedule 1 TSC Act (1995) 

J JAMBA: agreement between the government of Australia and the government of Japan for the protection of migratory birds and birds in 

danger of extinction and their environment 

C CAMBA: agreement between the government of Australia and the government of the People’s Republic of China for the protection of 

migratory birds and their environment 

EGC endangered as defined by Garnett and Crowley 2000 

VGC vulnerable as defined by Garnett and Crowley 2000 

NTGC near threatened as defined by Garnett and Crowley 2000 

*ExSPS Extinct at a national and taxon level as defined by Smith et al 1994 

*ESPS Endangered at a national and taxon level as defined by Smith et al 1994 

*VSPS vulnerable at a national and taxon level as defined by Smith et al 1994 

*VnSPS vulnerable at a national and taxon level as defined by Smith et al 1994 with recent records probably only non-breeding 

*PTSPS possibly threatened at a national and taxon level as defined by Smith et al 1994 

ExSPS extinct in New South Wales as defined by Smith et al 1994 

EvSPS endangered in New South Wales as defined by Smith et al 1994 with recent records probably only vagrants 

VSPS vulnerable in New South Wales as defined by Smith et al 1994 

PTSPS possibly threatened in New South Wales as defined by Smith et al 1994 

ExWDSPS extinct in the western division of New South Wales as defined by Smith et al 1994 

PTWDSPS possibly threatened in the western division of New South Wales as defined by Smith et al 1994 

PTnWDSPS possibly threatened in the western division of New South Wales as defined by Smith et al 1994 with recent records probably only nonbreeding 

BA Birds Australia Dataset 




Bor Boronga NR Biodiversity Survey 

Cul Culgoa and Birrie River Floodplain Vertebrate Fauna Survey 

Lum Lumeah (Narran Lake NR) Biodiversity Survey 

Narw Narran Lake NR Waterbird Monitoring Program 

Tra Trangie Agricultural Research Centre - Faunal Biodiversity Survey 

MD Murray Darling Water Management Action Plan - Natural Resources Study (note: some records may have been detected outside the DRP) 

This list of threatened species occurring in the DRP is not necessarily comprehensive, as it 

includes only the datasets identified in Section 5.1. Other species, such as Hall’s babbler from 

Culgoa National Park have also been recorded (NPWS 2001b). The endangered swift parrot 

(Lathamus discolor), squatter pigeon (Geophaps scripta), and plains wanderer (Pedionomus 

torquatus), and the vulnerable scarlet-chested parrot (Neophema splendida), southern scrubrobin 

(Drymodes brunneopygia), masked owl (Tyto novaehollandiae) and pied honeyeater 

(Certhionyx variegatus) are predicted by bioclimatic analysis to occur in the DRP. 

In their analysis of the birds of conservation concern of the New South Wales western 

division, Smith et al. (1994) defined 60 threatened species and sub-species of native birds. 

Twenty-three of these are listed as threatened at the national level (EPBC Act), 23 are listed 

as threatened in New South Wales (TSC Act) and 14 considered under threat in the Western 

Division. Smith et al. (1994) also identified another 31 species of conservation concern 

because of their restricted breeding distribution in the division. This analysis includes more 

habitats than are present in the DRP bioregion. 

The analysis by Smith et al. (1994) is complemented by the analysis of threatened and 

declining birds in the New South Wales sheep-wheat belt (Reid 1999) which covers the 

eastern portion of the DRP. In addition to the species formally listed under the TSC Act, this 

104


analysis identified declining species. Eighty-five species of birds were identified in at least 

one study of wheatbelt birds to be locally extinct, declining or otherwise at risk and 16 

species were identified to be locally extinct, declining or otherwise at risk in at least three 

studies. These were the emu (Dromaius novaehollandiae), painted button-quail (Turnix 

varia), brown treecreeper, chestnut-rumped thornbill (Acanthiza uropygialis), southern 

whiteface (Aphelocephala leucopsis), jacky winter (Microeca fascinans), red-capped robin 

(Petroica goodenovii), eastern yellow robin (Eopsaltria australis), white-browed babbler 

(Pomatostomus superciliosus), varied sittella (Daphoenositta chrysoptera), crested shrike-tit 

(Falcunculus frontatus), crested bellbird, rufous whistler (Pachycephala rufiventris), restless 

flycatcher (Myiagra inquieta), white-browed woodswallow (Artamus superciliosus) and 

dusky woodswallow (Artamus cyanopterus). All of these species are found within the DRP. 

They occur in temperate eucalypt woodland habitats and represent a suite of formerly 

common and widespread bird species of the woodlands of the DRP that is in decline. 

Traill and Duncan (2000) also assessed the conservation status of woodland birds in NSW 

and defined the eastern population of the crested bellbird as an endangered population, and 

another ten species as ‘near threatened’, as defined by IUCN criteria. They also defined a 

temperate woodland bird community and suggested that this community satisfies the criteria 

required for listing as an endangered ecological community. 

Historical evidence indicates a massive change in the abundance and distribution of the flock 

bronzewing in the DRP. Collectors and naturalists from 1839 to 1920 recorded this species 

on a number of occasions on the northern plains in the Narrabri, Moree and Gwydir districts, 

occasionally in large flocks (thousands) and breeding. In more recent times, there have been 

few records from the DRP, with the most recent being of a single bird south west of 

Goodooga in 1988. The decline of this pigeon throughout its range in New South Wales, 

where it is now only an irregular visitor, has been linked to the spread of livestock and rabbits 

and their impact on grassland habitats (McAllan 1996). 

Waterbird habitats and breeding requirements have also been adversely affected by human 

activities. Major change to hydrological regimes, combined with clearing and agricultural 

activities has substantially decreased the amount of inland waterfowl habitat and breeding 

sites and has changed flooding regimes (Briggs et al.1994). 


No threatened populations of birds have been listed for the bioregion in the TSC Act but 

several species have a large proportion of their total distribution within the bioregion. These 

include the spotted bowerbird (Chlamydera maculata), striped honeyeater (Plectorhyncha 

lanceolata) and plum-headed finch (Neochmia modesta). In New South Wales, the red-tailed 

black cockatoo is closely associated with Eucalyptus camaldulensis woodland, requiring the 

large hollows for nesting (Smith et al. 1994). Nearly all records of red-tailed black cockatoos 

in New South Wales are from the DRP bioregion, primarily in the vicinity of the Barwon- 

Darling River. This population of the red-tailed black cockatoo may also be isolated from 

other populations of the species (Simpson et al. 1999). The conservation of this population, 

and the other bird species identified as having large portions of their range within the DRP, 

will depend on land management within the DRP. 

105


5.4.4 Introduced and pest species 

Six feral bird species have been recorded from the DRP (Table 5.4, Map 37). The number of 

records of each species has been included to indicate the severity of the problem posed by 

these species. 

Table 5.4 Feral bird species recorded in the DRP 

Common name Scientific name Number of records Dataset 

mallard Anas platyrhynchos 4 BA (2), WLA (2) 

rock dove Columba livia 158 BA (101), WLA (55), MD (1), Gwy (1) 

house sparrow Passer domesticus 468 BA (337), WLA (130), Tra, MD (1) 

spotted turtle-dove Streptopelia chinensis 2 BA 

common starling Sturnus vulgaris 1 193 BA (670), AM (3), WLA (488), Tra (>30), 

Gwy (2) 

common blackbird Turdus merula 9 BA (8), WLA (1) 

Key 





MD Murray Darling Water Management Action Plan - Natural Resources Study (note: some 

records may have been detected outside the DRP) 


5.5 MAMMALS 


There are 1 515 records of 70 species of mammals recorded from the DRP, including 332 

records of 17 bat species (Map 38). Historical records indicate that there has been a 

significant decline in terrestrial mammal species in the bioregion with 23 species known to 

have occurred in western New South Wales now extinct. The spatial distribution of mammal 

records per 1:100 000 mapsheets (Map 39) indicates a bias in the location of records, both 

within the DRP and in comparison with other areas of the state (NPWS 1999c). The majority 

of mammal records are from the northern portion of the DRP. 

Thirty-seven species of native mammals have been recorded in the northern floodplains, as 

well as nine introduced mammal species (Smith et al 1998). Fourteen species of mammals 

have been recorded from the Macquarie Marshes, including the threatened Chalinolobus 

picatus (little pied bat) (NPWS 1993) and Saccolaimus flaviventris (yellow-bellied sheathtail 

bat) (Wilson et al. 1993). Sixteen species of mammal have been recorded in the Narran Lake 

Nature Reserve; four macropods, the echidna (Tachyglossus aculeatus), two dasyurids, the 

common brushtail possum (Trichosurus vulpecula), seven bats and the water rat (Hydromys 

chrysogaster) (NPWS 2000a). Seventeen native mammal species were found in the broader 

Narran River floodplain study (Smith 1993). No threatened species of mammal have been 

recorded from Narran Lake Nature Reserve to date but the koala (Phascolarctos cinereus) 

occurs in the general area. 

In the Gwydir watercourse study, Spark (1998) recorded nine terrestrial mammal species and 

18 bat species. Terrestrial mammals include the narrow-nosed planigale (Planigale 

106


tenuirostris), common brushtail possum and sugar glider (Petaurus breviceps). The 

identification of several of the 18 bat species is questionable as they were only identified from 

echolocation calls and include several species not likely to occur in this area. No unusual bat 

species were caught in harp traps. The threatened stripe-faced dunnart (Sminthopsis 

macroura) has also been recorded in previous survey of the area (Spark 1998). 

The Culgoa and Birrie River floodplain survey in the early 1990s recorded 19 native and 

seven introduced mammal species (Dick & Andrew 1993). The terrestrial mammal fauna of 

this area was dominated by dasyurids, with the only native rodent being the water rat in 

aquatic habitats. The four dasyurid species included the threatened stripe-faced dunnart. Two 

species of macropod were present, and the regionally rare swamp wallaby (Wallabia bicolor) 

had been reported from nearby properties. There were also three species of arboreal mammal: 

koala, common brushtail possum and an unidentified Petaurus glider. All of these species are 

of regional significance in this area. Seven species of bats included Chalinolobus picatus 

(little pied bat) and several species which are of conservation concern in the western division. 


Eight extinct, two endangered and nine vulnerable species listed in the TSC Act have been 

recorded in the DRP (databases; Dickman & Read 1992; Dickman 1993). Recent records of 

threatened species are mostly confined to the northern tip of the bioregion (Table 5.5, Map 

40). 

Table 5.5 Mammal species of conservation concern recorded in the DRP. 

Common name Scientific name Legal status Number of Dataset 

records 

platypus Ornithorhynchus anatinus VDPLP 6 AM (5), WLA (1) 

spotted-tailed quoll Dasyurus maculatus V (subsp. maculatus 3 

VMBM), EDPLP 

WLA 

yellow-footed antechinus Antechinus flavipes VDPLP 15 AM (2), WLA (13) 

brush-tailed phascogale Phascogale tapoatafa V (subsp. tapoatafa 1 

NTMBM), PEDPLP 

CSIRO 

kultarr Antechinomys laniger E1, PEDPLP 8 AM (4), WLA (4) 

stripe-faced dunnart Sminthopsis macroura V 22 AM (10), WLA (9), CSIRO 

(1), Cul (2) 

western barred bandicoot Perameles bougainville E4 (subsp fasciata 1 WLA (last recorded in 1840) 

bilby Macrotis lagotis 

EXMBM) 

E4, VMBM 5 AM (3), WLA (2) (last 

koala Phascolarctos cinereus V (NTMBM), PEDPLP 167 

recorded in 1940) 

AM (1), WLA (164), Cul (1), 

MD (1) 

sugar glider Petaurus breviceps PEDPLP 9 AM (2), WLA (1), Boo, Gwy 

(6) 

squirrel glider Petaurus norfolcensis V (NTMBM) 1 WLA 

common ringtail possum Pseudocheirus peregrinus EDPLP 2 AM (1), WLA (1) 

common brushtail possum Trichosurus vulpecula VDPLP 119 AM (4), WLA (58), Bor (2), 

Cul (6), Nar (3), Tra (14), 

Gwy (32) 

burrowing bettong Bettongia lesueur E4 (subsp graii 1 WLA (last recorded in 1879) 

brush-tailed bettong Bettongia penicillata 

EXMBM) 

E4 (subsp penicillata 1 

EXMBM) 

WLA (last recorded in 1882) 

northern bettong Bettongia tropica E4, EMBM 1 WLA (last recorded in 1840) 

eastern hare-wallaby Lagorchestes leporides *E4 (EXMBM) 2 WLA (last recorded in 1863) 

swamp wallaby Wallabia bicolor PEDPLP 128 AM (2), WLA (106), Bor (2), 

Lum, Nar (2), Gwy (16) 

107


Common name Scientific name Legal status Number of Dataset 

records 

yellow-bellied sheathtail-bat Saccolaimus flaviventris V 28 AM (7), WLA (21) 

Gould's long-eared bat Nyctophilus gouldi PEDPLP 29 AM (9), WLA (12), Cul (3), 

Nar (1), Gwy (4) 

little pied bat Chalinolobus picatus V, NTDBM 14 AM (4), WLA (9), Cul (1) 

inland forest bat Vespadelus baverstocki V 7 AM (2), WLA (2), MD (3) 

white-footed rabbit-rat Conilurus albipes *E4 2 WLA (last recorded in 1846) 

silky mouse Pseudomys apodemoides E1, ExDPLP 1 WLA (historic record – last 

recorded in DRP near 

Gould's mouse Pseudomys gouldii *E4 1 

Walgett in 1800) 

WLA (last recorded in 1858) 

pale field-rat Rattus tunneyi XDPLP 2 WLA 

long-haired rat Rattus villosissimus V, VDPLP 3 WLA (historic record – last 

recorded in 1887 in the Tilpa 

District) 

Key 

V Vulnerable under schedule 2 TSC Act (1995) An asterix denotes those species which are also listed as nationally vulnerable 

under the EPBC Act. 

E1 Endangered under schedule 1 TSC Act (1995) 

E4 Extinct under Schedule 4 TSC Act (1995) 

NTDBM Near threatened as defined by Duncan et al 1999 

EXMBM Extinct as defined by Maxwell et al 1996 

EMBM Endangered as defined by Maxwell et al 1996 

VMBM Vulnerable as defined by Maxwell, et al 1996 

NTMBM Near threatened as defined by Maxwell et al 1996 

XDPLP Extinct in the Western Division of New South Wales as defined by Dickman et al 1993. 

ExDPLP Probably extinct in the Western Division of New South Wales as defined by Dickman et al 1993 

EDPLP Endangered in the Western Division of New South Wales as defined by Dickman et al 1993 

PEDPLP Possibly endangered in the Western Division of New South Wales as defined by Dickman et al 1993. 

VDPLP Vulnerable in the Western Division of New South Wales as defined by Dickman et al 1993 





Boo Boomi and Boomi West NRs Survey 



Nar Vertebrate Fauna Survey of Narran River Floodplain 


MD Murray Darling Water Management Action Plan - Natural Resources Study (note: some records may have been detected 

outside the DRP) 


The endangered yellow-footed rock-wallaby (Petrogale xanthopus) and vulnerable brushtailed 

rock-wallaby (Petrogale penicillata) listed under the TSC Act are also predicted to 

occur in the DRP but these predictions do not include the assessment of the presence of 

suitable habitat for these species. 

Grazing by stock, disturbance by feral mammals and land clearance have been identified as 

the major current threats to these species of conservation concern (Dickman et al. 1993). 


No threatened populations of mammals have been identified in the bioregion under the TSC 

Act. Populations of swamp wallaby, common brushtail possum, koala and Petaurus glider 

which were recorded in the Northern Floodplains and Culgoa Birrie surveys and are regarded 

as regionally significant (Smith et al. 1998), but are not listed under the TSC Act. 

108


5.5.4 Introduced and pest species 

Twelve feral mammal species have been recorded from the DRP in the databases (Table 5.6, 

Map 40). The number of records of each species has been included to indicate the severity of 

the problem posed by these species. 

Table 5.6 Feral mammals recorded from the DRP. 

Common name Scientific name Number of records Dataset 

cattle (feral) Bos taurus 105 WLA (90), Bor (15) 

dingo and dog (feral) Canis familiaris 5 WLA 

goat (feral) Capra hircus 121 WLA (88), Cul (20), Lum, MD (13) 

horse (feral) Equus caballus 3 WLA 

cat (feral) Felis catus 58 WLA (42), Lum, MD (6), Gwy (10) 

brown hare Lepus capensis 97 WLA (84), Bor (2), Cul (1), Lum, Nar (4), MD (2), 

Gwy (4) 

house mouse Mus musculus 393 AM (26), WLA (114), CSIRO (4), Mid(28), Bor (7), 

Cul (2), Nar (5), Tra (29), MD (9), Gwy (169) 

rabbit Oryctolagus cuniculus 159 WLA (136), Bor (4), Cul (1), MD (18) 

sheep (feral) Ovis aries 4 WLA (4) 

black rat Rattus rattus 4 AM (1), WLA (3) 

pig (feral) Sus scrofa 8,838 AM (1), WLA (8800), Cul (23), Lum, Nar (2), MD 

(7), Gwy (5) 

fox Vulpes vulpes 304 WLA (262), Mid(1), Bor (1), Cul (3), Lum, Nar (3), 

Tra (18), MD (9), Gwy (7) 

Key 





Mid Midkin NR Flora Fauna Survey 




Nar Vertebrate Fauna Survey of Narran River Floodplain 



MD Murray Darling Water Management Action Plan - Natural Resources Study (note: 

some records may have been detected outside the DRP) 

Feral pigs are widespread in the Namoi catchment with higher densities in the wetland or 

riverine environments on the plains, causing considerable damage to vegetation and crops and 

fouling water supplies. This problem is not confined to that part of the DRP and associated 

catchments. 

109



5.6.1 Summary 

Information about the distribution and abundance of the terrestrial vertebrate fauna across the 

bioregion is based on a few scattered systematic surveys and incidental records. As is 

illustrated on Maps 30, 32, 35 and 39, there are substantial gaps in the coverage of records 

and most of the mapsheets have been inadequately sampled. An exception is the number of 

bird records (5 001-26 785) for the Macquarie Marshes and the northern floodplains which 

are the most intensively sampled areas. Some mapsheets have no mammal, reptile or 

amphibian records and the areas with the lowest number of terrestrial vertebrate records are 

the upper and lower Bogan River. These areas should be targeted for fauna survey. 

Planning for future surveys within the DRP should focus on vegetation communities and 

landscapes that have not been intensively sampled. Habitat preference and expected 

distribution throughout the bioregion can be predicted from this data. Population viability 

assessments are also required for threatened vertebrate fauna in the DRP. In summary the 

status of the four terrestrial vertebrate taxa are shown in Table 5.7. In this table: listed species 

means those species which are listed under the TSC Act as endangered or vulnerable; species 

of concern are those species which are considered of concern as outlined in sections 5.2.2, 

5.3.2, 5.4.2 and 5.5.2; and predicted listed species are those species listed on the TSC Act 

which have been predicted to occur within the DRP using bioclimatic analysis. 

Taxon Total recorded 

species diversity 

Table 5.7 Summary of vertebrate taxa in the DRP 

Listed species 

(TSC Act) 

Species of 

concern 

Amphibians 25 0 5 0 

Reptiles 104 6 25 2 

Birds 319 40 25 7 

Mammals 58 19 8 10 

Predicted listed 

species (TSC Act) 

There are also six feral bird species and 12 feral mammal species known to occur within the 

DRP. 

On the basis of existing records, the Macquarie Marshes and part of the Menindee Lakes have 

most records of vulnerable species (Map 42). There is an apparent bias in the distribution of 

threatened species to the areas which have been more intensively surveyed suggesting that the 

gaps in the distribution of vulnerable species (Map 42) reflect a lack of survey effort rather 

than an absence of these species. 

110



Further work related to terrestrial vertebrate fauna in the DRP includes the following: 

collation of all datasets from previous surveys in the DRP; 

carefully located systematic and stratified fauna surveys across the DRP which fill the 

gaps in the existing survey database as indicated by mapsheets with few records (eg. 

along the Bogan River); 

targeted fauna surveys for cryptic, rare or other species unlikely to be adequately sampled 

by systematic methods; 

detailed description of habitats including structural and floristic information on fauna 

survey sites; 

review of the status of all terrestrial vertebrate fauna occurring in the DRP in order to 

identify species and populations at risk; 

preparation of nominations for identified species and populations for listing on the TSC 

Act where appropriate; 

preparation of profiles of priority species (threatened, declining and otherwise unusual 

species); 

population viability analysis and predictive habitat modelling for selected priority species; 

identification of areas of significance for threatened species, communities and 

populations; 

prioritisation of significant areas for conservation within the normal purchasing/property 

agreement arrangement; 

preparation of recovery plans for those threatened species and populations not already 

covered and implementation of recommendations and objectives; 

research priorities to be developed for exotic fauna species in the DRP, including a threat 

assessment, information about the abundance, impact on native species and communities 

and most effective control methods. 

111


6 OTHER FAUNA 

6.1 INVERTEBRATES 

Very little is known about invertebrate diversity within the bioregion. Not only is this 

knowledge of importance for assessing the biodiversity of the area, but invertebrates also 

perform an essential role in ecosystem function. They are of critical importance as food for 

many species (such as bats, insectivorous birds, water birds, waders, dasyurids and reptiles) 

and play an important role as decomposer organisms and in nutrient cycling. Some species 

can also be agricultural pests. Due to the lack of information about invertebrates, it is not 

possible to estimate rates of extinction or decline. As invertebrates play a critical role in the 

functioning of natural systems, improving the information base and therefore the conservation 

management for this group is critical to any strategy for conserving biodiversity (New 1984; 

NPWS 1992). A list of invertebrate taxa recorded from the DRP is shown in Appendix G. 

6.1.1 Aquatic invertebrates 

Rivers and streams exist as a patchwork of habitats, which can be classified into three broad 

habitat types for aquatic invertebrates. Macrohabitats are the large distinct reaches of the river 

system; mesohabitats are smaller habitats including the main channel, backwaters, billabongs, 

effluent creeks and floodplain channels; and microhabitats are the smallest habitat types 

which include snags (fallen timber), aquatic vegetation and different substrate types. 

In a survey of aquatic invertebrates in these three primary habitat types in the Darling River 

between Bourke and Wilcannia, Sheldon (1995) found insects were the dominant group, 

comprising 85% of taxa and 81% of individuals. Of these Dipterans (flies) and Coleopterons 

(beetles) were most abundant. Billabongs had a greater number of taxa and individuals than 

channel habitats and temporary billabongs had more individuals than permanent billabongs. 

Overall, river geomorphology was found to significantly influence aquatic invertebrate 

assemblages through the diversity of mesohabitats and microhabitats it supports. Flow 

regulation also modifies the assemblage composition by favouring the development of 

specific microhabitat and isolating mesohabitats (Sheldon 1995). 

In the Macquarie Marshes a baseline survey of aquatic invertebrates found 197 taxa of which 

85% were insects (65 Coleopteron taxa, 54 Dipterans, 24 Hemipterans). In general, cumbungi 

swamps, lagoons, slow moving streams and intermittent streams had the greatest number of 

taxa present (Bray 1994a). Cherax destructor (yabby), a common resident in the Marshes, 

survives dry periods by burrowing into the mud. 

112


6.1.2 Terrestrial invertebrates 

Dr Robyn Gunning (New South Wales Agriculture, Tamworth) undertakes regular 

invertebrate surveys for the Department of Agriculture and her survey area includes parts of 

the DRP. Results of these surveys need to be incorporated into an assessment of the 

biodiversity of the bioregion. A large collection of invertebrates from around New South 

Wales is housed at New South Wales Agriculture, Orange. 

6.2 FISH 


In surveys conducted by New South Wales Fisheries in 1996 and Llewellyn in 1983 of the 

rivers of the Darling region (including New South Wales tributaries and extending east of the 

DRP bioregion) 30 fish species were recorded or considered likely to occur (Table 6.1 and 

Table 6.2). Of these species, 15 were found in the Gwydir River basin, 16 in the Namoi, eight 

in the Castlereagh, 21 in the Macquarie and 13 in the Darling River (Harris & Gehrke 1997). 

Table 6.1 Fish species known or likely to occur in the Darling Region 

(Harris & Gehrke, 1997; Harris, 1995) 

Family Scientific Name Common Name Catchment 

Recorded 

Atherinidae Craterocephalus stercusmuscarum flyspecked hardyhead N, B-D 

Clupeidae Nematalosa erebi bony herring G, N, C, M, D, B-D 

Eleotridae Hypseleotris sp. gudgeon G, N, C, M, D 

Eleotridae Hypseleotris klunzingeri western carp gudgeon B-D 

Eleotridae Hypseleotris sp1 Lake's carp gudgeon B-D 

Eleotridae Hyseleotris sp2 Midgley's carp gudgeon B-D 

Eleotridae Mogurnda mogurnda northern purple-spotted gudgeon B-D 

Galaxiidae Galaxias olidus mountain galaxis G, N, M, B-D 

Melanotaeniidae Melanotaenia fluviatilis crimson-spotted rainbowfish G, N, M, D, B-D 

Percichthyidae Macquaria ambigua golden perch G, N, M, D, B-D 

Retropinnidae Retropinna semoni Australian smelt G, N, C, M, D, B-D 

Terapontidae Leiopotherapon unicolor spangled perch G, N, C, M, D, B-D 

Ambassidae Ambassis castelnaui olive perchlet B-D 

Atherinidae Craterocephalus amniculus Darling River hardyhead B-D 

Galaxiidae Galaxias rostratus Murray jollytail Predicted 

Plotosidae Neosilurus hyrtlii Hyrtl's tandan Predicted 

Eleotridae Philypnodon sp. dwarf flathead gudgeon B-D 

Key 

G = Gwydir River Catchment M = Macquarie River Catchment 

N = Namoi River Catchment D = Darling River Catchment 

C = Castlereagh River Catchment B-D = Barwon Darling River 

Twenty-three fish species are known to occur in the Barwon-Darling River system (Table 6.1 

and Table 6.2). This list does not include some species found only in the tributaries and five 

113


of the recorded species are introduced (Thoms et al. 1995). Most of the native species are 

carnivorous, eating crustaceans, insects and other fish. Nematalosa erebi (bony herring) is 

herbivorous and some other species are omnivores. Two distinct food chains support fish 

production in the Darling River: 

Nematalosa erebi feed on the algal/bacterial/fungal biofilms on riverbanks, snags, rocks 

and the algae attached to aquatic plants. Nematalosa erebi are then a food source for the 

predator species such as Macquaria ambigua (golden perch) and Maccullochella peelii 

(Murray cod); and 

plant litter washed into the river is consumed by midge larvae and shrimps that are in turn 

preyed upon by small and medium-sized fish. 

Many terrestrial vertebrates rely on these species as they form part of the total food web of 

wetland habitats. 

Fifteen species of fish have been recorded in the Macquarie Marshes, two of which are 

introduced. The native species include Nematalosa erebi, Macquaria ambigua, Melanotaenia 

fluviatilis (rainbow fish), Retropinna semoni (Australian smelt) and Hypseleotris klunzingeri 

(western carp-gudgeon). Introduced species are Cyprinus carpio (European carp) and 

Gambusia holbrooki (gambusia). Diversity and abundance of native fish species is low and 

appears to be in decline, with species like Tandanus tandanus (catfish) once being common 

but now rarely seen (Harris & Gehrke 1997). The fish diversity and relative abundance in the 

ephemeral wetlands of the Narran Lakes differs from that in the Macquarie Marshes. Five 

species were recorded by surveys of Clear Lake, with a high abundance of Macquaria 

ambigua being recorded (NPWS 2000a). 

Seven fish species were predicted to occur but were not recorded in surveys of the Darling 

catchment (Harris & Gehrke 1997). One of these, Hyrtl’s tandan (Neosilurus hyrtlii), 

probably only occurs in the Paroo system, which is not part of the DRP, and another, the 

dwarf flathead gudgeon (Philypnodon sp 1), is only known from the Bathurst area, also 

outside the bioregion. The other unrecorded species were Ambassis agassizii (olive perchlet), 

Craterocephalus amniculus (Darling River hardyhead), Mogurnda adspersa (purple-spotted 

gudgeon), Galaxias rostratus (Murray jollytail) and Maccullochella macquariensis (trout 

cod). 


Three fish species known from the Darling region have been listed under Schedules 3 and 5 

of the Fisheries Management Act (FMA) 1994, and two of these species are also listed on the 

EPBC Act (Table 6.2). The western populations of two species within the DRP are listed as 

endangered populations under Schedule 4 of the FMA 1994. Reasons for listing of species 

under this Act include habitat changes due to agricultural practices, spawning failures due to 

cold water releases from dams, predation by, and competition with, introduced species such 

as Perca fluviatilis and Gambusia holbrooki, and construction of barriers to migration and 

recolonisation (FSC, 2001e). Five species are also considered to be of concern in New South 

Wales by Fletcher and McVea (2001). 

114


Table 6.2 Fish species of conservation concern within the DRP 

(Harris & Gehrke 1997; Harris 1995) 

Family Scientific Name Common Name Catchment 

Status 

Atherinidae Craterocephalus fluviatilis Murray hardyhead 

Recorded 

N, M E FMAct, VEPBC 

Percichthyidae Maccullochella macquariensis trout cod Predicted *E FMAct 

Terapontidae Bidyanus bidyanus silver perch G, N, M, D, V FMAct, IUCNV 

B-D 

Ambassidae Ambassis agassizii olive perchlet M CC1 

Eleotridae Philypnodon grandiceps flathead gudgeon M CC1 

Galaxiidae Gadopsis marmoratus river blackfish G, N, C, M CC2 

Percichthyidae Maccullochella peelii Murray cod G, N, M, D, CC3 

B-D 

Plotosidae Tandanas tandanas freshwater catfish G, N, M, B-D CC4 

Key 

IUCNV = Classified as vulnerable under IUCN Red List Classifications (Fletcher and McVea 2001) 

VEPBC = Listed as vulnerable under the Environment Protection and Biodiversity Conservation Act, 1999 

E FMAct = Listed as endangered under Schedule 3 of the Fisheries Management Act, 1994 an asterix denotes that the 

species is also listed as endangered under the Environment Protection and Biodiversity Conservation Act, 1999 

V FMAct = Listed as vulnerable under Schedule 5 of the Fisheries Management Act, 1994 

CC1 = of conservation concern due to reduced distribution and abundance inland (Fletcher and McVea 2001) 

CC2 = of conservation concern due to susceptibility to increased sediment load (Fletcher and McVea 2001) 

CC3 = of conservation concern due to reduced and fragmented distribution (Fletcher and McVea 2001) 

CC4 = of conservation concern due to scarcity in many inland habitats (Fletcher and McVea 2001) 

G = Gwydir River Catchment 

N = Namoi River Catchment 

C = Castlereagh River Catchment 

M = Macquarie River Catchment 

D = Darling River Catchment 

B-D = Barwon-Darling River 

The distribution and population size of many native fish species within the Murray-Darling 

system have contracted markedly as a result of changes in the rivers (Morton et al. 1995). 

Threats in this river system include river diversion, over-fishing, water quality (salinity, 

eutrophication) and the impact of introduced species, particularly Cyprinus carpio, Perca 

fluviatilis (redfin perch) and Gambusia holbrooki. The significant change in the natural 

pattern of high and low flows has also had an impact on the two fundamental food webs in 

the system. Biofilms on riverbanks are now constrained to a single narrow strip, rather than a 

broad band, because river heights are tightly controlled. Significant quantities of plant litter 

now lie unused on the floodplain and in anabranches for much longer periods. River flow 

diversion also creates another, little acknowledged, problem with many small fish being 

sucked from the river into irrigation systems and lost (Harris 1995). 

The construction of weirs and dams has had a significant effect on the life cycle of many 

species. Some species spawn in one part of the river system, use a different part as a nursery 

area and then disperse into a third area for growth into adults. Macquaria ambigua spawn 

during floods in lowland reaches of rivers, the young move into the floodplain or river-margin 

nurseries and finally travel upstream in river channels. Maccullochella peelii (Murray cod) 

make upstream spawning migrations using anabranches and flood-runners and then make a 

precise homing migration to their original territory. These fish therefore require the survival 

of each of these habitats and the maintenance of free passage between them. The scale of 

115


movements varies between species: the migratory species Macquaria ambigua and Bidyanus 

bidyanus (silver perch) can travel the length of the Murray-Darling system, while some small 

species such as hardyheads and gudgeons require only a few kilometres of river to complete 

their life cycle. Obstruction of migratory movements can lead to the extinction of populations 

and species and this problem requires large scale change to river management to be effective 

(Harris 1995). The NSW Rivers survey found that there were proportionally more native 

species than introduced species in unregulated rivers and 13 native fish species showed a 

negative response to river regulation (Harris & Gehrke 1997). 

The severity of the decline in fish diversity and abundance in this system has not been fully 

documented, although some significant falls have been documented in catches of 

Maccullochella peelii, Tandanus tandanus and the near disappearance of Bidyanus bidyanus 

from the Darling. Overall, in New South Wales rivers 62% of native fish have undergone 

reductions in range and/or abundance, suggesting that they are more vulnerable to disturbance 

than was previously thought. Maccullochella peelii has undergone a significant reduction in 

range and abundance and is now relatively uncommon in many areas (Harris & Gehrke 

1997). 


Two significant populations of fish have been identified as occurring in the DRP. The 

population of Mogurnda adspersa in western New South Wales has been listed as an 

endangered population under the FMA 1994. This species was once widespread throughout 

the Murray-Darling system and in coastal streams. The eastern population now occurs in 

coastal drainages north of the Clarence River, but its distribution throughout the Murray- 

Darling system is very limited and has significantly declined in recent years. There has been 

only a single record of this species in the Murray-Darling since 1983. These eastern and 

western populations may be genetically distinct. The causes of the decline of the western 

populations of this species are thought to include predation by Gambusia holbrooki and Perca 

fluviatilis, habitat loss and rapid fluctuations in water levels as a result of water regulation, 

which affects reproduction and recruitment (FSC 2001e). 

The Fisheries Scientific Committee has also listed the western population of Ambassis 

agassizii as an endangered population under the FMA 1994. This population has declined 

seriously in recent decades and is now possibly absent from the majority of Murray-Darling 

waterways (FSC 2001e). 

Regionally endemic species include Gadopsis bispinosus (two-spined blackfish), Galaxias 

rostratus, Melanotaenia fluviatilis (Australian rainbowfish), Maccullochella peelii and 

Bidyanus bidyanus (Morton et al. 1995). 

6.2.4 Introduced fish species 

Of all rivers within NSW, the Darling River catchment contains the greatest diversity of 

introduced species, with six being present. These species are Cyprinus carpio, Carassius 

auratus (goldfish), Gambusia holbrooki, Perca fluviatilis, Oncorhynchus mykiss (rainbow 

trout) and Salmo trutta (brown trout). The two trout species and Perca fluviatilis are probably 

not present in the DRP bioregion, preferring the higher reaches of the Darling tributaries. 

Introduced species represented 25.1% of the total fish catch in the Darling system (Harris and 

Gehrke 1997). 

116


Table 6.3 Introduced fish species recorded within the Barwon-Darling Region 

(Harris & Gehrke 1997; Harris 1995) 

Family Scientific Name Common Name Catchment Recorded 

Atherinidae Carassius auratus goldfish G, N, C, M, D, B-D 

Cyprinidae Cyprinus carpio European carp G, N, C, M, D, B-D 

Percidae Perca fluviatilis redfin perch G, M, D, B-D 

Poeciliidae Gambusia holbrooki gambusia G, N, C, M, D, B-D 

Salmonidae Oncorhynchus mykiss rainbow trout M 

Salmonidae Salmo trutta brown trout M 

Salmonidae Salvelinus fontinalis brook trout M 

Cyprinidae Tinca tinca tench B-D 

Key 

G = Gwydir River Catchment M = Macquarie River Catchment 

N = Namoi River Catchment D = Darling River Catchment 

C = Castlereagh River Catchment B-D = Barwon Darling River 

Gambusia 

Gambusia holbrooki have been implicated in the decline in abundance or range of 35 fish 

species world-wide, and there is circumstantial evidence that several Australian native fish 

species have been adversely affected by the spread of this species. Predation by Gambusia has 

been listed as a key threatening process under the TSC Act, primarily because of predation of 

tadpoles and eggs of some frog species in eastern New South Wales. The impact of Gambusia 

on native fish species occurs through a variety of mechanisms including direct competition 

for resources, interference, competition and predation. The species is an adaptable generalist 

predator, which feeds on a wide range of both terrestrial and aquatic organisms (Harris & 

Gehrke 1997). 

European carp 

Numbers of European carp increased greatly in the Macquarie and Bogan River system in the 

mid-1970s, assisted by the floods of 1974 and 1975 (Macquarie 2100 plan 1999). It has been 

estimated that European carp make up 50% of the total biomass in the river. European carp 

damage the river habitat by increasing water turbidity, decreasing water plant diversity and 

abundance, increasing water nutrients, increasing algal concentrations by preying on 

zooplankton, reducing native fish numbers, decreasing small insect numbers and eroding 

stream banks (King 1995). European carp are the dominant fish species of the Murray- 

Darling system. Their abundance is demonstrated at one site in the lower reaches of the 

Bogan River, where there was an average of one European carp per square metre of river 

surface area. Flow regulation has allowed the development of suitable habitat for European 

carp while promoting the destruction of suitable habitat for the less sedentary native species 

(Harris & Gehrke 1997). 

117



6.3.1 Summary 

The knowledge of invertebrate biodiversity within the DRP is extremely limited but it is 

essential for a variety of reasons. In addition to their own contribution to the biodiversity of 

the ecosystem, invertebrate species are fundamental to the survival of many vertebrate species 

as a food resource, can be used as indicator species for land health and are an essential 

component of ecosystem function. It is also important to recognise that the impact of land 

management on invertebrate populations is not necessarily restricted to the DRP for example, 

the bogong moths which breed in the floodplains of the DRP are an essential food source for 

the threatened mountain pygmy possum (Burramys parvus) when they migrate to the alpine 

regions prior to winter and also have important cultural significance to Aboriginal people in 

the alpine regions. 

Although more information is available about the diversity of aquatic invertebrates than 

terrestrial invertebrates in the DRP, this information is still insufficient to classify aquatic 

habitats such as wetlands as critical habitats for waterbirds. Like the bogong moth, many of 

the aquatic invertebrates can have an impact on vertebrate biodiversity beyond the DRP 

bioregion. 

The health of fish populations can also affect the conservation of terrestrial vertebrates. 

Research into the distribution, abundance and status of fish in New South Wales is primarily 

the responsibility of NSW Fisheries, but as the DRP is a fluvial environment the health of the 

rivers and the fish fauna is an essential component of the overall conservation of this 

bioregion. 


Further work related to the full range of fauna in the DRP includes the following: 

continued survey of aquatic invertebrates across the variety of wetlands in order to 

determine the significance of each wetland for the maintenance of waterbird populations; 

collation of existing information about terrestrial invertebrates and determination of 

priorities for further work, especially in relation to terrestrial vertebrate conservation 

strategies; 

assessment of terrestrial invertebrates critical for the survival of threatened vertebrate 

species; 

assessment of information relating to the fish fauna and determination of priorities for 

further work, especially in relation to terrestrial vertebrate conservation strategies; and 

further research into the relationship between invertebrate diversity and abundance and 

flood events in the various river catchments within the DRP. 

118


7 ECOLOGICAL AND 

THREATENING 

PROCESSES 

7.1 ECOLOGICAL PROCESSES 

The State Biodiversity Strategy requires the maintenance of ecological processes such as 

nutrient cycling, soil formation and hydrological processes. 

7.1.1 Nutrient cycling and soil formation 

Nutrients are essential for the growth of plants and include potassium, nitrogen, magnesium, 

calcium, iron and phosphorus. Nutrients are cycled through an ecosystem by various 

mechanisms including animals eating plants and depositing faeces, rain and groundwater 

flows washing nutrients from one place to another, wind and water erosion of soils 

transporting nutrients, soil fauna such as microbes and invertebrates, and uptake of nutrients 

by plants followed by subsequent decomposition and return of nutrients to the soil. These 

processes ensure continuous cycling of nutrients through the system. Fluctuation or 

disruption of nutrient cycles may be caused by factors such as removal of vegetation, bushfire 

and drought. (APASE 2001) 

Soil formation processes involve the continuous breaking down of rock material through 

physical, chemical and biological mechanisms. This is affected by the parent rock type, 

living organisms (e.g. fungi, burrowing insects, animals and man), climate, topography and 

time. Soil formation processes may take a very long time and the parent rock type mostly 

determines the soil characteristics. Soil formation processes can be disrupted by erosion, 

clearing of vegetation and agriculture. Deep rooted trees and shrubs act as nutrient “pumps” 

for weathering substrates from between ten and 20m below the surface (Nix, H., ANU, 

pers.com 2001). 

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7.1.2 Hydrological regimes 

The Mehi, Macintyre, Namoi and Macquarie Rivers, and Moomin, Carole, Gunningbar, and 

Duck Creeks are regulated rivers and parts of the Gwydir and Darling Rivers are also 

regulated. Regulated rivers are those that “have large dams supplying irrigation water (and 

some town and industrial water) for substantial distances downstream. Downstream tributary 

inflows are typically supplemented during the irrigation season, resulting in fairly stable and 

unnaturally high water levels. River flow is substantially reduced during the non- or lowirrigation 

seasons. At any time of year in periods which would normally have high or very 

high flow, flows may be substantially reduced by the trapping of water in a large dam” (EPA 

2001). River Management Committees are considering and implementing environmental 

flows to improve this flow reduction. 

The Castlereagh River and all other streams within the Castlereagh catchment in the DRP, the 

Bogan River, Whalan Creek, Thalaba Creek, Marra Creek, and Talyawalka Creek are 

classified as unregulated rivers. Unregulated or uncontrolled streams are those streams where 

“flow patterns are largely natural. Flows can occur in these streams from local runoff. They 

are typically ephemeral (flowing only during floods and freshes). Frequently, they open into 

or flow through wetlands and billabongs” (EPA 2001). 

The Barwon, Culgoa, Birrie, Bokhara, Narran, and Boomi Rivers, the Gwydir Watercourse 

and Pian Creek, and the parts of the lower Gwydir, lower Macquarie and upper Darling 

Rivers are classified as controlled rivers with reduced flow. Controlled rivers with reduced 

flows include: 

1. “River reaches downstream of the major regulated sections where the water is extracted or 

diverted. Flow is generally reduced throughout the year. Water is delivered from the main 

stream for stock, domestic, some irrigation, and town water supplies several times a year. 

2. Sections of rivers immediately below town water supply dams, where water is diverted 

directly from the dam. Flows can be substantially reduced throughout the year, though 

special environmental releases may be possible” (EPA 2001). 

The majority of the bioregion is categorised as either over-extracted in relation to 

groundwater or with an extraction level of greater than 100% of the sustainable yield for 

groundwater systems. Two smaller areas in the east and south of the bioregion have a total 

extraction level of between 70 and 100%. The remainder of the bioregion has an abstraction 

of greater than 30% sustainable yield. This area is mostly the Darling riverine corridor of the 

bioregion (EPA 2000). 

EPA (2000) lists good-quality (or low-salinity) ground water as that found in aquifers 

including those in the Darling River corridor. The yields from aquifers within the Darling 

River corridor are generally low and more suitable for domestic and stock use or small-scale 

irrigation (for example, for orchards). Aquifers that have good-quality water and high yields 

within the DRP include the river corridors of the Namoi and Upper Gwydir. These aquifers 

are used mainly for irrigated agriculture and stock watering, but potable water extraction is 

also an important use. Ground water from the aquifers bounded by the Lachlan, Darling and 

Bogan rivers and the south-western corner of the State is generally of poor quality or 

extremely low-yielding (EPA 2000). 

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Contamination of groundwater by pesticides has been recorded in the lower Namoi Valley but 

monitoring of pesticides in groundwater is limited and further sampling and monitoring is 

required to assess accurately levels of contamination (EPA 2000). 

7.2 LISTED AND POTENTIAL THREATENING PROCESSES 

Key threatening processes listed under the TSC Act are those that threaten, or may have the 

capability of threatening, the survival or evolutionary development of species, populations or 

ecological communities. Eight of the key threatening processes (KTPs) listed under Schedule 

3 of the TSC Act affect the ecology of the DRP bioregion. A preliminary determinations has 

also been made by the NSW Scientific Committee to support the listing of the ‘competition 

with feral honeybees Apis mellifera’ as a KTP (NPWS 2001A). 

The Fisheries Management Act 1994 (NSW) (FMA 1994) also lists key threatening processes. 

The NSW Fisheries Scientific Committee has made final recommendations to list 

‘degradation of native riparian vegetation along New South Wales watercourses’, ‘removal of 

large woody debris’, and ‘introduction of fish to fresh waters within a river catchment outside 

their natural range’ as key threatening processes under the FMA 1994. The Fisheries 

Scientific Committee has also made a recommendation to list ‘installation and operation of 

instream structures that modify flow’ as a key threatening process under the FMA 1994. 

The EPBC Act lists nine KTPs of relevance to the DRP. Some of these identify the same 

process as listed on the TSC Act but may define them differently (Environment Australia 

2001c). 

7.2.1 Listed Threatening Processes 

High frequency fire 

‘High frequency fire resulting in the disruption of life cycle processes in plants and animals 

and loss of vegetation structure and composition’ has been listed as a key threatening process 

under the TSC Act. The NSW Scientific Committee defines high frequency fire as ‘two or 

more successive fires close enough together in time to interfere with or limit the ability of 

plants or animals to recruit new individuals into a population, or for plants to build up a 

seedbank sufficient in size to maintain the population through the next fire’ (NPWS 2001A). 

The rate of decrease of woody vegetation across New South Wales between 1990 and 1995 

due to bushfires has been estimated to be 33 520 ha / year. 66% of this area of woody 

vegetation is expected to regenerate quickly (Bureau of Rural Sciences 1999). 

Threatened species known from the DRP likely to be affected by high frequency fires include 

Swainsona plagiotropis, glossy black-cockatoo, malleefowl, rufous bettong, black-striped 

wallaby, spotted-tailed quoll and squirrel glider (NPWS 2001a). Species not yet listed but 

occurring in the DRP that could become threatened by high frequency fires include feathertail 

glider (Acrobates pygmaeus), common ringtail possum, yellow-footed antechinus (Antechinus 

flavipes) and sugar glider (Petaurus breviceps) (NPWS 2001a). 

Anthropogenic climate change 

Anthropogenic climate change is listed as a key threatening process under the TSC Act and 

the EPBC Act. Natural climate change has been a major ecological driving force throughout 

geological history but there is evidence to suggest that modification of the environment by 

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humans may cause future climate change. Many landscapes in New South Wales, including 

the DRP, are highly modified and the ability of organisms to survive climate change through 

dispersal will be limited (Brasher & Pittock 1998). The EBPC Act also specifically lists the 

impact of greenhouse emissions. 

Species that would be at risk from anthropogenic climate change include those that have long 

generations, poor mobility, narrow ranges, specific host relationships, isolated and specialised 

species, and those with large home ranges (Hughes & Westoby 1994). Threatened species 

recorded within the DRP that would be at risk from anthropogenic climate change in New 

South Wales include malleefowl, plains-wanderer, red-tailed black-cockatoo and regent 

parrot (NPWS 2001a). 

Predation by the feral cat (Felis catus) 

Predation by the feral cat is listed as a key threatening process under the TSC Act and the 

EPBC Act. Many species are threatened by predation from cats including species already 

listed as threatened and those at risk of becoming threatened. Small mammals such as the 

sandy inland mouse and ground-nesting birds are particularly at risk (NPWS 2001a). The 

malleefowl (Leipoa ocellata) is one species listed by the Commonwealth Threat Abatement 

Plan for Predation by Feral Cats which is perceived to be further threatened by this process 

(Environment Australia 1999c). 

Predation by the European red fox (Vulpes vulpes) 

Predation by the European red fox is listed as a key threatening process under the TSC Act 

and the EPBC Act. Species threatened by predation from foxes include species already listed 

as threatened and at risk of becoming threatened. This includes some larger arboreal species 

such as the common brushtail possum that are in significant decline in the DRP bioregion. 

The malleefowl (Leipoa ocellata) is one species identified under both the Commonwealth 

Threat Abatement Plan for Predation by the European Red Fox (Environment Australia 

1999d) and the NSW Draft Threat Abatement Plan (NPWS 2001c). Other species identified 

under the NSW Draft Threat Abatement Plan as high priority species for fox control recorded 

within the DRP are the bush stone-curlew (Burhinus grallarius), chestnut quail thrush 

(Cinclosoma castanotus), flock bronzewing (Phaps histrionica), Australian bustard (Ardeotis 

australis), Australasian bittern (Botaurus poiciloptilus), brolga (Grus rubicunda), woma 

(Aspidites ramsayi), and the western blue-tongued lizard (Tiliqua occipitalis). The medium 

priority species, spotted tail quoll (Dasyurus maculatus) and brush-tailed phascogale 

(Phascogale tapoatafa). Foxes have also been identified as being a vector for bitou bush 

(Chrysanthemoides monilifera rotundata) (NPWS 2001a). Priority areas for fox control 

within the DRP include the Macquarie Marshes and Narran Lakes (NPWS 2001c) 

Predation by gambusia (Gambusia holbrooki) 

Predation by the gambusia is listed as a key threatening process under the TSC Act. Gambusia 

holbrooki preys upon eggs and tadpoles of several frog species, particularly the bell frogs 

(Littoria spp.) (NPWS 2001a). Due to the largely aquatic nature of the bioregion, and records 

of Gambusia holbrooki within the waterways, this process is likely to threaten species of the 

DRP. 

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Competition and land degradation by Feral Goats (Capra hircus) 

Competition and land degradation by the feral goats is listed as a key threatening process 

under the EPBC Act. A variety of habitats, particularly the semi-arid habitats, in the DRP 

have been successfully occupied by feral goats. They compete with native fauna for food, 

water and shelter and threaten the survival of some native plant species. The malleefowl 

(Leipoa ocellata) is one species listed under the Commonwealth Threat Abatement Plan for 

Competition and Land Degradation by Feral Goats known to be further threatened by this 

process. Plant species within the DRP seriously affected by this process include Alectryon 

oleifolius, Santalum acuminatum, Santalum spicatum and Capparis mitchelli (Environment 

Australia 1999e). 

Competition and land degradation by feral rabbits (Oryctolagus cuniculus) 

Competition and land degradation by feral rabbits is listed as a key threatening process under 

the EPBC Act. Rabbits inhibit regeneration of native vegetation (Crisp 1978; Lange & 

Graham 1983; Cooke 1987), compete with native fauna for food (Dawson & Ellis 1979) and 

shelter (Martin & Sobey 1983; Priddel et al. 1995), support populations of introduced canids 

and felids (Catling 1988), and cause soil erosion (McManus 1979; Norman 1988). The 

malleefowl (Leipoa ocellata) is one species listed under the Commonwealth Threat 

Abatement Plan for Competition and Land Degradation by Feral Rabbits which is perceived 

to be further threatened by this process with rabbits attracting predators to this species 

(Environment Australia 1999f). 

Predation, habitat degradation, competition and disease transmission by feral pigs (Sus 

scrofa) 

Predation habitat degradation, competition and disease transmission by feral pigs is listed as a 

key threatening process under the EPBC Act. Feral pigs prey on bird chicks, reptiles, reptile 

and bird eggs, frogs, soil organisms, invertebrates, and plants. They cause habitat changes by 

destroying plants, reducing regeneration of native plants, changing floristic composition, 

altering soil structure, enhancing invasion and spread of weed species, increasing access for 

other predators, reducing the amount and quality of water available, spreading exotic 

earthworms and creating suitable habitat for disease vectors such as the root-rot fungus 

Phytophthora cinnamomi (Environment Australia 2001c). 

Invasion of native communities by Chrysanthemoides monilifera subsp. rotundata (bitou 

bush) 

Invasion of native communities by Chrysanthemoides monilifera subsp. rotundata (bitou 

bush) is listed as a key threatening process under the TSC Act. This key threatening process 

has a deleterious impact on several threatened species, populations and endangered ecological 

communities in coastal NSW (NPWS 2001a). The threat posed to native communities by this 

weed is substantially less in the DRP but there is an infestation of Chrysanthemoides 

monilifera at Menindee and this weed species is recorded for the DRP in the NPWS Wildlife 

Atlas (Appendix D). 

Clearing of native vegetation and land clearance 

Clearing of native vegetation is listed as a key threatening process under the TSC Act and land 

clearance is listed as a key threatening process under the EPBC Act. Clearing of vegetation 

results in habitat loss and fragmentation and a decline in the quality of habitat for a number of 

species across a wide range of ecosystems (EPA 2000). The NSW Scientific Committee 

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(NPWS 2001a) defines clearing as: 

loss or modification of native vegetation for cropping, establishment of plantations or for 

improved pasture; 

loss or modification of native vegetation for urban development; 

loss or modification of native vegetation for development of industry and infrastructure 

(eg quarries, mines, factory sites, dams, roads, railways, powerlines); and 

clearing of understorey (and/ or replacement by exotic species) for example, along 

roadsides. 

EPA (2000) states that ‘vegetation clearance is the single greatest threat to terrestrial 

biological diversity in New South Wales and is still causing significant biodiversity losses in 

the State’. NPWS (2001a) outline the impacts of clearing on biodiversity as: 

destruction of habitat resulting in loss of local populations of individual species; 

expansion of dryland salinity; 

riparian zone degradation; 

increased greenhouse gas emissions; 

increased habitat for exotic species; 

loss of leaf litter layer; and 

loss or disruption of functioning ecological interactions. 

Many threatened species of flora and fauna and ecological communities occurring in the DRP 

are threatened by clearing. These include the seven mammals, three reptiles, 24 bird species 

and five plant species (NPWS 2001a). 

Dieback caused by Phytophthora cinnamomi (cinnamon fungus) 

Dieback caused by Phytophthora cinnamomi is listed as a key threatening process under the 

EPBC Act. Dieback in plants caused by Phytophthora cinnamomi is mainly a problem in 

other bioregions and states or territories and it has not yet been recorded in western New 

South Wales. This lack of data on the fungus is justified by climatic variables not being 

suitable in the area because it is not humid enough and that the cost of undertaking extensive 

mapping of the fungus nationally is extreme (Environment Australia 1999a, 1999b). Several 

species present in the DRP have the potential to be adversely affected. 

Psittacine circoviral (beak and feather) disease 

Psittacine circoviral disease is listed as a key threatening process under the EPBC Act. 

Psittacine Circoviral disease affects parrots and their allies (Psittacines) and is usually fatal. 

The virus is long-lived and has the potential to persist in nest hollows causing their long-term 

contamination. The virus is widespread in wild Psittacines, including in galahs (Cacatua 

roseicapilla) and sulphur-crested cockatoos (C. galerita). Potentially catastrophic losses 

could occur if an infestation was to occur in bird populations that had been dramatically 

reduced (Environment Australia 2001c). It has been specifically listed as a KTP for nationally 

endangered parrots, none of which have been recorded within the DRP but species such as the 

superb parrot could also be at risk. No threat abatement plan has been prepared for this KTP. 

Removal of large woody debris 

Removal of large woody debris has been listed as key threatening process under the FMA 

1994. Large woody debris includes “large masses of trees or shrubs that have fallen or that 

have been washed into rivers and streams” (FSC 2001a). Large woody debris (FSC 2001a): 

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provide habitat for benthic plants; 

lead to organic enrichment by capturing detritus and contributing to secondary production 

by degradation of the debris itself; 

provide refuges from predators and interactions between competitors for fish and 

invertebrates; 

provide velocity refuges that minimise energy costs of swimming; 

provide spawning sites essential for successful reproduction; 

provide home range markers for territorial and migratory fish species; 

provide refuge and spawning habitats in the riparian zone during overbank flooding; 

assist in erosion prevention by stabilising sediments of stream banks and riparian zones; 

and 

assist in the scouring of deep holes adjacent to woody debris which acts as temperature 

and drought refuges. 

Threatened fish species that occur within the DRP and which are affected by this process 

include trout cod (Maccullochella macquariensis) and silver perch (Bidyanus bidyanus) (FSC 

2001a). 

Degradation of native riparian vegetation along New South Wales water courses 

‘Degradation of native riparian vegetation along New South Wales water courses’ has been 

listed as a key threatening process under the FMA 1994. The Fisheries Scientific Committee 

defines riparian vegetation as “any vegetation on land which adjoins, directly influences, or is 

influenced by a body of water” (FSC 2001b). Degradation of native riparian vegetation 

includes invasion of riparian vegetation by non-native species. Negative effects of 

degradation of native riparian vegetation include increased amounts of sediment and nutrients 

via runoff and increased light penetration to the waterbody leading to increased algal growth 

and smothering of benthic communities, reduced inputs of organic carbon which are a major 

energy source in most stream ecosystems, reduced inputs of large woody debris entering the 

system leading to a reduction in spawning and habitat sites of several fish and aquatic 

invertebrates, destabilisation of river banks, and reduced overhanging riparian vegetation 

leading to decreased shelter and shade for fish. Threatened fish species recorded within the 

DRP affected by this process include trout cod (Maccullochella macquariensis), Murray 

hardyhead (Craterocephalus fluviatilis), and silver perch (Bidyanus bidyanus) and the 

endangered populations of purple-spotted gudgeon (Mogurnda adspersa), and olive perchlet 

(Ambassis agassizii) (FSC 2001b). 

Introduction of fish to fresh waters within a river catchment outside their natural range 

‘Introduction of fish to fresh waters within a river catchment outside their natural range’ is 

listed as a key threatening process under the FMA, 1994. Introduced fish recorded in the DRP 

(brown trout (Salmo trutta), rainbow trout (Onchorynchus mykiss), European carp (Cyprinus 

carpio), goldfish (Carassius auratus), gambusia (Gambusia holbrooki) and redfin perch 

(Perca fluviatilis)) all have self-sustaining populations within the waterways of New South 

Wales (FSC 2001c). Introduced fish affect populations of native fauna and flora by direct 

predation, competition for food, competition for spawning localities, competition for habitat, 

habitat degradation through uprooting vegetation and disturbance of sediments and promotion 

of the spread of diseases in native species. Threatened fish species recorded within the DRP 

affected by this process include Murray hardyhead (Craterocephalus fluviatilis), trout cod 

(Maccullochella macquariensis), and silver perch (Bidyanus bidyanus) the endangered 

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populations of olive perchlet (Ambassis agassizii), and purple-spotted gudgeon (Mogurnda 

adspersa) (FSC 2001c). 

7.2.2 Potential Threatening Processes 

Competition from honeybees (Apis mellifera) (preliminary determination) 

The NSW Scientific Committee have made a preliminary determination to list competition 

from honeybees as a key threatening process under the TSC Act. Breeding colonies of 

honeybees compete with native hollow-dependant fauna for tree hollows. At least 20% of 

bird species are hollow dependant (Saunders et al. 1982) and all native arboreal marsupials 

depend on tree hollows except the koala (Lindenmayer et al. 1991). Threatened species likely 

to be affected by competition from feral honeybees include the squirrel glider, Major 

Mitchell’s cockatoo, glossy black-cockatoo and superb parrot (NPWS 2001a). 

Honeybees, both feral and managed, often remove up to 80% of the floral resources produced 

by plants, and this may result in the displacement of native fauna such as honeyeaters and 

native bees which rely on these resources (Paton 1993, 1996, 2000; Sugden & Pyke 1991; 

Sugden et al. 1996). Apiary has an unmeasured impact on biodiversity and some studies have 

shown that where nectar and pollen resources are limited Apis mellifera may reduce the 

degree of seed set in some plant species (Gibbs & Muirhead 1998; Paton 1996; Pyke & 

Blazer 1985). 

Alteration to the natural flow regimes of rivers and streams and their floodplains and 

wetlands (preliminary determination) 

The NSW Scientific Committee has made a preliminary determination to list ‘alteration to the 

natural flow regimes of rivers and streams and their floodplains and wetlands’ as a key 

threatening process under the TSC Act. The NSW Scientific Committee has found that this 

process is recognised as a major factor contributing to loss of biological diversity and 

ecological function in aquatic ecosystems, including floodplains (NPWS 2001a). The NSW 

Scientific Committee describes alterations to natural flow regimes as either reducing or 

increasing flows, altering seasonality of flows, reducing frequency, duration and magnitude 

of flow events, altering water levels and increasing the rate of fall of water levels (Walker 

1985; Cadwallader & Lawrence 1990; Gehrke et al. 1995; Kingsford 1995. Maheshwari et al. 

1995; Robertson et al. 1999, 2001; NPWS 2001a). 

A high proportion of flow alterations to the majority of streams across New South Wales have 

had a major impact on the pattern of natural flows in these waterways. Alteration of flows 

reduces habitat by changing the area, frequency and duration of flooding of floodplains and 

terminal wetlands. Increasing flows causes more permanent flooding of wetlands, riparian 

zone degradation, increased habitat for invasive species, and loss or disruption of ecological 

function. Threatened species recorded within the DRP affected by this process include the 

blue-billed duck, and freckled duck (NPWS 2001a). 

Installation and operation of instream structures that modify flow (proposed 

recommendation) 

The Fisheries Scientific Committee has made a recommendation to list ‘Installation and 

operation of instream structures that modify flow’ as a key threatening process under the 

FMA, 1994. The Fisheries Scientific Committee identifies instream structures which modify 

flow as including dams, weirs, navigation locks, floodgates, culverts, flow regulators, levee 

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banks, erosion control structures and causeways (FSC 2001d). Ecosystem effects related to 

these structures include: cold water releases from dams impair spawning, growth, 

recruitment, feeding and other life cycle processes in native fish species; present barriers to 

migration of native fish species and provide ideal habitat for invasive species; changes of 

seasonality and variability of flow regimes disrupt natural environmental cues necessary for 

reproductive cycles in native fish, reduction in total availability of water for riverine 

ecosystems, and interrupt or change natural processes of sediment deposition, erosion and 

transport which result in loss of fish habitat including important feeding and breeding sites. 

Threatened fish species recorded in the DRP affected by this process include Murray 

hardyhead (Craterocephalus fluviatilis), trout cod (Maccullochella macquariensis), and silver 

perch (Bidyanus bidyanus) and endangered populations of olive perchlet (Ambassis agassizii) 

and purple-spotted gudgeon (Mogurnda adspersa) (FSC, 2001d). 

7.3 WEEDS AND PEST ANIMALS 

7.3.1 Weeds 

The invasive and degrading nature of environmental weeds poses a significant threat to the 

management of remnant vegetation and the conservation of native fauna and flora. Weed 

problems throughout this bioregion are becoming progressively worse, exacerbated by land 

degradation, the increased mobility of vehicles and population pressures. Weeds can compete 

vigorously with native plants for resources, affecting the microclimate and increasing the 

susceptibility of native plants to disease. Weeds also generally provide poor habitat for native 

fauna when compared with native plants. The impact of weed invasion on vegetation 

communities increases with a decrease in the size of remnant native vegetation communities. 

Aquatic weeds such as Eichhornia crassipes and floodplain weeds such as Phyla canescens 

are an especially significant problem for the extensive wetlands and rivers of this bioregion. 

In Narran Lakes Nature Reserve noogoora burr (Xanthium occidentale) and Bathurst burr 

(Xanthium spinosum) are common along the river. Golden dodder (Cuscuta campestris) is a 

weed that has invaded the wetlands, particularly the lignum communities (NPWS 2000a). In 

the Macquarie Marshes Nature Reserve, lippia (Phyla cansecens) has also become a common 

weed (Shelly, D., DLWC, pers. com. Dec. 2001). 

Bitou bush is the only weed of national significance which has been recorded within the DRP 

(National Weeds Strategy Executive Committee 1999). Only two records of this species are 

listed in the DRP databases (Section 4.1.1). 

Declared noxious weeds in the DRP and the area for which they are declared are listed in 

Table 7.1 and Appendix D lists all exotic flora recorded within the DRP. 

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Table 7.1 

(NSW Agriculture, 2001) 

Declared noxious weeds occurring within the DRP 

Scientific Name Common Name Categories Area Declared 

Alternanthera pungens khaki weed W2 W 

Heliotropium amplexicaule blue heliotrope W2 Bo, C, L, Nbi, Nmn 

Raphanus raphanistrum wild radish W2 L, P 

Cuscuta campestris golden dodder W2 Bo, Bk, Bre, CD, C, L, MP, Nbi, Nmn, P, U, W 

Sorghum halepense Johnson grass W2 Bo, Bk, Bre, CD, C, L, MP, Nbi, Nmn, P, U, W 

Cenchrus incertus W2 Bk, Bre, C, L, MP, Nbi, Nmn, P, W 

Cestrum parqui green cestrum W2 Bo, Bk, Bre, CD, C, MP, Nbi, Nmn, P, U 

Lycium ferocissimum African boxthorn W2 Bk, Bre, CD, C, L, MP, Nbi, P, U, W 

Solanum rostratum pincushion nightshade W2 L 

Ibicella lutea yellow-flowered devil's W2, W3 W, L, P 

claw 

Asphodelus fistulosus onion weed W3 W 

Xanthium occidentale noogoora burr W3 Bo, Bk, Bre, C, L, MP, Nbi, Nmn, P, W 

Xanthium orientale Californian burr W3 Bo, Bk, Bre, C, L, MP, Nbi, Nmn, P, W 

Xanthium spinosum Bathurst burr W3 Bo, Bk, Bre, C, L, MP, Nbi, Nmn, P, W 

Echium plantagineum Patterson's curse W3 MP 

Salvia reflexa mintweed W3 MP 

Marrubium vulgare horehound W3 W 

Pennisetum villosum feathertop W3 MP 

Phyla canescens lippia W4c MP 

Phyla nodiflora var nodiflora lippia W4c MP 

Opuntia aurantiaca tiger pear W4f Bo, Bk, Bre, CD, C, L, MP, Nbi, Nmn, P, U, W 

Opuntia stricta prickly pear W4f Bo, Bk, Bre, CD, C, L, MP, Nbi, Nmn, P, U, W 

Opuntia stricta var stricta common prickly pear W4f Bo, Bk, Bre, CD, C, L, MP, Nbi, Nmn, P, U, W 

KEY 

Bo Bogan MP Moree Plains 

Bk Bourke Nbi Narrabri 

Bre Brewarrina Nmn Narromine 

CD Central Darling P Parkes 

C Cobar U Unincorporated 

L Lachlan W Wentworth 

1.1.2 Dense tree and shrub regeneration 

The problem of unpalatable native shrubs or ‘woody weeds’ in this region is viewed as a 

threat to both agriculture and conservation. Woody weeds are dense regeneration of some 

native species of trees and woody shrubs as a result of favourable climatic conditions in 

association with the prevailing agricultural management of the land. The Macquarie-Bogan 

floodplain has extensive areas of ‘woody weeds’ with most occurring to the west of the 

Bogan River adjacent to the Barwon River. Shrubs regarded as a problem include Eremophila 

sturtii, Eremophila mitchellii, Dodonaea viscosa subsp. angustissima, Senna artemisioides 

var. nemophila (punty bush) and Senna artemisioides (silver cassia) (Howling 1997, Noble 

1997). There is an urgent need to research the ecological processes producing the ‘woody 

weed problem’. It is important to remember that they are native species and that they have 

been recorded as growing in impenetrable densities at the time the early explorers moved 

through this region and some prefer or are restricted to dense communities. 

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7.3.2 Kangaroos 

Aerial survey by NPWS of red and grey kangaroos Macropus rufus, M. giganteus and M. 

fuliginosus in 1995 and 1996 indicate that densities in the western region portion of the DRP 

vary from quite low to moderately high and vary between years. Extremely high numbers of 

kangaroos occur through the Gingham watercourse subjecting the regularly flooded areas to 

extremely high grazing pressure (McCosker 1996). All wetlands within the DRP potentially 

become drought refuges in dry years, leading to very high numbers concentrated in relatively 

small areas and, therefore, increased grazing pressure in these areas. 

7.3.3 Feral animals 

The alluvial plains and basins of the DRP in the Western Division are considered to be 

primary pig habitat. Pigs are widespread throughout the DRP. However large number occur 

in richer areas such as the Gingham wetlands and the Macquarie Marshes. Numbers have 

been reduced significantly in these two wetlands through control programs. This needs to be 

maintained. Foxes and cats are present in the Gingham wetlands and the Macquarie Marshes 

and can cause significant damage to the nesting waterbirds and their fledglings. Other feral 

mammal species recorded in the DRP are listed in section 5.5.4. 

7.4 OTHER THREATS TO BIODIVERSITY 

Other factors considered to potentially reduce biodiversity in the DRP include illegal hunting 

and collecting, firewood collection and private timber harvesting. The effects of salinity on 

wetland, river and land health are discussed in Chapter 2. 

7.4.1 Firewood collection and timber harvesting on private lands 

The tree species most commonly used for firewood in NSW are Eucalyptus polyanthemos 

(red box), Eucalyptus melliodora, Eucalyptus blakelyi and Eucalyptus camaldulensis, all of 

which occur and are harvested in the DRP. Seventy six per cent of all firewood collected in 

New South Wales is taken from fallen timber resources, 19% from standing dead timber and 

5% from standing live timber. Many species of invertebrates feed on dead wood and are 

likely to be adversely affected by firewood collection. This affects other species such as 

fungi that rely on these invertebrates for their dispersal and also affects the rates of decay 

within forests and woodlands (Driscoll et al. 2000). Firewood distribution to wood yards can 

also distribute invertebrate species outside their natural range and enhance the potential for 

competition with local indigenous species (Todd & Horwitz 1990). 

Threatened species recorded in the DRP which may be affected by firewood collection 

include the spotted-tailed quoll, squirrel glider, square-tailed kite, bush stone curlew, glossy 

black-cockatoo, superb parrot, turquoise parrot, barking owl, masked owl, regent honeyeater, 

painted honeyeater and Hoplocephalus bitorquatus (Driscoll et al. 2000). 

Timber harvesting particularly affects tree-dwelling or hollow-nesting native fauna and can 

destroy understorey vegetation and vegetation structure, which is also essential for the 

maintenance of biodiversity (Benson 1999). 

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7.4.2 Grazing 

Grazing by domestic sheep and cattle together with the introduced goat and rabbit, and the 

increasing numbers of native macropods, has led to a reduction in total plant biomass and an 

altered vegetation structure. Continuous grazing can prevent plant regeneration and reduce 

seedling recruitment (Benson 1999). Grazing of domestic stock mostly occurs on leasehold 

and private land, with grazing permits also being issued by Rural Lands Protection Board and 

NSW State Forests for some Crown land. 


7.5.1 Summary 

Fifteen listed or preliminary determinations of key threatening processes have been made 

under the TSC Act and/or EPBC Act which are likely to negatively affect the biodiversity of 

the DRP. Another four key threatening processes are listed for fish under the FMA, 1994 by 

the Fisheries Scientific Committee. In addition to these threatening processes, weeds and pest 

animals, firewood collection, private timber harvesting and grazing are threats to the 

biodiversity of the bioregion. 

The extent and severity of the majority of these identified threats in the DRP has not been 

assessed nor have threat abatement procedures been determined. 


It is necessary that data be gathered for the assessment of conservation values of the DRP, 

allowing for a comprehensive bioregional assessment to be undertaken and to assist in the 

development of conservation strategies for threatening processes. This requires: 

collection of detailed information about listed key threatening processes and their effects 

on biodiversity within each province; 

development of monitoring strategies for effects of key threatening processes; 

definition and mapping of ecosystems at a useful resolution such as across the whole of 

the DRP to assist conservation assessment and reservation or restoration of these 

endangered ecological communities; and 

identification of ecological processes and establishment of studies to examine the function 

of ecological processes and their function in the DRP. 

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8 EXISTING 

CONSERVATION 

MANAGEMENT 

8.1 EXISTING CONSERVATION ASSESSMENTS 

The conservation of biodiversity, regardless of the mechanisms used, requires an 

understanding of the natural variation and patterns inherent across landscapes, ecosystems, 

habitats, communities, populations and species. Critical to the retention of biodiversity is the 

need to protect whole ecosystems or landscapes rather than individual components of these. 

Priority Action 13 of the New South Wales Biodiversity Strategy aims to “adopt a 

standardised, integrated, whole-of Government approach to the collection, analysis and 

distribution of biodiversity data for use in assessing the conservation significance of land 

areas throughout New South Wales” (NPWS 1999b). This calls for assessments to be made 

on a bioregional basis with the aim of providing biodiversity information for all tenures, with 

a priority being the systematic and cost-effective collection of information, enabling gaps in 

information to be identified and addressed. A bioregional approach to conservation 

recognises homogeneity of environmental patterns and ecological processes and the processes 

that generally threaten biodiversity, such as landscape degradation, erosion and vegetation 

clearing. The framework for the bioregional conservation assessment is illustrated in Figure 

8.1. 

The NSW Biodiversity Strategy defines the primary objective of bioregional conservation 

assessments as to ‘identify areas and features of high biodiversity significance and to advise 

on appropriate conservation measures’. These measures will then be used to make informed 

land management decisions through the following mechanisms and organisations (NPWS 

1999b): 

Native Vegetation Conservation Act, 1997 (NVC Act). The Regional Vegetation 

Committees empowered by this act will use ecosystem-based biodiversity information to 

develop Regional Vegetation Management Plans; 

Catchment management under the Catchment Management Act, 1989. Catchment 

Management Boards are developing Catchment Blueprints which will set targets for 

improved land management across all catchments; 

Voluntary participation by landholders using programs such as Land for Wildlife, 

Wildlife Refuges and Voluntary Conservation Agreements ; 

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River Management Plans under the Water Management Act, 2000. Water Management 

Committees have developed interim river flow objectives for all catchments across the 

state; 

Farming for the Future programs run cooperatively between NPWS, NSW Agriculture, 

Department of Land and Water Conservation and NSW Farmers Association; 

Bushcare regional planning funded by Natural Heritage Trust; 

Comprehensive, adequate and representative (CAR) reserve system planning; 

Local and Regional Environmental Plans under the Environmental Planning and 

Assessment Act, 1979; and 

Recovery Planning for threatened species and endangered ecological communities and 

Threat Abatement Planning under the TSC Act. 

The DRP is dominated by water driven, and water derived habitats and environments. One of 

the major requirements in planning for the conservation of this landscape is to assess the 

abiotic and biotic factors that drive the ecosystem function of the bioregion. Conservation 

criteria are required to identify conservation values across the bioregion and integrated 

planning should include modelling of the climatic influences and an analysis of the issues 

affecting river health within the bioregion. 

At this stage less than one percent of the DRP bioregion is managed as conservation reserve 

(Pressey et al. 2000), with 0.89% as National Parks or Nature Reserves. The existing reserves 

are unrepresentative of the range of physical and ecological characteristics of the bioregion 

(Thackway & Cresswell 1995). Most of the defined landscapes within the DRP are not within 

reserves, and those within the eastern portion of the DRP have no potential for reservation, 

because there are no large areas of native vegetation remaining. Areas along the Macquarie 

River have intermediate levels of reservation and landscapes in the western division have 

been classified as having a lower priority for immediate conservation action (Table 8.1, 

Pressey et al. 2000). Some key areas which are appropriate for inclusion in a integrated 

landscape conservation network were defined by Morgan and Terry (1992) using a range of 

factors including size, diversity, shape, level of disturbance, integrity of catchments, 

adjoining land uses and, for the western division, property boundaries. 

Table 8.1 Reservation status of major regional ecosystems in the DRP 

(adapted from Morgan & Terry 1992) 

Province No. major regional Reservation Status* 

ecosystems Adequate Inadequate Nil 

Bogan-Macquarie 3 1 1 1 

Castlereagh-Barwon 3 1 2 

Culgoa-Bokhara 3 3 

Warrambool-Moonie 3 3 

Narran-Lightning Ridge 3 1 2 

Collarenebri Interfluve 1 1 

Louth Plains 2 2 

Wilcannia Plains 3 3 

Menindee 4 2 1 1 

NB: These figures do not include the additions to the NPWS estate of Culgoa National Park (Culgoa – Bokhara Province), Tillpilly station 

(Wilcannia Plains Province) and Mount Murchison (Wilcannia Plains Province) 

KEY 

* Number of ecosystems having the following reservation status: 

Adequate – protected in large reserve, or in several smaller reserves 

Inadequate – protected only in small and isolated reserves, or a small occurrence in a larger reserve 

132

Initial Phase 

Assessment Phase 


Indicative Timeframes 

1-2 years 

1-2 years 

(DRP is at this stage) 

Nil - Not protected to any extent 

Selection of most 

appropriate / applicable 

existing datasets for 

conservation assessment 

Assessment of relative 

conservation values of 

the bioregion 

Data audit - review existing data 

sets and mapping regarding 

applicability for conservation 

assessment 

Production of new 

bioregion-wide 

mapping 

Compilation of final mapping 

and datasets suitable for 

conservation assessment 

Assessment of current, past 

and potential threatening 

processes and their affects 

Identification of the conservation status of 

landscapes / areas / biodiversity within the 

bioregion and management required 

Sub-division of the bioregion into 

management units eg remnant habitats, 

corridors, wetlands, provinces 

Identification of potential conservation 

outcomes and management requirements 

for each management unit 

Figure 8.1. Bioregional conservation assessment framework 

Data collection - 

eg flora and fauna 

surveys, vegetation 

mapping, cultural 

heritage 

assessment, and 

further abiotic data 

collection 

133 

Community consultation and involvement


8.2 FORMAL RESERVES AND OTHER CROWN LANDS 

8.2.1 National Parks and Nature Reserves 

Eight conservation reserves and two recently acquired properties managed by the New South 

Wales NPWS are within or partially within the DRP (Map 4). These reserves cover an 

estimated area of 82 357ha, or 0.89% of the total land area of the bioregion. 

Culgoa National Park 

Culgoa NP (NPWS 2001b) is located 40 km west of Goodooga in northern NSW and adjacent 

to the Queensland border. The reserve was created in 1996, with additions in 1998, and 

covers an area of 22 430 ha along the Culgoa River and associated floodplains. The reserve is 

made up of the former pastoral leases of Byerawering, Cawwell and Burban Grange.. The 42 

800 ha Culgoa Floodplain NP in Queensland joins the north western boundary of Culgoa NP 

creating a nationally significant park system. 

The significance of Culgoa National Park is described in the draft plan of management 

(NPWS 2001b). The park includes one of the least disturbed floodplains in New South Wales 

and it also incorporates regionally and nationally significant vegetation and faunal 

communities. The vegetation communities present are otherwise poorly represented or 

unrepresented within the current reserve system. The Culgoa floodplain also contains the core 

of the largest and least disturbed area of continuous Coolabah (Eucalyptus coolabah) 

woodland remaining in NSW. It contains a diverse fauna, with 19% of species present being 

of regional or national conservation significance. 

The soils of Culgoa River floodplain are dominated by grey cracking clays, interspersed with 

sandy soils and non-cracking clays associated with rises and claypans. In the western section 

of the reserve, boulders of silicified sandstone and conglomerate combined with red and 

brown silt and sand form a type of gibber plain which is more widespread outside of the 

reserve. 

Vegetation communities in Culgoa NP include: 

Riverine communities - Eucalyptus camaldulensis and Melaleuca trichostachya (river 

paperbark) line the river channel, with Acacia stenophylla, Eremophila bignoniiflora, 

Paspalidium jubiflorum and Cyperus concinnus in the shrub and understorey layers. 

Floodplain communities - Forests and woodlands near the Culgoa River are dominated by 

Eucalyptus coolabah, with an understorey of grasses, sedges or Muehlenbeckia florulenta. 

Woodland on grey cracking clays and red-brown soils - In the western sections of the 

reserve woodland of Eucalyptus coolabah, Acacia harpophylla and Acacia cambagei with an 

understorey of chenopods including Atriplex nummularia, Atriplex vesicaria and Enchylaena 

tomentosa. 

Woodland on low, sandy rises - Low sandy rises support mixed woodland of Eucalyptus 

coolabah, Eucalyptus populnea subsp. bimbil, Acacia cambagei and Acacia harpophylla. 

Common shrubs and understorey plants include Atalaya hemiglauca, Alectryon oleifolius, 

Myoporum montanum and Apophyllum anomalum. 

Shrubland on red and white sand deposits - This community consists of Acacia 

murrayana, Callitris glaucophylla, Santalum lanceolatum (sandalwood), Ventilago viminalis, 

Canthium oleifolius, Geijera parviflora, Dodonaea viscosa subsp. angustifolia (narrowleaved 

hopbush) and Pimelea penicillaris (sandhill rice-flower). 

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Grasslands - To the east of the Culgoa River grasslands of Agrostis avenacea and Eragrostis 

setifolia occur with scattered Muehlenbeckia florulenta. On scalded or sandy rises daisies and 

chenopods become more common. 

Kinchega National Park 

This National Park covers an area of 44 182 ha and is 113 km south east of Broken Hill. The 

majority of this reserve occurs within the DRP with a small portion extending into the Broken 

Hill Complex bioregion. The park was established in 1967 with the acquisition of Western 

Lands leases within Kars and Kinchega stations. Prior to acquisition, the area had been grazed 

for more than 100 years (NPWS 1996). 

Kinchega National Park is the only national park in New South Wales on the Darling River, 

and includes Lake Menindee and Lake Cawndilla, two of the largest lakes of the Menindee 

Lakes Storage Scheme. These lakes provide important habitat for regionally significant 

waterbird species. The National Park also includes several land units of the lower Darling 

River including areas of floodplain, overflow lakes and channels, lunettes, sandplains and 

sand dunes. The alluvial habitats have been superimposed on extensive areas of red sandplain. 

In this area of increasing agricultural development along the lower Darling River, the Park 

protects a nucleus of viable ecological communities. 

The natural overflow depressions of Lake Menindee and Lake Cawndilla are managed by the 

Department of Land and Water Conservation (DLWC) which retains the right to fill and 

empty the lakes as part of its water management operations. The lakebeds are held as a 

permissive occupancy by the New South Wales NPWS from DLWC and are managed as part 

of the park. 

A large number of Aboriginal sites exist in the Park. Most are less than 5 000 years old and 

show a changing pattern of occupation as the Willandra Lakes system dried out and 

Aboriginal people moved into wetter areas near the lower Darling River. Sites include 

burials, campsites, middens, cooking pits, stone artefacts and scarred trees. A number of 

significant fossil animal remains have been found in the lunettes adjacent to the lakes. 

Kinchega Station was one of the earliest European settlements along the Darling River. The 

woolshed was built from local timbers in 1872 and has been restored. 

Vegetation communities include: 

Eucalyptus camaldulensis open forest - along the Darling River and major channels on 

heavy-textured cracking clay; 

Eucalyptus largiflorens open woodland - on flat, black soil floodplains extending away from 

the river, with Eucalyptus coolabah on billabong banks; 

Lake foreshore - dominated by Morgania glabra (blue rod) and Zygochloa paradoxa 

(sandhill canegrass); 

Red sand-dune shrubland - Casuarina cristata, Alectryon oleifolius, Acacia sp. and D. 

attenuata are dominant on the dune crests, with Acacia victoriae, Acacia loderi, Hakea 

leucoptera (needlewood) and Maireana pyramidata on the sandplains 

Maireana pyramidata / Zygochloa paradoxa lunettes - on sand and clay dunes on the lake 

margins. 

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Boronga Nature Reserve 

This Reserve covers 195 ha and is located 16 km east of Boomi. Boronga State Forest was 

dedicated in 1920 and used for grazing and timber extraction until the dedication of the nature 

reserve in 1976. Cropping, grazing and cotton production properties surround the reserve. 

Soils of the reserve range from dark clay floodplain soils to deep sand ridges (Hunt 1993a). 

Boronga Nature Reserve contains a carbeen open forest community, which is listed as an 

endangered ecological community under the TSC Act. This community is only reserved in the 

three small areas of Boronga, Boomi and Boomi West Nature Reserves. The surrounding area 

have been extensively modified for agricultural production. 

Vegetation communities in the reserve are: 

Callitris glaucophylla woodland - mature and regrowth Callitris glaucophylla with scattered 

Corymbia tessellaris and grassy understorey on sandy soils; 

Eucalyptus populnea subsp. bimbil woodland - clay soils support Eucalyptus populnea 

subsp. bimbil woodland with scattered Eucalyptus melanophloia and a shrub layer of Geijera 

parviflora and Eremophila mitchellii; 

Casuarina cristata woodland - on seasonally waterlogged clay soil areas, with no shrub 

understorey and few grasses; 

Corymbia tessellaris woodland - Corymbia tessellaris with Eucalyptus populnea subsp. 

bimbil and Callitris glaucophylla, understorey of Geijera parviflora, Eremophila mitchellii 

and Corymbia dolichocarpa on sandy soils; 

Casuarina cristata / Eremophila mitchellii shrubland - on clay soils; 

Corymbia tessellaris / Corymbia dolichocarpa woodland - on sandy soils with Callitris 

glaucophylla; 

Cleared grassland – on sandy soils; 

Corymbia tessellaris / Callitris glaucophylla woodland - woodland on sandy soils with a 

grassy understorey, sometimes mixed with Eucalyptus blakelyi. 

Boomi and Boomi West Nature Reserves 

Boomi Nature Reserve covers 156 ha and is located 2 km east of Boomi and 17 km south of 

the Macintyre River. Boomi West Nature Reserve covers 149 ha and is located 6.5 km west 

of Boomi and 17 km south of the Macintyre River (Butler 1996). 

These reserves contain carbeen open forest community, which is a listed endangered 

ecological community under the TSC Act. This community is only reserved in one other small 

area within Boronga Nature Reserve. Aboriginal scarred trees exist on the reserve and the 

wetland area provides habitat for a variety of waterbirds. 

Vegetation communities include: 

Native grassland - dominated in Boomi by Chloris truncata (windmill grass) and Aristida 

jerichoensis (No. 9 wiregrass) with emergent Acacia salicina, Geijera parviflora, Acacia 

excelsa and Atalaya hemiglauca; in Boomi West contains Panicum sp. (hairy panic), 

Bothriochloa macra (red grass), Setaria geniculata (pale pigeon grass) and a number of weed 

species; 

Eucalyptus populnea subsp. bimbil woodland - shrub species include Eremophila mitchellii, 

Casuarina cristata and Geijera parviflora, and the groundcover Bassia birchii (galvanised 

burr), Themeda australis (kangaroo grass) and Bassia divaricata (pale poverty bush); 

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Callitris glaucophylla forest - associated species Corymbia tessellaris, Eucalyptus populnea 

subsp. bimbil and Eucalyptus coolabah. The understorey contains Paspalidium jubiflorum; 

Eucalyptus coolabah / Casuarina cristata woodland - in Boomi West with an understorey 

containing Paspalidium jubiflorum. 

Macquarie Marshes Nature Reserve 

The Macquarie Marshes Crown Land was first declared a game reserve in 1900 and then 

declared a sanctuary (Birds and Animals Protection Act 1918-1930 and Fauna Protection Act 

1980). The reserve covers an area of 18 143 hectares and is divided into two sections: the 

Northern Marsh and Southern Marsh. The importance of the Marshes has been recognised by 

its inclusion in several agreements and registers including the Ramsar Convention, JAMBA 

and CAMBA. The plant communities in this reserve are described in Section 3.3.4. 

The Macquarie Marshes Nature Reserve protects part of the internationally important 

Macquarie Marshes, one of the largest remaining inland semi-permanent wetlands in south 

eastern Australia. The Marshes contain the largest area of reeds (Phragmites sp.) in south 

eastern Australia. The Nature Reserve includes significant stands of river red gum 

(Eucalyptus camaldulensis) and coolibah (E. coolabah). They are important to nine migratory 

bird species listed in the Japan-Australia and China-Australia Migratory Bird Agreements and 

eighteen endangered bird species. The Marshes are also a refuge for many native animals and 

are the western limit of the known distribution of Gould’s long eared bat (Nyctophilus 

gouldii) in NSW. 

A range of significant Aboriginal sites including oven mounds, surface campsites, scarred 

trees and artefacts exist within the Nature Reserve. 

Narran Lake Nature Reserve 

Narran Lake Nature Reserve is located between Brewarrina and Walgett in northern New 

South Wales and includes part of the terminal wetlands of the Narran River. The 5 538 ha 

reserve was dedicated in 1988 and an additional 3 547 ha adjoining the reserve is owned by 

the NPWS and managed as part of the reserve. The reserve covers the north-eastern third of 

the Narran Lake wetland system and does not include Narran Lake itself (NPWS 2000a). 

This Reserve is listed on the national estate and recognised as a wetland of international 

importance under the Ramsar convention. Approximately half of the nature reserve consists 

of wetlands subject to inundation by the Narran River, including two small lakes, Back and 

Clear Lakes, and extensive surrounding channelised wetlands. Aeolian lunettes and sandy 

levees border the wetlands. The other half of the reserve has gently undulating sandy and 

rocky ridges with several semi-saline playa lakes and drainage depressions. 

Aboriginal camp sites are present around the lake and the area also contains oven mounds and 

shell middens, scatters of stone artefacts associated with clay ground ovens and several small 

silcrete quarries on the colluvial ridge system. 

There are six dominant vegetation communities: 

Muehlenbeckia florulenta thickets - dense shrublands in the littoral zone of Clear and Back 

Lake; small areas of Phragmites australis between the lignum and sedges, ephemeral herbs 

and grasses grow on playa lakes and the main lake beds after floodwaters recede. 

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Riparian open forest - Eucalyptus camaldulensis, Eucalyptus coolabah, Eucalyptus 

largiflorens and Acacia stenophylla fringe the river and wetland channels, Acacia stenophylla 

extends into lignum shrublands; 

Chenopod low open scrub and ephemeral herbfield - chenopods such as Sclerolaena 

diacantha and Sclerolaena decurrens and grasses grow on sandy lakeshore and dune areas; 

Mixed low woodlands - woodland of Eucalyptus populnea subsp. bimbil, Callitris 

glaucophylla and a variety of tall shrubs grows on sandy ridge country; 

Acacia aneura low woodland - rocky areas support small stands of Acacia aneura; 

Spinifex hummock grassland and low woodlands - Small areas of woodland of Eucalyptus 

melanophloia, Brachychiton populneum and Angophora melanoxylon (coolibah apple) grow 

in association with Triodia mitchellii (spinifex). 

Midkin Nature Reserve 

This 360 ha reserve is located approximately 16 km north-west of Moree. It was formerly a 

State Forest (established in 1921) and was subject to timber harvesting and grazing until the 

dedication of the nature reserve in 1976. Land surrounding the reserve is used for cropping, 

grazing and cotton production. Black clays, sands and gravel form the soils of the reserve 

(Hunt 1993b). 

Vegetation communities in the reserve, in addition to cleared grassland, are: 

Eucalyptus coolabah open woodland - woodland with various grasses restricted to a small 

patch on the edge of the reserve; 

Eucalyptus populnea subsp. bimbil woodland - contains stands of Callitris glaucophylla, 

and the understorey species Eremophila mitchellii, Geijera parviflora and Capparis 

mitchellii; 

Eucalyptus populnea subsp. bimbil / Eucalyptus melanophloia woodland - located in the 

centre of the reserve with Callitris glaucophylla regrowth and grassy understorey. 

Tilpilly additions 

In 2000 the New South Wales NPWS acquired the former Tilpilly Station, south east of Tilpa 

and north-east of Wilcannia. Most of the property lies within the Cobar Peneplain bioregion 

but a small section around Lake Tilpilly is within the DRP. The property has been grazed and 

some of the land has been cleared of woody vegetation. The area is identified as distinct 

within the Murray-Darling Depression. 

Within the landscape there is a closed drainage depression (Coonavitra Lake) surrounded by 

Eucalyptus populnea subsp. bimbil (bimble box) and Eucalyptus largiflorens (black box). 

Tillpilly Station is likely to provide an ideal habitat for many of the JAMBA and CAMBA 

bird species. The area on the Darling Riverine Plains provides a large overflow lake (Tilpilly 

Lake). These Muehlenbeckia florulenta (lignum) and Chenopodium spp. (goosefoot) areas 

would provide ideal breeding habitat for many duck species while the flooded grasslands 

would attract, among others, swans and grebes. These wetlands are set in a grassy open 

woodlands context. The woodlands contain a variety of trees including Casuarina sp. 

(belah), Callitris glaucophylla (white cypress pine), Alectryon oleifolius (rosewood), Acacia 

aneura (mulga) and shrubs including Eremophila sturtii (turpentine), Dodonaea sp. 

(hopbush), Senna spp. (cassia), Eremophila longifolia (emu bush) and are the dominant 

vegetation type of the Northern Dunefields area. 

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Mount Murchison 

In September 2001 the NPWS acquired the former Mount Murchison property, north-east of 

Wilcannia. Mount Murchison consists of the riverine corridor and floodplains of the Darling 

River and Darling Riverine Plains Bioregion, extending north into undulating country 

associated with the Mulga Lands Bioregion. The property includes 57 km of Darling River 

frontage. During heavy rain and flooding, there is a series of lakes, swamps and channels on 

the floodplain adjoining the Darling River that fill with water. Jamiesons Billabong in the 

south-eastern portion of the property is five kilometres long when full and can hold water for 

more than 12 months. The western portion of Mount Murchison also contains part of the 

Paroo Overflow, with the confluence of the Paroo River and the Darling River occurring just 

west of the property (NPWS 2001d). 

Mount Murchison provides habitat for a number of species listed under the TSC Act, 

including Australian bustard (Ardeotis australis), blue-billed duck (Oxyura australis), squaretailed 

kite (Lophoictinia isura), black-breasted buzzard (Hamirostra melanosternon), redtailed 

black-cockatoo (Calyptorhynchus banksii), Major Mitchell's cockatoo (Cacatua 

leadbeateri), Chalinolobus picatus (little pied bat), and Grevillea nematophylla (silver-leaved 

water tree) (NPWS 2001d). 

The main vegetation types on Mount Murchison include Eucalyptus camaldulensis (river red 

gum) open forest as a riparian strip along the Darling River, Eucalyptus coolabah (coolibah) 

open woodland on the Darling River floodplains, with Maireana pyramidata (black bluebush) 

and E. largiflorens (black box) low open shrubland on the adjoining hummocky sandplains. 

Off the floodplain, Casuarina pauper (belah) and Flindersia maculosa (leopardwood) tall 

open shrubland occurs on level sandplains, while an extensive herbland dominated by 

Eragrostis australasica (cane grass) and Muehlenbeckia florulenta (lignum) occurs on the 

undulating sandplain of McIntyres Plain at the northern end of the property. In general, the 

vegetation on Mount Murchison has been lightly grazed and is in excellent condition (NPWS 

2001d). 

8.2.2 Other Crown lands Managed For Conservation 

Other Crown lands, including Crown reserves, travelling stock reserves, state forests and 

leasehold lands, contribute to the conservation of biodiversity. Land area covered by these 

leases is indicated in section 1.3.3. Management practices carried out on each of these types 

of lands may differ across the bioregion and many of these areas have significant 

conservation values because the native vegetation has been retained and there has been 

minimal degradation. 

Sandgate Flora Reserve 

Sandgate Flora Reserve was gazetted in 1977 and is located within the Sandgate State Forest. 

The reserve covers 16 ha of Callitris glaucophylla (white cypress pine) – Eucalyptus blakelyi 

(Blakely’s red gum) forest. Mining is excluded in the reserve (Forestry Commission of NSW 

1989). 

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State Forests 

State forests within the DRP where threatened species have been recorded are listed in Table 

8.2. 

Table 8.2 Threatened fauna recorded within State forests of the DRP 

Common name Scientific name State Forest 

bush stone-curlew Burhinus grallarius Bourbah SF, Narraway SF 

barking owl Ninox connivens Bourbah SF, Narraway SF, Sandgate SF, Tallegar 

SF 

speckled warbler Pyrrholaemus sagittatus Gilgandra SF 

superb parrot Polytelis swainsonii Mellerstain SF, Sandgate SF 

glossy black-cockatoo Calyptorhynchus lathami Narraway SF 

little pied bat Chalinolobus picatus Narraway SF 

yellow-bellied sheathtail bat Saccolaimus flaviventris Narraway SF 

koala Phascolarctos cinereus Pilliga West SF 

diamond firetail Stagonopleura guttata Sandgate SF, Tailby SF 

The dominant vegetation types within State forests of the DRP are listed in Table 8.3. 

Table 8.3 Dominant vegetation types within State forests of the DRP 

(Forestry Commission of NSW 1984; 1986; 1988) 

Vegetation type State forests 

bimble box (Eucalyptus populnea subsp. bimbil) Berida SF, Bourbah SF, Sandgate SF, Tailby SF 

bimble box – belah (Casuarina cristata) Bourbah SF 

bimble box – white cypress pine (Callitris Berida SF, Bourbah SF, Gilgandra SF, Narraway SF, Pilliga 

columellaris) 

West SF, Sandgate SF, Tailby SF, Tallegar SF, Warrie SF 

bimble box – white cypress pine – forest oak 

(Allocasuarina luehmannii) 

Merrinele SF 

fuzzy box (E. conica) Eringanerin SF 

Blakely’s red gum (E. blakelyi) – rough barked apple Berida SF, Eringanerin SF 

(Angophora floribunda) – white cypress pine 

Blakely’s red gum – white cypress pine Bourbah SF, Eringanerin SF, Gilgandra SF, Merri Merri SF, 

Narraway SF, Sandgate SF, Tailby SF, Tallegar SF, Warrie SF 

Blakely’s red gum Bourbah SF 

white cypress pine – bimble box Bourbah SF, Pilliga West SF, Sandgate SF, Tailby SF, 

Tallegar SF, Warrie SF 

white cypress pine – fuzzy box Gilgandra SF 

white cypress pine – narrowleaf ironbark (E. crebra) 

– forest oak 

Pilliga West SF 

white cypress pine – narrowleaf ironbark – Blakely’s 

red gum 


white cypress pine – Blakely’s red gum – roughbark Berida SF, Eringanerin SF 

apple 

white cypress pine – bimble box – forest oak Merrinele SF 

white cypress pine – Blakely’s red gum Bourbah SF, Eringanerin SF, Gilgandra SF, Merri Merri SF, 

Narraway SF, Sandgate SF, Tailby SF, Tallegar SF, Warrie SF 

white cypress pine – Blakely’s red gum – narrowleaf 

ironbark 


white cypress pine – forest oak Merrinele SF 

140


8.3 OFF-RESERVE CONSERVATION 

8.3.1 Voluntary Conservation Agreements 

Voluntary conservation agreements (VCAs) are permanent arrangements between 

landholders and the Minister for the Environment of New South Wales regarding the use and 

management of the specified land. The National Parks and Wildlife Service administers these 

agreements. Conditions regarding agricultural use of the land vary. One VCA currently exists 

within the DRP and covers approximately 19 hectares. 

8.3.2 Wildlife Refuges 

Wildlife Refuges are a voluntary agreement between a landholder and the NPWS. Wildlife 

Refuges provide legal protection for the native plants and animals on the property. Wildlife 

Refuges can be entered into for the following purposes: 

conserving, preserving, propagating, and studying native plant and animals; 

conserving and studying natural environments; or 

creating simulated natural environments. 

Forty-eight Wildlife Refuges have been gazetted in the DRP, covering approximately 550 000 

ha (Table 8.4). 

Table 8.4 Wildlife Refuges within the DRP 

NPWS Area Approximate total area Number of Wildlife 

(ha) 

Refuges 

Broken Hill 232 000 11 

Cobar 169 000 7 

Coonabarabran 64 000 10 

Narrabri 87300 20 

Forest Management Zones 

Forest Management Zones (FMZs) are a classification system used by State Forest of NSW to 

classify areas of their estate in terms of intended management. This classification system is 

based on the “Nationally Agreed Criteria for the Establishment of a Comprehensive, 

Adequate and Representative Reserve System for Forests in Australia” (JANIS 1997). FMZs 

1-4 afford varying degrees of protection for natural and cultural values. FMZs 1-4, their 

management guidelines and relation to JANIS criteria are outlined in Table 8.5 below. FMZ 

classification is not yet finalised for the DRP. 

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(SFNSW 1999) 

FMZ category JANIS 

Zone 1 – 

special 

protection 

Zone 2 – 

special 

management 

Zone 3a – 

harvesting 

exclusions 

Zone 3b – 

special 

prescription 

Zone 4 – 

general 

management 

Table 8.5 Forest Management Zones 

Management objectives Size and boundaries Activities not 

criterion 

permitted 

dedicated management to 40ha or greater preferred any activity no 

formal maximise protection of boundaries to be based on permitted by a 

reserves very high natural and topographic features in working plan 

cultural conservation combination with major 

values 

cadastral boundaries 

informal specific management and 40ha or greater preferred any operation 

reserves protection of natural and boundaries to be based on prohibited by 

cultural conservation topographic features in the Minister 

values 

combination with major 

values management for 


minimum size is size required case by case 

protected by conservation of identified for the protection of value and assessment 

prescription values and/or forest facilitation of other dependent on 

ecosystems and their management activity 

specific 

natural processes boundaries to be based on special value 

topographic features in involved 


values management for 


minimum size is size required case by case 

protected by conservation of identified for the protection of value and assessment 

prescription values and/or forest facilitation of other dependent on 

ecosystems and their management activity 

specific 

natural processes boundaries to be based on special value 

topographic features in involved 



contributes management for native size based on harvesting none 

to JANIS timber production and practicalities – dependant of 

criteria conservation of broad local conditions 

values area habitat and boundaries based on 

protected by 

prescription 

environmental values 

surrounding FMZs 

8.3.3 Catchment Blueprints 

Catchment blueprints are 10 year plans produced by Catchment Management Boards. 

Catchment blueprints provide directions for natural resource activities and investment within 

each catchment. The purpose of catchment blueprints is to set targets for improved land 

management across all catchments. They will provide “focus and direction to individual and 

community initiatives, help coordinate government investment, such as extension work and 

grant funding, and contribute to the implementation of legislation such as the Native 

Vegetation Conservation Act 1997 and the Water Management Act, 2000” (DLWC 2001b). 

Draft catchment blueprints have been prepared for all Catchment Management Boards within 

the DRP. 

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8.3.4 Water Management Plans 

Water management committees, which include River Management Committees, have the 

responsibility of developing river flow regulations. Jurisdictions of water management 

committees vary, as some deal with regulated rivers and others deal with unregulated rivers 

and groundwater. Interim river flow objectives have been developed for all catchments within 

the DRP and river management committees use these objectives in preparing the flow 

regulations for their management plans (EPA 2000). Environmental flows aim to restore, to 

some degree, natural flows within each catchment. 

River flow regulations differ from catchment to catchment and include various combinations 

of the following criteria (EPA 2000): 

“off-allocation access rules - restrictions on extraction of naturally occurring high 

flows; 

transparent dam rules - releases from water storages are matched to inflows (usually 

confined to relatively small inflows); 

translucent dam rules - a percentage of inflows to the dam must be released (usually 

confined to periods outside the irrigation season); 

contingency allowances - a bank of water reserved in the dam and released for specific 

environmental purposes (such as flushing algal blooms or providing water to complete 

fish or waterbird breeding); 

end of system flows - releases to ensure that the river provides water for downstream 

waterways (beyond the end of the river); and 

diversion thresholds - these require extractions to be reduced or to cease when flows 

are below a defined level.” 

River Management Committees for all major regulated rivers and the Barwon-Darling River 

developed flow rules in 1999 for 1999-2000 (EPA 2000) (Table 8.6). 

Table 8.6 River flow rules and implementation status within the DRP 

(EPA 2000) 

Drainage region River flow rule type Implementation status 

Border rivers (Regulated) Low-flow protection (Severn River) Operating since 1999; rules for 

other regulated sections are being 

Gwydir (Regulated) Protect low flows; off-allocation 

access rules; provision of water for 

environmental contingencies 

Namoi (Regulated) Off-allocation limits; retain low-flow 

requirements; off-allocation access 

rules 

Macquarie (Regulated) Maximum annual stock and 

domestic flows; off-allocation limits; 

provision of water for environmental 

contingencies 

negotiated with Queensland 

Operating since 1995 

Operating since 1998 

Water for Macquarie Marshes 

supplied since 1986 

Barwon-Darling (Unregulated) Protect low flows Being implemented in 2000 

Namoi, Castlereagh, Macquarie, Interim extraction limits Being developed 

Bogan, Condamine-Culgoa, 

Warrego, Paroo, (all Unregulated) 

Border rivers, Gwydir (all Protect low flows Being developed 

Unregulated) 

143


Groundwater management plans (GMPs) are being developed for areas of significant 

groundwater use or where groundwater resources require protection. The preparation of 

GMPs for specific areas and aquifers has been prioritised based on a risk assessment 

undertaken by DLWC, and is being managed by the Great Artesian Basin, Gwydir, 

Macquarie, and Namoi groundwater management committees within the DRP (EPA 2000). 

RMCs within the DRP are required to produce water sharing plans (Table 8.7). These plans 

are designed to establish environmental water rules, requirements for basic landholder rights, 

requirements for water extraction under access licences, and bulk access regimes for 

extraction licences (which determines how much water will be available for extraction by 

licensed water users) (DLWC 2001a). 

(DLWC 2001a) 

Water management 

area 

Central West 

Gwydir 

Table 8.7 Water sharing plans being prepared within the DRP 

Water management committee (MC) Type of water source Water source for which a water 

sharing plan is being prepared 

Macquarie Cudgegong River MC Regulated river Macquarie- Cudgegong Rivers 

Central West Unregulated Streams MC Subcatchment Castlereagh River above 

Binnaway 

Macquarie Groundwater MC Groundwater Lower Macquarie aquifer 

Gwydir River (Regulated) River MC Regulated river Gwydir River 

Gwydir Unregulated River MC Subcatchment Upper Horton River, Lower 

Horton River, Cobbodah Creek, 

Rocky Creek 

Gwydir Groundwater MC Groundwater Gwydir aquifer 

Namoi 

Namoi Regulated River MC Regulated river Namoi River 

Namoi Unregulated River MC Subcatchment Phillips Creek, Mooki River, 

Quirindi Creek, Warrah Creek 

Namoi Groundwater MC Groundwater Upper Namoi aquifer, Lower 

Western, Border Great Artesian Basin Groundwater MC Groundwater 

Namoi aquifer 

Great Artesian Basin 

Rivers, Gwydir, 

Namoi, Central West 

8.3.5 Regional Vegetation Management Plans 

Regional Vegetation Committees (RVCs) are responsible for producing Regional Vegetation 

Management Plans. Through the RVCs these plans enable communities to develop their own 

localised plans which deal with the native vegetation issues most affecting their region, such 

as native vegetation conservation, viability of agricultural production, dryland salinity and the 

conservation of native species (NSW Govt. 1999). RVCs are governed by the NVC Act, 1997 

and are coordinated through DLWC. 

By November 2001, the Mid-Lachlan RVC was the only RVC within the DRP that had 

completed a Regional Vegetation Management Plan. All other RVC’s within the DRP have 

Regional Vegetation Management Plans in varying stages of development. 

144


8.3.6 Salinity Management Plans 

The New South Wales Salinity Strategy (DLWC 2000) has established a series of targets 

aimed at reducing the effects of salinity in the state. A river-based end-of-valley salinity 

target program has been established to monitor overall salinity conditions. Six of these are 

located within the DRP. They are on the: 

Namoi River at Goangra; 

Macintyre River at Mungindi; 

Gwydir River near Collarenebri; 

Macquarie River at Carinda; 

Bogan River at Gongolgon; and 

Barwon-Darling River at Menindee. 

These end-of-valley salinity targets will measure the cumulative impact of past actions and 

the effects of future actions across each valley. Some of the management targets will include: 

no net loss of vegetation; 

revegetation of 20% of salt affected land; 

revegetation of 30% of recharge areas; 

introduction of deep rooted perennial pastures on 20% of pastures; 

development of and adherence to mid-catchment salinity targets to protect wetlands; 

changes in a variety of farming practices; and 

engineering solutions. 

A variety of pilot projects and government initiatives have been proposed and recommended 

as a part of the New South Wales salinity strategy. 

8.4 AREAS OF BIOLOGICAL SIGNIFICANCE 

8.4.1 Key areas 

Twenty key conservation areas and two corridors within the DRP were identified by Morgan 

and Terry (1992). Five of these are mainly located in adjoining bioregions but extend into the 

DRP. These areas cover 5 040 km 2 and are: 

Key area 1: Cowal State Forest (~ 500 ha) - the largest forested area remaining in the 

southern part of the Bogan-Macquarie province; 

Key area 2: A western extension of the northern section of the Macquarie Marshes Nature 

Reserve, containing Flindersia maculosa and Acacia pendula woodlands, in the Bogan- 

Macquarie province (350 km 2 ); 

Key area 3: Overlapping the boundary of the Bogan-Macquarie and Castlereagh-Barwon 

provinces, incorporating wetlands on a tributary of the Castlereagh and Eucalyptus populnea 

subsp. bimbil ridge country (270 km 2 ); 

Corridor: A major corridor along the Macquarie River downstream of Warren, connecting 

the Macquarie Marshes with Narran Lakes including the most reliable riverine environment 

in the sub-region; 

Key area 4: On the lower floodplain and channels of the Barwon River below Collarenebri, 

and including some higher areas of grey clays, in the Castlereagh-Barwon province (440 

km 2 ); 

145


Key area 5: In the Castlereagh-Barwon province near Thalaba Creek to the north west of 

Narrabri. The area consists of prior stream deposits and high-level floodplains of the upper 

alluvial fans (330 km 2 ); 

Corridor: A corridor along Thalaba Creek, mainly following the stock route along the 

Millie-Merrywinebone Road, connecting key areas 4 and 5; 

Key area 6: An extension from the Narran Lakes area south to the Barwon River to sample 

the broad and complex flood plain of the Barwon in the Castlereagh-Barwon province 

(300km 2 ); 

Key area 7: Based on the discontinuous band of State Forests on a low red rise in the south 

of the Castlereagh-Barwon province. Tallegar and Sandgate State Forests are the largest and 

least disturbed remnants and form part of a proposed corridor linking Warrie State Forest in 

the south-east to Narraway State Forest in the north-west (40 km 2 ); 

Key area 8: Includes the major land systems within the Culgoa-Bokhara province, and 

connects with proposed key area 11 for the Narran Lakes area (160 km 2 ); 

Key area 9: Contains land systems typical of the northern part of the Warrambool-Moonie 

province, and adjoins proposed key area 13 in the Collarenebri Interfluve province (140 km 2 ); 

Key area 10: Adjoins the large Narran Lakes key area, and is representative of the southern 

part of the Warrambool-Moonie province (410 km 2 ); 

Key area 11: A large and complex area within the Narran-Lightning Ridge province, 

including Narran Lake Nature Reserve. This would expand the Nature Reserve to include 

adjoining land systems and connect to key areas in adjacent provinces (1 380 km 2 ); 

Key area 12: In the northern section of the Narran-Lightning Ridge province and containing 

a wetland and sandstone ridge (150 km 2 ); 

Key area 13: The largest remaining example of intact natural vegetation in the Collarenebri 

Interfluve province, which is a restricted land unit in New South Wales (250 km 2 ); 

Key area 14: Spans the Darling flood plain and contains representative examples of all 

provincial land systems in the Louth Plains province (550 km 2 ); 

Key area 15: Spans the Darling flood plain and contains most of the land systems of the 

Wilcannia Plains province (330 km 2 ); 

Key area 23: Extends over the Culgoa River to include river fringing and flood plain 

communities typical of the Culgoa-Bokhara province, and areas of the Warrego fan natural 

region (360 km 2 ); 

Key area 40: Mostly located within the Darling Depression natural region, but contains areas 

representative of the overflow basins of the Wilcannia Plains province (240 km 2 ); 

Key area 55: Straddles the border of the Castlereagh-Barwon province and the northern 

sandstones natural region (mainly in the latter), and contains areas of grey clay communities 

(160 km 2 ); 

Key area 61: Extends from the Pilliga outwash natural region north west to the Namoi River, 

which is at the edge of the Castlereagh-Barwon province (220 km 2 ); 

Key area 90: Mostly located within the Cobar Peneplain natural region, but extends into the 

Louth Plains province on ancestral alluvials (790 km 2 ). 

8.4.2 Refugia 

Refugia are defined by EPA (2000) as ‘areas which have escaped the great changes 

undergone by a region as a whole, providing conditions in which relic communities of plants 

and animals can survive’. The DRP contains three of the nationally significant biological 

refugia listed in Morton et al. (1995) for arid and semi-arid Australia. They are the Macquarie 

Marshes, Narran Lakes and the Darling and Talyawalka Anabranch Lakes (Figure 8.2). 

Morton et al. (1995) also identified the Paroo wetlands, most of which are located in the 

146


adjoining Mulga Lands bioregion, as a nationally significant biological refugium. This 

analysis does not include the north eastern corner of the DRP which may contain significant 

refugia and requires analysis. 

The Macquarie Marshes provide drought refuge when other wetlands, especially inland 

wetlands, are dry. They provide habitat for a diverse reptile fauna that are aquatic or are 

strongly associated with water. Narran wetlands also provide important drought refuge for 

waterbirds when other inland wetlands are dry and support large nesting colonies of strawnecked 

ibis Threskiornis spinicollis and large concentrations of ducks when water levels 

recede. The third refuge area, the Talyawalka Anabranch of the Darling River and its 

distributary Teryawynia Creek, between Wilcannia and Menindee has large areas of 

Eucalyptus largiflorens (black box) and when inundated provides habitat for large numbers of 

waterbirds. 

Figure 8.2. Nationally significant biological refugia within the DRP 

(Morton et al. 1995) 

8.4.3 Centres of endemism 

The springs of the Great Artesian Basin contain unique and endemic biota and represent the 

only known centre of endemism within the DRP. This is discussed in Section 3.4. The fluvial 

landscape of the DRP has generally subtle biophysical changes with few unique and restricted 

147


landscapes, such as unique lithologies or mountain ranges, that may result in the evolution of 

centres of endemism for flora or vertebrate fauna. 

8.4.4 Areas of high biodiversity 

The patchy distribution of biodiversity data and data collection in the DRP makes it 

impossible to assess accurately the levels of biodiversity across the entire DRP. Most 

assessments have taken place in core blocks of remnant vegetation in the east of the 

bioregion, and diverse areas in the west of the bioregion where clearing has not had a great 

impact on biodiversity. The Macquarie Marshes and Narran Lakes wetlands appear to 

represent areas of high biodiversity but there have been no comparative analyses enabling 

areas of high biodiversity within the DRP to be defined. 

8.5 WILDERNESS VALUES IN THE DRP(NSW) 

The Wilderness Act, 1987 defines wilderness as an area of land that: 

(a) with its plant and animal communities, is in a state that has not been substantially 

modified by humans and their works or is capable of being restored to such a state; 

(b) is of a sufficient size to make its maintenance in such a state feasible; and 

(c) is capable of providing opportunities for solitude and appropriate self-reliant recreation. 

As outlined in the Wilderness Act, 1987, wilderness areas are to be managed so as to: 

(a) restore (if applicable) and to protect the unmodified state of the area and its plant and 

animal communities; 

(b) preserve the capacity of the area to evolve in the absence of significant human 

interference; and 

(c) permit opportunities for solitude and appropriate self-reliant recreation. 

The National Wilderness Inventory uses four indicators of wilderness quality: remoteness 

from settlement; remoteness from access; aesthetic naturalness; and biophysical naturalness. 

Knight (1998) identified 14 areas in a study of the wilderness quality of the Western Division 

of New South Wales. None of these fell within the DRP. This assessment did not include the 

portion of the DRP bioregion east of the Western Division administrative boundary (Map 9). 

With the extensive modification of land that has occurred in the eastern portion of the DRP 

since European settlement there is limited opportunity for any of this area to satisfy the 

requirements of the Wilderness Act. 


8.6.1 Summary 

Less than one percent of the DRP is managed in conservation reserves and a variety of other 

off-reserve conservation procedures are in operation within this bioregion. At present, the 

lack of detailed information makes it difficult to identify specific areas of high biodiversity or 

centres of endemism in this bioregion. Three nationally significant biological refugia have 

been identified in the western portion of the bioregion but more areas may be important at the 

bioregional level. 

148


Conservation assessment has been very limited in this bioregion but there have been 22 key 

areas identified as being important if the conservation gaps are to be filled. In the absence of 

detailed flora and fauna surveys and ecosystem mapping of the DRP, detailed analysis of the 

vegetation communities represented within the conservation reserves as a proportion of 

defined plant communities, and assessment of the Key areas should be carried out. 


Further work required in the DRP include the following: 

Evaluation of Water Management Plans, Catchment Management Plans and Regional 

Vegetation Management Plans to determine how the information contained in these 

documents can be used in a bioregional context; 

Implementation of a comprehensive and systematic conservation assessment of the DRP; 

Determination of the conservation values of the bioregion and each of its provinces using 

measures of diversity of land capability, vegetation communities, soils, species and 

habitats; and 

Preparation of a preliminary bioregional landscape framework with options for 

developing conservation management plans integrating conservation and production 

including: 

lists and descriptions of priority plant communities and priority conservation areas (e.g. 

largest remaining area of native vegetation, corridors, wetlands, rivers etc); 

identification of priority areas for restoration and regeneration; 

identification of other areas of regional significance such as aquifer recharge zones and 

priority catchments for management actions. 

149


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165


10 APPENDICES 

166

Appendix A: Mean Monthly Rainfall and Raindays for DRP 

(Bureau of Meteorology, 2001) 

mm 

45 

40 

35 

30 

25 

20 

15 

10 

5 

0 

30 

25 

20 

15 

10 

5 

0 

Trangie Mean Monthly Rainfall and Raindays 


Month 

Mean Monthly Rainfall Mean Monthly Raindays 

Bourke Mean Monthly Rainfall and Raindays 


Month 


15 

10 

5 

0 

15 

10 

5 

0 

raindays

mm 

70 

60 

50 

40 

30 

20 

10 

0 

80 

70 

60 

50 

40 

30 

20 

10 

0 

Walgett Mean Monthly Rainfall and Raindays 


Month 


Mungindi Mean Monthly Rainfall and Raindays 


Month 


15 

10 

5 

0 

15 

10 

5 

0 

raindays

80 

70 

60 

50 

40 

30 

20 

10 

0 

25 

20 

15 

10 

5 

0 

Moree Mean Monthly Rainfall and Raindays 


Month 


Menindee Mean Monthly Rainfall and Raindays 


Month 


15 

10 

5 

0 

15 

10 

5 

0

Appendix B: Land Systems within the DRP 

(Walker 1991) 

Major 

Rangetype 

Northern 

Floodplains 

Southern 

Riverine 

Woodlands 

Mitchell Grass 

Plains 

E. populnea - 

Pine 

Belah and 

Bluebush 

Rangetype Physiography Land System Area 

intersecting 

DRP (ha) 

% Land 

System 

% DRP 

Scalded floodplains Playas and Basins Popelloe 14 883 66% 0.2% 

Alluvial plains Rugby 192 317 99% 2.1% 

Hermidon 158 645 97% 1.7% 

Rostella 150 674 99% 1.6% 

Dunoak 50 482 68% 0.5% 

Gingie 48 969 99% 0.5% 

Budda 37 878 98% 0.4% 

Geera 27 146 99% 0.3% 

Tatala 19 706 81% 0.2% 

Dumble 17 252 98% 0.2% 

Pendiana 14 638 49% 0.2% 

Lakes and swamps Playas and Basins Thackenbie 50 700 96% 0.5% 

Rotten Plain 48 448 99% 0.5% 

Narran 27 196 99% 0.3% 

Walkdens 16 449 13% 0.2% 

Cobham 26

Major 

Rangetype 


intersecting 

DRP (ha) 

Sandplains and 

dunefields with 

Casuarina cristata 

and Alectryon 

oleifolius 

% Land 

System 

% DRP 

Oulilla 2 008 2%

Major 

Rangetype 


intersecting 

DRP (ha) 

% Land 

System 

% DRP 

Ennisvale 1

Appendix C : Native Flora Other Than Those of Conservation Significance Recorded 

in the DRP 

Family Scientific Name Common Name No. 

Records 

Dataset 

Isoetaceae Isoetes muelleri 5 MMVS(5) 

Ophioglossaceae Ophioglossum polyphyllum 2WLA 

Adiantaceae Cheilanthes sieberi subsp. sieberi 43 WLA(10), BBSPil(5), BBSSF&NR(1), 

Moree(1), NLNRVS(12), NWB(10), 

BBSpil2(2), WFS(2) 

Adiantaceae Cheilanthes lasiophylla 3WLA(2), NWB(1) 

Adiantaceae Cheilanthes distans Bristly Cloak Fern 26 WLA(10), BBSPil(3), BBSSF(1), 

NLNRVS(2), NWB(10) 

Adiantaceae Cheilanthes austrotenuifolia Rock Fern 24 WLA(12), MMVS(2), NWB(10) 

Aspleniaceae Pleurosorus rutifolius Blanket Fern 1 WLA 

Marsileaceae Marsilea hirsuta 2WLA(1), NWB(1) 

Marsileaceae Marsilea exarata 4WLA(2), NWB(2) 

Marsileaceae Marsilea drummondii Common Nardoo 1478 WLA(1146), MMVS(121), Moree(85), 

NLNRVS(7), NWB(68), WFS(1), 

Wombeira(50) 

Marsileaceae Marsilea costulifera 5 WLA(2), MMVS(1), NLNRVS(2) 

Azollaceae Azolla pinnata 1001 WLA(1000), MMVS(1) 

Azollaceae Azolla filiculoides 42 WLA (16), MMVS(15), NLNRVS(5), 

NWB(6) 

Cupressaceae Callitris gracilis subsp. murrayensis Murray Pine 1 WLA 

Cupressaceae Callitris glaucophylla White Cypress Pine 220 WLA(94), BBSPil(8), BBSSF&NR(1), 

BBSSF(1), MMVS(5), NLNRVS(20), 

NWB(87), BBSpil2(2), WFS(2) 

Cupressaceae Callitris endlicheri Black Cypress Pine 3 WLA(1), NWB(1), BBSpil2(1) 

Ranunculaceae Ranunculus undosus 80 WLA(8), MMVS(66), Moree(2), 

NWB(4) 

Ranunculaceae Ranunculus sessiliflorus 1WLA 

Ranunculaceae Ranunculus sceleratus 1 MMVS(1) 

Ranunculaceae Ranunculus pumilio 27 WLA(9), MMVS(14), NWB(1), 

Wombeira(3) 

Ranunculaceae Ranunculus pentandrus var 

pentandrus 

2WLA(1), NWB(1) 

Ranunculaceae Ranunculus pentandrus subsp. 

platycarpus 

10 WLA 

Ranunculaceae Ranunculus lappaceus Common Buttercup 2 Moree(2) 

Ranunculaceae Ranunculus inundatus 12 WLA(6), NWB(6) 

Ranunculaceae Myosurus minimus var australis Mousetail 15 WLA(9), Wombeira(6) 

Ranunculaceae Clematis microphylla var microphylla Small-leaved 

Clematia 

2WLA 

Papaveraceae Papaver aculeatum Native Poppy 1 WLA 

Portulacaceae Portulaca oleracea Pigweed 269 WLA(61), Brigfauna(1), MMVS(115), 


Namoi(3), WFS(10) 

Portulacaceae Portulaca filifolia 52 WLA(50), BBSPil(1), NLNRVS(1) 

Portulacaceae Calandrinia volubilis 2WLA 

Portulacaceae Calandrinia pumila 2 WLA(1), NLNRVS(1) 

Portulacaceae Calandrinia ptychosperma 1WLA 

Portulacaceae Calandrinia eremaea 25 WLA(7), NLNRVS(15), NWB(3) 

Portulacaceae Calandrinia balonensis 13 WLA(2), NLNRVS(11) 

Portulacaceae Anacampseros australiana 2 WLA(1), MMVS(1) 

Nyctaginaceae Boerhavia repleta Tarvine 10 Moree(9), NLNRVS(1)


Records 

Dataset 

Nyctaginaceae Boerhavia dominii Tarvine 563 WLA(353), BBSPil(5), Brigfauna(1), 

BBSSF(1), MMVS(94), Moree(77), 

NLNRVS(3), NWB(7), Namoi(3), 

WFS(15), Wombeira(4) 

Aizoaceae Zaleya galericulata subsp. 

galericulata 

3WLA 

Aizoaceae Zaleya galericulata subsp. australis 36 WLA(2), MMVS(34) 

Aizoaceae Zaleya galericulata Hogweed 23 WLA 

Aizoaceae Trianthema triquetra 97 WLA(2), MMVS(91), NLNRVS(2), 

WFS(2) 

Aizoaceae Tetragonia tetragonoides New Zealand 

Spinach 

115 WLA 

Aizoaceae Tetragonia moorei 1 BBSPil(1) 

Aizoaceae Tetragonia eremaea 1WLA 

Aizoaceae Glinus lotoides 31 WLA(23), MMVS(6), NWB(2) 

Aizoaceae Disphyma crassifolium subsp. 

clavellatum 

2WLA 

Chenopodiaceae Sclerolaena ventricosa 9WLA(8), NWB(1) 

Chenopodiaceae Sclerolaena tubata 1 Moree(1) 

Chenopodiaceae Sclerolaena tricuspis Giant Redburr 83 WLA(49), BrigOut(2), MMVS(12), 

Moree(4), NWB(14), Wombeira(2) 

Chenopodiaceae Sclerolaena tetracuspis Brigalow Burr 2 WLA(1), NWB(1) 

Chenopodiaceae Sclerolaena stelligera 61 WLA(31), MMVS(12), Moree(10), 

NWB(7), WFS(1) 

Chenopodiaceae Sclerolaena patenticuspis 23 WLA 

Chenopodiaceae Sclerolaena parviflora 1WLA 

Chenopodiaceae Sclerolaena parallelicuspis 5 NLNRVS(5) 

Chenopodiaceae Sclerolaena obliquicuspis 20 WLA 

Chenopodiaceae Sclerolaena muricata var villosa Black Rolypoly 95 WLA(7), Moree(85), NWB(2), 

Wombeira(1) 

Chenopodiaceae Sclerolaena muricata var semiglabra Black Rolypoly 44 WLA(2), Moree(41), NWB(1) 

Chenopodiaceae Sclerolaena muricata var muricata Black Rolypoly 118 WLA(50), Moree(68) 

Chenopodiaceae Sclerolaena muricata Black Rolypoly 512 WLA(183), Brigfauna(1), MMVS(140), 

NWB(152), Namoi(1), WFS(10), 

Wombeira(25) 

Chenopodiaceae Sclerolaena longicuspis 3 Moree(3) 

Chenopodiaceae Sclerolaena limbata 6 MMVS(1), Moree(4), NWB(1) 

Chenopodiaceae Sclerolaena lanicuspis Woolly Copperburr 6 WLA 

Chenopodiaceae Sclerolaena intricata 19 WLA(18), Moree(1) 

Chenopodiaceae Sclerolaena glabra 2WLA 

Chenopodiaceae Sclerolaena divaricata Tangled Copperburr 54 WLA(45), NLNRVS(1), NWB(5), 

Wombeira(3) 

Chenopodiaceae Sclerolaena diacantha Grey Copperburr 95 WLA(67), Brigfauna(1), NWB(16), 


Chenopodiaceae Sclerolaena decurrens 28 WLA(22), NLNRVS(4), NWB(2) 

Chenopodiaceae Sclerolaena cuneata 1NWB(1) 

Chenopodiaceae Sclerolaena convexula 14 WLA(2), NLNRVS(12) 

Chenopodiaceae Sclerolaena calcarata Redburr 95 WLA(39), MMVS(26), Moree(12), 

NWB(12), WFS(5), Wombeira(1) 

Chenopodiaceae Sclerolaena brachyptera 48 WLA(45), MMVS(1), NWB(1), 

Wombeira(1) 

Chenopodiaceae Sclerolaena birchii Galvinized Burr 372 WLA(155), BrigOut(1), MMVS(36), 


Namoi(1), WFS(7), Wombeira(5) 

Chenopodiaceae Sclerolaena bicornis var horrida Goathead Burr 60 WLA(29), NWB(29), Wombeira(2) 

Chenopodiaceae Sclerolaena bicornis var bicornis Goathead Burr 24 WLA(5), Moree(7), NLNRVS(5), 

NWB(7) 

Chenopodiaceae Sclerolaena bicornis Goathead Burr 77 WLA(28), BrigOut(2), MMVS(21),


Records 

Dataset 

NWB(21), WFS(5) 

Chenopodiaceae Sclerolaena anisacanthoides Yellow Burr 17 WLA(1), MMVS(8), Moree(7), 

NWB(1) 

Chenopodiaceae Scleroblitum atriplicinum Purple Goosefoot 20 WLA(14), MMVS(6) 

Chenopodiaceae Salsola tragus 308 WLA(140), Moree(28), NLNRVS(1), 

BBSPil(1), MMVS(86), NWB(47), 


Chenopodiaceae Rhagodia spinescens 376 WLA(180), BrigOut(1), MMVS(20), 

Moree(9), NWB(162), WFS(1), 

Wombeira(3) 

Chenopodiaceae Osteocarpum dipterocarpum 3 WLA(1), NLNRVS(2) 

Chenopodiaceae Osteocarpum acropterum var 

deminuta 

24 WLA(15), MMVS(8), NWB(1) 

Chenopodiaceae Osteocarpum acropterum 34 WLA(33), MMVS(1) 

Chenopodiaceae Neobassia proceriflora Soda Bush 10 WLA(8), NLNRVS(1), NWB(1) 

Chenopodiaceae Malacocera tricornis Soft Horns 10 WLA(8), MMVS(1), NWB(1) 

Chenopodiaceae Maireana tomentosa subsp. urceolata 1WLA 

Chenopodiaceae Maireana sedifolia Pearl Bluebush 6 WLA 

Chenopodiaceae Maireana sclerolaenoides 3WLA 

Chenopodiaceae Maireana pyramidata Black Bluebush 66 WLA(65), NWB(1) 

Chenopodiaceae Maireana pentatropis 3WLA 

Chenopodiaceae Maireana pentagona Hairy Bluebush 5 WLA(2), MMVS(1), NWB(2) 

Chenopodiaceae Maireana microphylla 20 WLA(8), NWB(11), BBSpil2(1) 

Chenopodiaceae Maireana lobiflora 1WLA 

Chenopodiaceae Maireana integra 2WLA 

Chenopodiaceae Maireana georgei 2WLA 

Chenopodiaceae Maireana enchylaenoides 4 WLA(1), MMVS(2), NWB(1) 

Chenopodiaceae Maireana decalvans Black Cotton Bush 127 WLA(78), MMVS(15), Moree(6), 

NWB(28) 

Chenopodiaceae Maireana coronata 27 WLA(15), MMVS(1), Moree(3), 


Wombeira(3) 

Chenopodiaceae Maireana ciliata 6 MMVS(6) 

Chenopodiaceae Maireana brevifolia 9 WLA(8), MMVS(1) 

Chenopodiaceae Maireana astrotricha Low Bluebush 2 WLA 

Chenopodiaceae Maireana appressa 8 WLA(6), NLNRVS(2) 

Chenopodiaceae Maireana aphylla Cotton Bush 96 WLA(46), MMVS(3), Moree(6), 

NWB(40), Wombeira(1) 

Chenopodiaceae Halosarcia pergranulata 1 NLNRVS(1) 

Chenopodiaceae Enchylaena tomentosa Ruby Saltbush 229 WLA(153), BBSPil(5), Brigfauna(1), 



Chenopodiaceae Einadia trigonos subsp. leiocarpa 4 Moree(4) 

Chenopodiaceae Einadia trigonos Fishweed 8 WLA(2), BBSPil(2), Moree(1), 

BBSpil2(1), Namoi(2) 

Chenopodiaceae Einadia polygonoides 46 WLA(1), Moree(44), Wombeira(1) 

Chenopodiaceae Einadia nutans subsp. nutans Climbing Saltbush 282 WLA(10), BBSPil(5), BBSSF(1), 


BBSpil2(1) 

Chenopodiaceae Einadia nutans subsp. linifolia Climbing Saltbush 18 WLA(6), BBSPil(1), Moree(5), 

NWB(6) 

Chenopodiaceae Einadia nutans subsp. eremaea 1 Moree(1) 

Chenopodiaceae Einadia nutans Climbing Saltbush 452 WLA(302), BBSSF&NR(1), 

BrigOut(2), Brigfauna(1), 

MMVS(125), NWB(2), WFS(6), 

Wombeira(13) 

Chenopodiaceae Einadia hastata Berry Saltbush 54 WLA(22), BBSSF(1), Moree(9), 

NWB(22)


Records 

Chenopodiaceae Dysphania rhadinostachya subsp. 

inflata 

Dataset 

1WLA 

Chenopodiaceae Dysphania littoralis 2WLA 

Chenopodiaceae Dysphania kalpari 2WLA 

Chenopodiaceae Dysphania glomulifera subsp. 

eremaea 

1 Moree(1) 

Chenopodiaceae Dissocarpus paradoxus Cannonball Burr 38 WLA(35), NLNRVS(3) 

Chenopodiaceae Dissocarpus biflorus var 

25 WLA(10), Moree(2), NWB(10), 

cephalocarpus 

WFS(3) 

Chenopodiaceae Dissocarpus biflorus 8 WLA(5), NWB(1), WFS(2) 

Chenopodiaceae Chenopodium truncatum 4 WLA(3), Moree(1) 

Chenopodiaceae Chenopodium pumilio Small Crumbweed 1129 WLA(1015), MMVS(100), Moree(11), 

NWB(3) 

Chenopodiaceae Chenopodium nitrariaceum Nitre Goosefoot 67 WLA(48), Moree(8), NWB(5), 


Chenopodiaceae Chenopodium melanocarpum Black Crumbweed 40 WLA(3), BBSPil(1), MMVS(14), 


Chenopodiaceae Chenopodium desertorum subsp. 

microphyllum 

Wombeira(2) 

16 WLA(11), NWB(3), Wombeira(2) 


desertorum 

5 BBSPil(1), NLNRVS(3), Namoi(1) 


anidiophyllum 

3NWB(3) 

Chenopodiaceae Chenopodium desertorum 21 WLA 

Chenopodiaceae Chenopodium curvispicatum 43 WLA(23), MMVS(3), NLNRVS(15), 


Chenopodiaceae Chenopodium cristatum Crested Goosefoot 8 WLA 

Chenopodiaceae Chenopodium auricomum 34 WLA(14), Brigfauna(2), Moree(5), 


Chenopodiaceae Atriplex vesicaria subsp. 

macrocystidia 

3 Moree(2), NLNRVS(1) 

Chenopodiaceae Atriplex vesicaria Bladder Saltbush 34 WLA(17), MMVS(2), NWB(15) 

Chenopodiaceae Atriplex velutinella 6WLA 

Chenopodiaceae Atriplex suberecta 35 WLA(17), MMVS(1), Moree(15), 


Chenopodiaceae Atriplex stipitata Mallee Saltbush 14 WLA 

Chenopodiaceae Atriplex spongiosa Pop Saltbush 9 WLA(7), NWB(2) 

Chenopodiaceae Atriplex spinibractea 3 WLA(1), Moree(2) 

Chenopodiaceae Atriplex species B 7 Moree(7) 

Chenopodiaceae Atriplex semibaccata Creeping Saltbush 54 WLA(10), MMVS(22), Moree(9), 

NWB(12), WFS(1) 

Chenopodiaceae Atriplex pseudocampanulata 56 WLA(31), MMVS(2), NWB(17), 

Wombeira(6) 

Chenopodiaceae Atriplex nummularia Old Man Saltbush 50 WLA(29), MMVS(4), NLNRVS(2), 

NWB(13), WFS(2) 

Chenopodiaceae Atriplex muelleri 135 WLA(115), Moree(14), NWB(4), 

Wombeira(2) 

Chenopodiaceae Atriplex lindleyi 42 WLA(31), BrigOut(1), MMVS(4), 

Moree(4), Wombeira(2) 

Chenopodiaceae Atriplex limbata 32 WLA(29), Wombeira(3) 

Chenopodiaceae Atriplex leptocarpa Slender-fruit 

310 WLA(190), MMVS(45), Moree(28), 

Saltbush 

NWB(43), WFS(4) 

Chenopodiaceae Atriplex holocarpa Pop Saltbush 18 WLA(13), NLNRVS(2), Wombeira(3) 

Chenopodiaceae Atriplex eardleyae 23 WLA(19), MMVS(1), Moree(2), 

WFS(1) 

Chenopodiaceae Atriplex conduplicata 18 WLA(15), MMVS(1), NWB(1), 

Wombeira(1) 

Chenopodiaceae Atriplex angulata Fan Saltbush 22 WLA


Records 

Dataset 

Amaranthaceae Ptilotus semilanatus 118 WLA(105), MMVS(1), Moree(7), 


Amaranthaceae Ptilotus polystachyus var 

polystachyus 

16 NLNRVS(16) 

Amaranthaceae Ptilotus obovatus var parviflorus 7 Moree(7) 

Amaranthaceae Ptilotus obovatus var obovatus Smoke Bush 12 WLA(3), NLNRVS(7), NWB(2) 

Amaranthaceae Ptilotus obovatus 2WFS(2) 

Amaranthaceae Ptilotus nobilis 2WLA(1), NWB(1) 

Amaranthaceae Ptilotus macrocephalus Green Pussytails 4 WLA(1), Moree(2), NWB(1) 

Amaranthaceae Ptilotus exaltatus var exaltatus Tall Mulla Mulla 24 WLA(13), Moree(1), NWB(9), WFS(1) 

Amaranthaceae Ptilotus atriplicifolius var atriplicifolius 1NWB(1) 

Amaranthaceae Amaranthus mitchellii 5 Moree(5) 

Amaranthaceae Amaranthus macrocarpus var pallidus 12 Moree(12) 

Amaranthaceae Amaranthus macrocarpus var 

macrocarpus 

21 Moree(21) 

Amaranthaceae Amaranthus macrocarpus Dwarf Amaranth 35 WLA(14), MMVS(17), NWB(3), 

Namoi(1) 

Amaranthaceae Amaranthus grandiflorus 2WLA 

Amaranthaceae Alternanthera species A 3 BBSPil(1), BBSSF(1), BBSpil2(1) 

Amaranthaceae Alternanthera nodiflora Common Joyweed 40 WLA(22), Moree(14), Namoi(1), 

Wombeira(3) 

Amaranthaceae Alternanthera nana Hairy Joyweed 30 WLA(15), MMVS(1), NWB(5), 

Wombeira(9) 

Amaranthaceae Alternanthera denticulata Lesser Joyweed 1241 WLA(1028), BrigOut(1), MMVS(131), 



Amaranthaceae Alternanthera angustifolia 2 NLNRVS(2) 

Caryophyllaceae Stellaria angustifolia Swamp Starwort 267 WLA(213), MMVS(22), Moree(5), 

NLNRVS(14), NWB(2), 

Wombeira(11) 

Caryophyllaceae Scleranthus pungens 1 MMVS(1) 

Caryophyllaceae Scleranthus minusculus 1WLA 

Caryophyllaceae Scleranthus biflorus 6 WLA(2), MMVS(2), NWB(2) 

Caryophyllaceae Polycarpaea corymbosa var minor 1 NLNRVS(1) 

Caryophyllaceae Gypsophila tubulosa 12 NLNRVS(12) 

Polygonaceae Rumex tenax Shiny Dock 6 WLA(2), Moree(3), NWB(1) 

Polygonaceae Rumex stenoglottis 2WLA(1), Namoi(1) 

Polygonaceae Rumex dumosus 23 Moree(23) 

Polygonaceae Rumex crystallinus Shiny Dock 102 WLA(30), MMVS(48), Moree(5), 


Polygonaceae Rumex brownii Swamp Dock 65 WLA(39), BBSPil(1), MMVS(13), 

Moree(2), NWB(7), Namoi(3) 

Polygonaceae Rumex bidens 1 MMVS(1) 

Polygonaceae Polygonum plebeium Small Knotweed 1014 WLA 

Polygonaceae Persicaria prostrata Creeping Knotweed 17 WLA(7), MMVS(3), NLNRVS(1), 

NWB(1), Namoi(1), Wombeira(4) 

Polygonaceae Persicaria orientalis Princes Feathers 1 WLA 

Polygonaceae Persicaria lapathifolia Pale Knotweed 1012 WLA(1009), NWB(2), Namoi(1) 

Polygonaceae Persicaria hydropiper Water Pepper 11 WLA(8), NWB(3) 

Polygonaceae Persicaria decipiens Slender Knotweed 52 WLA(4), MMVS(46), NWB(2) 

Polygonaceae Persicaria attenuata 3WLA(2), NWB(1) 

Polygonaceae Muehlenbeckia horrida 23 WLA(22), MMVS(1) 

Polygonaceae Muehlenbeckia florulenta Lignum 426 WLA(185), Brigfauna(1), MMVS(55), 



Dilleniaceae Hibbertia obtusifolia 2 BBSSF&NR(1), BBSpil2(1)


Records 

Dataset 

Sterculiaceae Melhania oblongifolia 1 NLNRVS(1) 

Sterculiaceae Lasiopetalum baueri 4WLA(2), NWB(2) 

Sterculiaceae Brachychiton populneus Kurrajong 11 WLA(6), MMVS(2), NWB(3) 

Malvaceae Sida trichopoda 196 WLA(113), MMVS(21), Moree(50), 


Malvaceae Sida spinosa 2WLA(1), Namoi(1) 

Malvaceae Sida species B 1 Moree(1) 

Malvaceae Sida species A 10 NLNRVS(6), NWB(2) 

Malvaceae Sida pleiantha 4 WLA(2), Wombeira(2) 

Malvaceae Sida phaeotricha 4 WLA(2), Wombeira(2) 

Malvaceae Sida petrophila 2WLA 

Malvaceae Sida intricata 25 WLA(24), NWB(1) 

Malvaceae Sida goniocarpa 1WLA 

Malvaceae Sida filiformis 22 WLA(12), NWB(5), Wombeira(5) 

Malvaceae Sida fibulifera 50 WLA(5), MMVS(40), NWB(4), 

WFS(1) 

Malvaceae Sida cunninghamii 36 WLA(8), BBSPil(2), MMVS(4), 


BBSpil2(1) 

Malvaceae Sida corrugata 108 WLA(64), MMVS(19), Moree(10), 


Malvaceae Sida ammophila 5 Moree(1), NLNRVS(4) 

Malvaceae Malva australiana Native Hollyhock 6 WLA 

Malvaceae Hibiscus trionum Bladder Ketmia 151 WLA(120), MMVS(3), Moree(28) 

Malvaceae Hibiscus sturtii var sturtii 6 Moree(2), NLNRVS(4) 

Malvaceae Hibiscus sturtii Hill Hibiscus 11 WLA(5), BBSPil(1), NWB(5) 

Malvaceae Hibiscus krichauffianus Velvet-leaf Hibiscus 1 WLA 

Malvaceae Hibiscus brachysiphonius 18 WLA(5), Moree(9), NWB(2), 

Wombeira(2) 

Malvaceae Abutilon oxycarpum var subsagittatum Flannel Weed 1 WLA 

Malvaceae Abutilon oxycarpum Flannel Weed 195 WLA(144), BBSPil(1), BBSSF(1), 


Malvaceae Abutilon otocarpum 3 MMVS(1), WFS(2) 

Malvaceae Abutilon malvifolium 6 WLA(1), MMVS(5) 

Malvaceae Abutilon leucopetalum 13 WLA(5), NLNRVS(4), NWB(4) 

Malvaceae Abutilon fraseri 16 WLA(6), MMVS(1), NLNRVS(5), 

NWB(4) 

Urticaceae Urtica incisa Stinging Nettle 3 WLA(2), NWB(1) 

Urticaceae Parietaria debilis 1 MMVS(1) 

Rhamnaceae Ventilago viminalis Supple Jack 23 WLA(12), MMVS(2), NLNRVS(1), 

NWB(8) 

Thymelaeaceae Pimelea trichostachya 30 WLA(8), Moree(1), NLNRVS(21) 

Thymelaeaceae Pimelea trichostachya 22 Moree(1), NLNRVS(21) 

Thymelaeaceae Pimelea simplex subsp. continua 1WLA 

Thymelaeaceae Pimelea simplex 28 WLA(24), Wombeira(4) 

Thymelaeaceae Pimelea penicillaris 9WLA(7), NWB(2) 

Thymelaeaceae Pimelea pauciflora 2NWB(2) 

Thymelaeaceae Pimelea neo-anglica 2WLA 

Thymelaeaceae Pimelea microcephala subsp. 

microcephala 

Thymelaeaceae Pimelea linifolia subsp. linifolia 3 BBSPil(3) 

76 WLA(35), MMVS(5), Moree(1), 

NLNRVS(8), NWB(25), WFS(2) 

Thymelaeaceae Pimelea linifolia 5 WLA(2), NWB(2), BBSpil2(1) 

Euphorbiaceae Sauropus trachyspermus 1 Moree(1) 

Euphorbiaceae Poranthera microphylla 5 NLNRVS(5)


Records 

Dataset 

Euphorbiaceae Phyllanthus virgatus 37 WLA(11), BBSPil(3), BBSSF(1), 

MMVS(1), Moree(19), NLNRVS(1), 

BBSpil2(1) 

Euphorbiaceae Phyllanthus lacunellus 25 WLA 

Euphorbiaceae Petalostigma pubescens Bitter Bark 19 WLA(9), NWB(10) 

Euphorbiaceae Euphorbia stevenii Bottle-tree Spurge 1 WLA 

Euphorbiaceae Euphorbia planiticola 19 MMVS(3), Moree(16) 

Euphorbiaceae Euphorbia eremophila Desert Spurge 2 WLA 

Euphorbiaceae Croton phebalioides 3WLA 

Euphorbiaceae Chamaesyce species B 1 Moree(1) 

Euphorbiaceae Chamaesyce drummondii Caustic Weed 293 WLA(68), BBSPil(4), Brigfauna(1), 


NLNRVS(10), NWB(19), BBSpil2(1), 


Euphorbiaceae Chamaesyce dallachyana 102 WLA(101), Namoi(1) 

Euphorbiaceae Chamaesyce australis 2 WLA(1), Wombeira(1) 

Euphorbiaceae Adriana tomentosa var tomentosa 2WLA(1), Namoi(1) 

Violaceae Hybanthus monopetalus 1 NLNRVS(1) 

Cucurbitaceae Zehneria micrantha Desert Cucumber 7 WLA 

Cucurbitaceae Cucumis melo subsp. agrestis 1 Moree(1) 

Frankeniaceae Frankenia uncinata 1WLA 

Frankeniaceae Frankenia serpyllifolia 1WLA 

Frankeniaceae Frankenia connata 4WLA 

Capparaceae Capparis mitchellii Native Orange 172 WLA(85), MMVS(6), Moree(7), 

NWB(73), WFS(1) 

Capparaceae Capparis lasiantha Nepine 306 WLA(246), BBSPil(2), MMVS(4), 

Moree(3), NWB(45), WFS(6) 

Capparaceae Apophyllum anomalum Warrior Bush 157 WLA(77), BBSPil(1), BrigOut(1), 

MMVS(5), Moree(1), NWB(71), 

WFS(1) 

Brassicaceae Stenopetalum sphaerocarpum 1 Moree(1) 

Brassicaceae Stenopetalum lineare 5WLA 

Brassicaceae Sisymbrium erysimoides Smooth Mustard 55 WLA(54), NWB(1) 

Brassicaceae Rorippa laciniata 2WLA 

Brassicaceae Rorippa eustylis 72 WLA(2), MMVS(64), Moree(3), 

NLNRVS(3) 

Brassicaceae Phlegmatospermum cochlearinum Oval-podded Cress 14 WLA 

Brassicaceae Lepidium sagittulatum 18 WLA(8), Moree(4), NLNRVS(1), 

NWB(5) 

Brassicaceae Lepidium pseudohyssopifolium Peppercress 60 WLA(43), BBSPil(2), Moree(2), 


Brassicaceae Lepidium phlebopetalum Veined 

Peppercress 

2WLA 

Brassicaceae Lepidium papillosum Warty Peppercess 1 WLA 

Brassicaceae Lepidium oxytrichum 2WLA 

Brassicaceae Lepidium hypenantion 2 Moree(2) 

Brassicaceae Lepidium fasciculatum 39 WLA(17), MMVS(3), Moree(8), 

NWB(11) 

Brassicaceae Harmsiodoxa puberula 2WLA 

Brassicaceae Harmsiodoxa brevipes var major 2 NLNRVS(2) 

Brassicaceae Harmsiodoxa brevipes var brevipes 2WLA(1), NWB(1) 

Brassicaceae Harmsiodoxa brevipes 3WLA 

Brassicaceae Harmsiodoxa blennodioides 6 WLA(5), Moree(1) 

Brassicaceae Cuphonotus andraeanus 8WLA 

Brassicaceae Blennodia canescens Wild Stock 2 WLA 

Brassicaceae Arabidella trisecta 7WLA(6), NWB(1) 

Brassicaceae Arabidella procumbens 2WLA


Records 

Dataset 

Brassicaceae Arabidella nasturtium 3WLA 

Brassicaceae Arabidella eremigena 1WLA 

Gyrostemonaceae Gyrostemon australasicus 1WLA 

Clusiaceae Hypericum gramineum Small St John's 

Wort 

7 BBSPil(2), Moree(1), NLNRVS(4) 

Droseraceae Drosera peltata 1 NLNRVS(1) 

Droseraceae Drosera indica Sundew 1 WLA 

Casuarinaceae Casuarina pauper Belah 8 WLA 

Casuarinaceae Casuarina cristata Belah 291 WLA(143), BBSPil(1), MMVS(8), 

Moree(2), NWB(135), WFS(2) 

Casuarinaceae Allocasuarina verticillata Drooping Sheoak 1 WLA 

Casuarinaceae Allocasuarina luehmannii Bulloak 58 WLA(25), BBSPil(4), BBSSF&NR(1), 

BBSSF(1), MMVS(1), NWB(24), 

BBSpil2(2) 

Casuarinaceae Allocasuarina diminuta subsp. 

diminuta 

1 BBSpil2(1) 

Crassulaceae Crassula sieberiana Australian 

Stonecrop 

14 WLA(1), NLNRVS(13) 

Crassulaceae Crassula decumbens var decumbens 1WLA 

Crassulaceae Crassula colorata 35 WLA(33), BrigOut(1), NWB(1) 

Proteaceae Persoonia sericea 2WLA(1), NWB(1) 

Proteaceae Hakea tephrosperma Hooked 

Needlewood 

6WLA(5), NWB(1) 

Proteaceae Hakea leucoptera Needlewood 122 WLA(113), BBSPil(1), NLNRVS(1), 

NWB(7) 

Proteaceae Hakea decurrens 2 NLNRVS(2) 

Proteaceae Grevillea striata Beefwood 28 WLA(22), NLNRVS(2), NWB(4) 

Proteaceae Grevillea floribunda subsp floribunda Seven Dwarfs 

Grevillea 

Proteaceae Grevillea albiflora 2WLA 

Myrtaceae Micromyrtus hexamera 4WLA 

2 WLA(1), BBSpil2(1) 

Myrtaceae Micromyrtus ciliata 4WLA(2), NWB(2) 

Myrtaceae Melaleuca uncinata Broombush 1 WLA 

Myrtaceae Melaleuca trichostachya 19 WLA(16), NWB(1), Wombeira(2) 

Myrtaceae Melaleuca densispicata 2WLA(1), NWB(1) 

Myrtaceae Melaleuca bracteata 6WLA(3), NWB(3) 

Myrtaceae Melaleuca armillaris 1WLA 

Myrtaceae Leptospermum polygalifolium 2WLA(1), NWB(1) 

Myrtaceae Eucalyptus viridis Green Mallee 1 WLA 

Myrtaceae Eucalyptus socialis Red Mallee 3 WLA 

Myrtaceae Eucalyptus sideroxylon Mugga Ironbark 2 WLA 

Myrtaceae Eucalyptus populnea subsp. bimbil Bimble Box 551 WLA(311), BBSPil(2), MMVS(27), 


WFS(5) 

Myrtaceae Eucalyptus pilligaensis Narrow-leaved Grey 

Box 

7 WLA(2), BBSPil(2), NWB(2), 

BBSpil2(1) 

Myrtaceae Eucalyptus microcarpa Western Grey Box 25 WLA(12), BBSSF(1), NWB(11), 

WFS(1) 

Myrtaceae Eucalyptus melliodora Yellow Box 19 WLA(10), NWB(9) 

Myrtaceae Eucalyptus melanophloia Silver-leaved 

Ironbark 

18 WLA(8), NLNRVS(4), NWB(6) 

Myrtaceae Eucalyptus largiflorens Black Box 290 WLA(154), MMVS(29), Moree(7), 


Myrtaceae Eucalyptus dwyeri Dwyer's Red Gum 4 WLA(2), NWB(2) 

Myrtaceae Eucalyptus dumosa White Mallee 1 WLA 

Myrtaceae Eucalyptus dealbata Tumbledown Red 

Gum 

11 WLA(6), NWB(5)


Records 

Myrtaceae Eucalyptus crebra Narrow-leaved 

Ironbark 

Dataset 

11 WLA(4), BBSPil(1), BBSSF(1), 

NWB(4), BBSpil2(1) 

Myrtaceae Eucalyptus coolabah Coolibah 2445 WLA(2207), Brigfauna(1), MMVS(30), 



Myrtaceae Eucalyptus conica 1 BBSpil2(1) 

Myrtaceae Eucalyptus chloroclada Dirty Gum 27 WLA(11), BBSPil(4), MMVS(1), 

NWB(11) 

Myrtaceae Eucalyptus camaldulensis River Red Gum 513 WLA(334), MMVS(91), NLNRVS(5), 

NWB(73), Namoi(2), WFS(6), 

Wombeira(2) 

Myrtaceae Eucalyptus blakelyi Blakely's Red Gum 6 WLA(2), BBSPil(1), BBSSF&NR(1), 


Myrtaceae Corymbia tumescens 2WLA 

Myrtaceae Corymbia trachyphloia White Bloodwood 1 WLA 

Myrtaceae Corymbia tessellaris Carbeen 52 WLA(33), NWB(14), WFS(5) 

Myrtaceae Corymbia dolichocarpa Long-fruited 

Bloodwood 

32 WLA(21), NWB(11) 

Myrtaceae Calytrix tetragona 1 BBSpil2(1) 

Myrtaceae Calytrix longiflora 3WLA 

Myrtaceae Callistemon viminalis Weeping 

Bottlebrush 

Myrtaceae Callistemon linearis Narrow-leaved 

Bottlebrush 

1WLA 

2WLA(1), NWB(1) 

Myrtaceae Angophora melanoxylon 22 WLA(20), NLNRVS(2) 

Myrtaceae Angophora leiocarpa 1NWB(1) 

Myrtaceae Angophora floribunda Rough-barked 

Apple 

Myrtaceae Angophora costata Sydney Red/Rusty 

Gum 

4 WLA(2), BBSpil2(1), Namoi(1) 

1WLA 

Lythraceae Lythrum salicaria Purple Loosestrife 100 WLA 

Lythraceae Lythrum hyssopifolia Hyssop Loosestrife 11 WLA (2), MMVS (8), Wombeira (1) 

Lythraceae Ammannia multiflora Jerry-jerry 11 WLA 

Onagraceae Epilobium hirtigerum Willowherb 7 WLA(5), MMVS(2) 

Haloragaceae Myriophyllum verrucosum Red Water-milfoil 10 WLA(7), NLNRVS(2), Wombeira(1) 

Haloragaceae Myriophyllum striatum 1WLA 

Haloragaceae Myriophyllum simulans 2WLA 

Haloragaceae Myriophyllum propinquum 16 MMVS(14), NWB(2) 

Haloragaceae Haloragis odontocarpa 2 Moree(2) 

Haloragaceae Haloragis heterophylla 7 WLA(1), MMVS(5), WFS(1) 

Haloragaceae Haloragis glauca forma glauca 105 WLA(47), MMVS(7), Moree(6), 


Wombeira(35) 

Haloragaceae Haloragis aspera 7 WLA(2), MMVS(3), NLNRVS(1), 

NWB(1) 

Haloragaceae Gonocarpus elatus 1WLA 

Rutaceae Geijera parviflora Wilga 423 WLA(193), BBSPil(5), BBSSF(1), 



Rutaceae Phebalium squamulosum Scaly Phebalium 1 WLA 

Rutaceae Phebalium glandulosum Desert Phebalium 1 WLA 

Rutaceae Flindersia maculosa Leopardwood 54 WLA(25), BBSPil(1), BrigOut(1), 

MMVS(7), NLNRVS(3), NWB(17) 

Rutaceae Citrus glauca Desert Lime 9 WLA(6), NWB(3) 

Meliaceae Owenia acidula Gruie 24 WLA(19), NLNRVS(1), NWB(4) 

Sapindaceae Dodonaea viscosa subsp. spatulata 3 BBSPil(2), BBSpil2(1)


Records 

Dataset 

Sapindaceae Dodonaea viscosa subsp. mucronata Hop Bush 2 WLA(1), NWB(1) 

Sapindaceae Dodonaea viscosa subsp. cuneata Hop Bush 1 WLA 

Sapindaceae Dodonaea viscosa subsp. 

angustissima 

Hop Bush 33 WLA(30), NWB(3) 

Sapindaceae Dodonaea viscosa Hop Bush 27 WLA(11), MMVS(1), NLNRVS(6), 

NWB(9) 

Sapindaceae Dodonaea peduncularis 1 BBSpil2(1) 

Sapindaceae Atalaya hemiglauca Whitewood 164 WLA(88), MMVS(9), Moree(1), 


Wombeira(4) 

Sapindaceae Alectryon oleifolius subsp. elongatus Western 

Rosewood, 

Bonaree 

1WLA 

Sapindaceae Alectryon oleifolius subsp. canescens Western 

Rosewood, 

Bonaree 

10 WLA(9), Moree(1) 

Sapindaceae 

Fabaceae 

(Caesalpinioideae) 

Alectryon oleifolius Western 

Rosewood, 

Bonaree 

Fabaceae 


Fabaceae 


Fabaceae 


Fabaceae 


Fabaceae 


Fabaceae 


Fabaceae 


Fabaceae 


Fabaceae 


Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

254 WLA(121), MMVS(17), NWB(107), 


Senna form taxon 'zygophylla' 7 WLA(2), BBSPil(3), NWB(2) 

Senna form taxon 'petiolaris' Woody Cassia 8 WLA 

Senna form taxon 'filifolia' Silver Cassia 11 WLA(9), NWB(2) 

Senna circinnata Silver Cassia 9 WLA(6), NWB(3) 

Senna form taxon 'sturtii' Grey Cassia 2 WLA 

Senna form taxon 'coriacea' Silver Cassia 7 WLA 

Senna form taxon 'artemisioides' Silver Cassia 9 WLA(6), NWB(3) 

Senna artemisioides Silver Cassia 5 WLA(4), NWB(1) 

Petalostylis labicheoides var 

labicheoides 

Butterfly Bush 1 WLA 

Lysiphyllum gilvum 1WLA 

Trigonella suavissima Coopers Clover 61 WLA(33), NWB(1), Wombeira(27) 

Tephrosia sphaerospora 5 NLNRVS(5) 

Templetonia egena Desert Broombush 1 WLA 

Swainsona swainsonioides 52 WLA(45), MMVS(3), Moree(1), 

NLNRVS(1), Wombeira(2) 

Swainsona stipularis 1WLA 

Swainsona similis 2WLA 

Swainsona purpurea 5WLA 

Swainsona procumbens Broughton Pea 112 WLA(111), Wombeira(1) 

Swainsona phacoides 10 WLA(8), NWB(1), Wombeira(1) 

Swainsona oligophylla 1WLA 

Swainsona monticola 2WLA


Records 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Dataset 

Swainsona microphylla 3WLA(2), WFS(1) 

Swainsona luteola 21 WLA 

Swainsona greyana Darling Pea 33 WLA(29), NWB(4) 

Swainsona galegifolia Smooth Darling Pea 6 WLA(3), NWB(3) 

Swainsona campylantha 2WLA 

Swainsona affinis 3WLA 

Sesbania cannabina var cannabina Sesbania Pea 29 WLA(9), MMVS(13), Moree(1), 


Rhynchosia minima Ryncho 17 WLA(4), MMVS(1), Moree(10), 

NWB(2) 

Ptychosema anomalum 2WLA 

Muelleranthus stipularis Sand Pea 2 WLA(1), NLNRVS(1) 

Millotia greevesii subsp glandulosa 3 NLNRVS(3) 

Melilotus indicus 8 MMVS(8) 

Lotus cruentus Red-flowered Lotus 32 WLA 

Kennedia procurrens Purple Running Pea 5 WLA(2), NLNRVS(3) 

Indigofera linnaei Birdsville Indigo 1 WLA 

Indigofera coronillifolia 2WLA(1), NWB(1) 

Indigofera colutea Sticky Indigo 2 WLA(1), NWB(1) 

Indigofera brevidens 2WLA 

Indigofera australis 8 WLA(3), MMVS(2), NWB(3) 

Glycyrrhiza acanthocarpa Native Liquorice 27 WLA(25), NWB(2) 

Glycine tomentella Woolly Glycine 4 WLA(2), NWB(2) 

Glycine tabacina 21 WLA(7), BBSPil(4), BBSSF&NR(1), 

BBSSF(1), Moree(1), NWB(7) 

Glycine latifolia 1 Moree(1) 

Glycine clandestina Twining Glycine 29 WLA(9), MMVS(7), Moree(2), 

NLNRVS(3), NWB(7), Namoi(1) 

Glycine canescens Silky Glycine 21 WLA(6), BBSPil(2), BBSSF(1), 


Desmodium varians Slender Tick-trefoil 1 BBSSF(1) 

Desmodium brachypodum Large Tick-trefoil 3 BBSPil(3) 

Daviesia genistifolia 1 BBSpil2(1) 

Cullen tenax Emu-foot 215 WLA(166), MMVS(6), Moree(33), 

Namoi(1), Wombeira(9) 

Fabaceae 

(Faboideae) 

Cullen patens 1WLA 

Fabaceae 

(Faboideae) 

Cullen pallidum 14 WLA 

Fabaceae 

(Faboideae) 

Cullen cinereum Annual Verbine 6 WLA(5), MMVS(1) 

Fabaceae Crotalaria dissitiflora subsp. Grey Rattlepod 3 WLA(1), Moree(2)


Records 

(Faboideae) dissitiflora 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Fabaceae 

(Mimosoideae) 

Dataset 

Bossiaea walkeri Cactus Pea 1 WLA 

Aotus mollis 1 BBSpil2(1) 

Aeschynomene indica Budda Pea 1019 WLA(1002), MMVS(16), NLNRVS(1) 

Neptunia gracilis forma gracilis Sensitive Plant 156 WLA(105), MMVS(1), Moree(50) 

Acacia victoriae subsp. victoriae Prickly Wattle 24 WLA 

Acacia victoriae Prickly Wattle 8 WLA(6), NWB(1), Wombeira(1) 

Acacia triptera Spurwing Wattle 1 WLA 

Acacia tetragonophylla Dead Finish 1 WLA 

Acacia stenophylla River Cooba 279 WLA(133), MMVS(33), Moree(6), 


Wombeira(38) 

Acacia spectabilis Mudgee Wattle 3 WLA(1), BBSSF&NR(1), BBSpil2(1) 

Acacia salicina Cooba 74 WLA(38), MMVS(7), NWB(27), 

Namoi(2) 

Acacia rigens Needle Wattle 2 WLA 

Acacia pycnantha Golden Wattle 2 WLA(1), NWB(1) 

Acacia polybotrya 1 BBSpil2(1) 

Acacia penninervis Mountain Hickory 2 WLA(1), NWB(1) 

Acacia pendula Boree 99 WLA(45), MMVS(8), Moree(3), 


Acacia paradoxa 1 MMVS(1) 

Acacia oswaldii Miljee 45 WLA(25), MMVS(7), NLNRVS(1), 


Acacia murrayana 6 WLA(2), NLNRVS(2), NWB(1), 

Wombeira(1) 

Acacia loderi Nealie 8 WLA 

Acacia ligulata Umbrella Bush 11 WLA 

Acacia leptoclada 2WLA(1), NWB(1) 

Acacia jennerae Coonavittra Wattle 1 WLA 

Acacia ixiophylla 1 BBSPil(1) 

Acacia homalophylla Yarran 13 WLA(7), BBSPil(1), NLNRVS(1), 

NWB(4) 

Acacia harpophylla Brigalow 24 WLA(13), BrigOut(2), NWB(9) 

Acacia hakeoides Hakea Wattle 2 WLA(1), NWB(1) 

Acacia flexifolia 2WLA(1), NWB(1) 

Acacia filicifolia Fern-leaved Wattle 8 WLA(4), NWB(4) 

Acacia excelsa Ironwood 34 WLA(19), MMVS(1), NLNRVS(1), 

NWB(13) 

Acacia doratoxylon Currawang 10 WLA(6), NWB(4) 

Acacia decora Western Golden 

Wattle 

4WLA(3), NWB(1)


Records 

Dataset 

Fabaceae 

(Mimosoideae) 

Acacia deanei subsp deanei 2 WLA (1), NWB(1) 

Fabaceae 

(Mimosoideae) 

Acacia deanei subsp. paucijuga 3 BBSSF(1), BBSpil2(2) 

Fabaceae 

Acacia deanei Green Wattle 28 WLA(11), BBSPil(5), BBSSF&NR(1), 

(Mimosoideae) 

NWB(11) 

Fabaceae 

(Mimosoideae) 

Acacia coriacea subsp sericophylla Wirewood 8 WLA(4), Moree(4) 

Fabaceae 

(Mimosoideae) 

Acacia colletioides Wait-a-while 2 WLA(1), NWB(1) 

Fabaceae 

(Mimosoideae) 

Acacia caroleae 1 BBSpil2(1) 

Fabaceae 

Acacia cambagei Gidgee 13 WLA(6), BrigOut(1), Brigfauna(2), 

(Mimosoideae) 

Wombeira(4) 

Fabaceae 

(Mimosoideae) 

Acacia buxifolia subsp. buxifolia Box-leaved Wattle 1 WLA 

Fabaceae 

(Mimosoideae) 

Acacia brachystachya 4 NLNRVS(4) 

Fabaceae 

(Mimosoideae) 

Acacia brachybotrya Grey Mulga 1 WLA 

Fabaceae 

(Mimosoideae) 

Acacia aneura Mulga 14 WLA(10), NLNRVS(4) 

Fabaceae 

(Mimosoideae) 

Acacia acuminata subsp burkittii Sandhill Wattle 1 NLNRVS(1) 

Zygophyllaceae Zygophyllum simile 1WLA 

Zygophyllaceae Zygophyllum ovatum Dwarf Twinleaf 1 WLA 

Zygophyllaceae Zygophyllum iodocarpum Violet Twinleaf 10 WLA(9), Moree(1) 

Zygophyllaceae Zygophyllum glaucum 21 MMVS(21) 

Zygophyllaceae Zygophyllum eremaeum Climbing Twinleaf 2 WLA 

Zygophyllaceae Zygophyllum aurantiacum Shrubby Twinleaf 1 WLA 

Zygophyllaceae Zygophyllum apiculatum Gallweed, Pointed 

or Common 

Twinleaf 

3WLA(2), NWB(1) 

Zygophyllaceae Zygophyllum ammophilum Sand Twinleaf 8 WLA(5), Wombeira(3) 

Zygophyllaceae Tribulus micrococcus Yellow Vine, 

Spineless Caltrop 

Nitrariaceae Nitraria billardierei Dillon Bush 4 WLA 

Linaceae Linum marginale Native Flax 1 WLA 

Oxalidaceae Oxalis radicosa 13 Moree(13) 

19 WLA(1), Moree(17), Namoi(1) 

Oxalidaceae Oxalis perennans Wood Sorrel 97 WLA(21), BBSPil(5), BBSSF(1), 


NWB(1), BBSpil2(1), Namoi(3) 

Oxalidaceae Oxalis chnoodes 165 Moree(13), NLNRVS(20), NWB(132) 

Geraniaceae Pelargonium australe Native Storksbill 6 WLA(3), NWB(3) 

Geraniaceae Geranium solanderi var solanderi Native Geranium 11 WLA(3), Moree(4), NWB(4) 

Geraniaceae Geranium solanderi Native Geranium 2 WLA 

Geraniaceae Erodium cicutarium Common Crowfoot 9 WLA 

Geraniaceae Erodium cygnorum subsp. 

glandulosum 


Geraniaceae Erodium crinitum Blue Storksbill 56 WLA(14), MMVS(32), Moree(7), 


Celastraceae Maytenus cunninghamii Yellow-berry Bush 10 WLA(2), BBSPil(5), BBSSF(1), 

NWB(2) 

Celastraceae Cassine australis var angustifolia Red Olive Plum 6 WLA(3), NWB(3) 

Stackhousiaceae Stackhousia viminea Slender 

Stackhousia 

5 WLA(2), Moree(1), NWB(2) 

Stackhousiaceae Stackhousia muricata 4 BBSPil(2), Moree(1), BBSpil2(1) 

Stackhousiaceae Stackhousia monogyna Creamy Candles 3 WLA(2), NWB(1) 

Olacaceae Olax stricta 2WLA(1), NWB(1)


Records 

Dataset 

Oleaceae Jasminum lineare Desert Jasmine 66 WLA(28), BBSPil(4), MMVS(7), 


Loranthaceae Lysiana subfalcata 4 WLA(2), MMVS(1), NWB(1) 

Loranthaceae Lysiana murrayi 1WLA 

Loranthaceae Lysiana linearifolia 6WLA(3), NWB(3) 

Loranthaceae Lysiana exocarpi subsp. tenuis 7 WLA(3), BBSSF(1), NWB(3) 

Loranthaceae Lysiana exocarpi subsp. exocarpi 8WLA(5), NWB(3) 

Loranthaceae Lysiana exocarpi 28 WLA(17), NWB(11) 

Loranthaceae Diplatia grandibractea 6 WLA(5), Wombeira(1) 

Loranthaceae Dendrophthoe glabrescens 6WLA(4), NWB(2) 

Loranthaceae Amyema quandang var quandang 7 WLA(3), MMVS(1), NWB(2), 

Wombeira(1) 

Loranthaceae Amyema quandang var bancroftii 3WLA 

Loranthaceae Amyema quandang 16 WLA(8), NWB(8) 

Loranthaceae Amyema preissii 2WLA(1), NWB(1) 

Loranthaceae Amyema pendulum subsp. longifolium 3WLA(2), NWB(1) 

Loranthaceae Amyema miraculosum subsp. 

boormanii 

56 WLA(36), BBSPil(4), BrigOut(1), 

MMVS(1), NWB(10), Wombeira(4) 

Loranthaceae Amyema miquelii 85 WLA(49), MMVS(6), NWB(21), 

BBSpil2(1), Wombeira(8) 

Loranthaceae Amyema maidenii subsp. maidenii 2WLA(1), NWB(1) 

Loranthaceae Amyema maidenii subsp. 

angustifolium 

1WLA 

Loranthaceae Amyema maidenii 4WLA(2), NWB(2) 

Loranthaceae Amyema lucasii 3 WLA(1), MMVS(2) 

Loranthaceae Amyema linophyllum subsp. orientale 12 WLA(6), BBSPil(1), BBSSF(1), 

NWB(4) 

Loranthaceae Amyema gaudichaudii 2 MMVS(2) 

Loranthaceae Amyema cambagei 6WLA(2), NWB(4) 

Santalaceae Santalum lanceolatum Northern 

Sandalwood 

12 WLA(7), NLNRVS(1), NWB(4) 

Santalaceae Santalum acuminatum Sweet Quandong 8 WLA(5), BBSPil(1), NWB(2) 

Santalaceae Exocarpos cupressiformis Native Cherry 1 NLNRVS(1) 

Santalaceae Exocarpos aphyllus Leafless Ballart 16 WLA(9), BBSPil(1), NWB(6) 

Pittosporaceae Pittosporum angustifolium Butterbush 46 WLA (28), NLNRVS(2), NWB(16) 

Pittosporaceae Bursaria spinosa Native Blackthorn 8 WLA(4), NWB(4) 

Apiaceae Trachymene ochracea White Parsnip 10 WLA(4), NLNRVS(6) 

Apiaceae Trachymene incisa subsp. corrugata 4WLA(2), NWB(2) 

Apiaceae Platysace ericoides 4 WLA(1), BBSSF&NR(1), NWB(1), 

BBSpil2(1) 

Apiaceae Hydrocotyle laxiflora Stinking Pennywort 1 WLA 

Apiaceae Eryngium plantagineum Long Eryngium 31 WLA(16), NWB(1), Wombeira(14) 

Apiaceae Eryngium paludosum 3 Moree(3) 

Apiaceae Daucus glochidiatus Native Carrot 90 WLA(36), BBSPil(1), MMVS(4), 



Apiaceae Actinotus gibbonsii 9 NLNRVS(8), BBSpil2(1) 

Campanulaceae Wahlenbergia tumidifructa 4WLA 

Campanulaceae Wahlenbergia stricta subsp. stricta 1 BBSPil(1) 

Campanulaceae Wahlenbergia stricta subsp. alterna 20 BBSPil(3), NLNRVS(17) 

Campanulaceae Wahlenbergia stricta Tall Bluebell 73 WLA(39), NWB(5), WFS(1), 

Wombeira(28) 

Campanulaceae Wahlenbergia queenslandica 11 WLA(6), NWB(5) 

Campanulaceae Wahlenbergia planiflora subsp. 

planiflora 

2WLA(1), NWB(1) 

Campanulaceae Wahlenbergia planiflora subsp. 6 BBSPil(6)


Records 

longipila 

Dataset 

Campanulaceae Wahlenbergia luteola 3 WLA(1), Moree(1), NWB(1) 

Campanulaceae Wahlenbergia graniticola Granite Bluebell 4 WLA(3), NLNRVS(1) 

Campanulaceae Wahlenbergia gracilis Sprawling or 

Australian Bluebell 

1 Moree(1) 

Campanulaceae Wahlenbergia gracilenta Annual Bluebell 7 WLA(6), BBSSF&NR(1) 

Campanulaceae Wahlenbergia fluminalis River Bluebell 36 WLA(21), Moree(2), NLNRVS(7), 

NWB(6) 

Campanulaceae Wahlenbergia communis Tufted Bluebell 38 WLA(13), BBSPil(2), MMVS(2), 

Moree(13), NWB(8) 

Campanulaceae Wahlenbergia aridicola 2WLA(1), NWB(1) 

Lobeliaceae Pratia purpurascens Whiteroot 6 WLA(3), Wombeira(3) 

Lobeliaceae Pratia darlingensis Darling Pratia 3 WLA(2), NWB(1) 

Lobeliaceae Pratia concolor Poison Pratia 148 WLA(25), MMVS(87), Moree(16), 

NLNRVS(1), NWB(15), Wombeira(4) 

Lobeliaceae Isotoma axillaris Showy Isotome 4 WLA(2), NWB(2) 

Asteraceae Vittadinia triloba 5WFS(5) 

Asteraceae Vittadinia sulcata 17 WLA(1), BBSPil(3), BBSSF(1), 

Moree(5), NLNRVS(5), BBSpil2(1), 

Namoi(1) 

Asteraceae Vittadinia pustulata 1 NLNRVS(1) 

Asteraceae Vittadinia pterochaeta Rough Fuzzweed 57 WLA(5), MMVS(26), Moree(21), 


Asteraceae Vittadinia hispidula 1NWB(1) 

Asteraceae Vittadinia dissecta var hirta 10 WLA(3), BBSPil(1), BBSSF(1), 


Asteraceae Vittadinia dissecta var dissecta 1WLA 

Asteraceae Vittadinia cuneata var cuneata Fuzzweed 2 WLA(1), NWB(1) 

Asteraceae Vittadinia cuneata Fuzzweed 276 WLA(255), BBSPil(2), 

BBSSF&NR(1), MMVS(4), Moree(7), 


Asteraceae Vittadinia cervicularis var cervicularis 2 BBSPil(2) 

Asteraceae Vittadinia cervicularis 2 NLNRVS(2) 

Asteraceae Vernonia cinerea var cinerea 2 BBSPil(2) 

Asteraceae Triptilodiscus pygmaeus 5WLA(4), NWB(1) 

Asteraceae Stuartina muelleri Spoon Cudweed 7 WLA(1), BrigOut(1), NLNRVS(5) 

Asteraceae Stuartina hamata Hooked Cudweed 2 WLA 

Asteraceae Solenogyne dominii 4WLA(2), NWB(2) 

Asteraceae Sigesbeckia orientalis subsp. 

orientalis 

Indian Weed 4 WLA(2), NLNRVS(2) 

Asteraceae Senecio runcinifolius Tall Groundsel 57 WLA(32), MMVS(6), Moree(1), 


Asteraceae Senecio quadridentatus Cotton Fireweed 75 WLA(53), MMVS(1), Moree(1), 


Asteraceae Senecio platylepis 1WLA 

Asteraceae Senecio murrayanus 3WLA 

Asteraceae Senecio lautus subsp. lautus Variable Groundsel 2 WLA 

Asteraceae Senecio lautus subsp. dissectifolius Variable Groundsel 9 WLA(6), MMVS(3) 

Asteraceae Senecio lautus Variable Groundsel 5 WLA(4), BBSPil(1) 

Asteraceae Senecio hispidulus var dissectus Hill Fireweed 1 WLA 

Asteraceae Senecio gregorii 1WLA 

Asteraceae Senecio glossanthus 27 WLA 

Asteraceae Senecio daltonii 1WLA 

Asteraceae Senecio cunninghamii var serratus 7WLA 

Asteraceae Senecio cunninghamii 6 WLA(5), MMVS(1) 

Asteraceae Rutidosis helichrysoides 1WLA


Records 

Dataset 

Asteraceae Rhodanthe uniflora 6 WLA(5), Wombeira(1) 

Asteraceae Rhodanthe stuartiana 15 WLA 

Asteraceae Rhodanthe stricta Slender Sunray 12 WLA(11), BrigOut(1) 

Asteraceae Rhodanthe pygmaea Pigmy Sunray 2 WLA 

Asteraceae Rhodanthe moschata 29 WLA(8), NLNRVS(16), NWB(1), 


Asteraceae Rhodanthe floribunda 67 WLA(38), BrigOut(1), NLNRVS(5), 


Asteraceae Rhodanthe diffusa Ascending Sunray 8 WLA(4), Wombeira(4) 

Asteraceae Rhodanthe corymbiflora Small White Sunray 27 WLA 

Asteraceae Pycnosorus pleiocephalus 15 WLA(13), NWB(2) 

Asteraceae Pycnosorus globosus 41 WLA(13), Moree(14), NWB(14) 

Asteraceae Pycnosorus chrysanthes 16 WLA(9), NWB(1), Wombeira(6) 

Asteraceae Pterocaulon sphacelatum Applebush 2 WLA 

Asteraceae Pseudognaphalium luteoalbum Jersey Cudweed 173 WLA (146), BBSPil(1), Moree(5), 


Wombeira(18) 

Asteraceae Polycalymma stuartii Poached Eggs 1 Wombeira(1) 

Asteraceae Podolepis longipedata Tall Copper-wire 

Daisy 

Asteraceae Podolepis jaceoides Showy Copper-wire 

Daisy 

Asteraceae Podolepis canescens Large Copper-wire 

Daisy 

10 WLA(5), NWB(1), Wombeira(4) 

30 WLA(14), NLNRVS(10), Wombeira(6) 

4 WLA(3), Wombeira(1) 

Asteraceae Pluchea dentex 11 Moree(8), NLNRVS(3) 

Asteraceae Pluchea baccharoides Narrow-leaved 

Plains-bush 

1WLA 

Asteraceae Picris squarrosa 1WLA 

Asteraceae Olearia viscidula Wallaby Weed 2 WLA(1), NWB(1) 

Asteraceae Olearia pimeleoides 8 WLA(7), BBSPil(1) 

Asteraceae Olearia muelleri 1WLA 

Asteraceae Olearia decurrens 2WLA(1), NWB(1) 

Asteraceae Myriocephalus stuartii Poached Eggs 57 WLA 

Asteraceae Myriocephalus rhizocephalus Woolly-heads 4 WLA(3), BrigOut(1) 

Asteraceae Minuria leptophylla 16 WLA(15), MMVS(1) 

Asteraceae Minuria integerrima 84 WLA(42), MMVS(7), NLNRVS(1), 


Asteraceae Minuria denticulata 5 WLA(3), MMVS(1), NWB(1) 

Asteraceae Minuria cunninghamii 10 WLA(8), MMVS(2) 

Asteraceae Minuria annua 1WLA 

Asteraceae Leucochrysum molle Hoary Sunray 2 WLA(1), NWB(1) 

Asteraceae Leucochrysum albicans 1WLA 

Asteraceae Leptorhynchos panaetioides Woolly Buttons 14 WLA(5), Moree(8), Wombeira(1) 

Asteraceae Ixiolaena tomentosa Woolly Ixiolaena 26 WLA(15), NWB(10), Wombeira(1) 

Asteraceae Ixiolaena leptolepis 27 WLA(17), Moree(1), NWB(6), 

Wombeira(3) 

Asteraceae Ixiolaena brevicompta 113 WLA(49), Moree(19), NLNRVS(5), 


Asteraceae Isoetopsis graminifolia Grass Cushion 6 WLA(4), MMVS(2) 

Asteraceae Hyalosperma semisterile 3WLA 

Asteraceae Hyalosperma glutinosum subsp. 

glutinosum 

1WLA 

Asteraceae Helichrysum semifertile Dainty Everlasting 5 WLA(2), BrigOut(1), Moree(2) 

Asteraceae Gnephosis tenuissima 2 WLA(1), MMVS(1)


Records 

Dataset 

Asteraceae Gnephosis arachnoidea 8 WLA(7), Wombeira(1) 

Asteraceae Glossogyne tannensis Cobbler's Tack 22 WLA(10), BBSPil(1), BBSSF(1), 


WFS(1) 

Asteraceae Flaveria australasica Speedy Weed 32 WLA(8), Moree(16), Wombeira(8) 

Asteraceae Euchiton sphaericus 122 WLA(53), Moree(17), NLNRVS(6), 


Asteraceae Euchiton involucratus Star Cudweed 3 WLA 

Asteraceae Euchiton gymnocephalus Creeping Cudweed 1 BBSSF&NR(1) 

Asteraceae Eriochlamys species A 12 NLNRVS(12) 

Asteraceae Eriochlamys behrii Woolly Mantle 5 WLA 

Asteraceae Epaltes cunninghamii Tall Nut-heads 27 WLA(14), Wombeira(13) 

Asteraceae Epaltes australis Spreading Nutheads 

27 WLA(25), BBSPil(1), Wombeira(1) 

Asteraceae Eclipta platyglossa 129 WLA(30), MMVS(97), Namoi(1), 

Wombeira(1) 

Asteraceae Cymbonotus lawsonianus Bear's Ear 2 WLA(1), NWB(1) 

Asteraceae Craspedia variabilis 3WLA 

Asteraceae Craspedia haplorrhiza 3 WLA(2), Moree(1) 

Asteraceae Cotula australis Common Cotula 14 WLA(2), MMVS(9), Moree(3) 

Asteraceae Chthonocephalus pseudevax Ground-heads 7 WLA(3), NLNRVS(4) 

Asteraceae Chrysocephalum semipapposum Clustered 

Everlasting 

1 Moree(1) 

Asteraceae Chrysocephalum semicalvum subsp. 

semicalvum 

Hill Everlasting 22 WLA(1), Moree(21) 

Asteraceae Chrysocephalum apiculatum Common 

Everlasting 

Asteraceae Centipeda thespidioides Desert 

Sneezeweed 

Asteraceae Centipeda minima var minima Spreading 

Sneezeweed 

134 WLA(115), BBSPil(1), NLNRVS(9), 


30 WLA(18), BrigOut(1), Moree(4), 


1000 WLA 

Asteraceae Centipeda minima var lanuginosa 5 Moree(3), NLNRVS(2) 

Asteraceae Centipeda minima Spreading 

Sneezeweed 

Asteraceae Centipeda cunninghamii Common 

Sneezeweed 

Asteraceae Cassinia quinquefaria 1WLA 

Asteraceae Cassinia laevis Cough Bush 1 WLA 

57 WLA(14), MMVS(32), Wombeira(11) 

63 WLA(43), BrigOut(1), NLNRVS(6), 


Asteraceae Calotis scapigera Tufted Burr-daisy 119 WLA(67), MMVS(10), Moree(19), 


Wombeira(3) 

Asteraceae Calotis scabiosifolia var scabiosifolia Rough Burr-daisy 60 WLA(23), MMVS(5), Moree(29), 

NWB(3) 

Asteraceae Calotis scabiosifolia var integrifolia Rough Burr-daisy 2 WLA(1), NWB(1) 

Asteraceae Calotis scabiosifolia Rough Burr-daisy 18 WLA(12), NWB(2), Wombeira(4) 

Asteraceae Calotis plumulifera Woolly-headed 

Burr-daisy 

2WLA 

Asteraceae Calotis latiuscula 1WLA 

Asteraceae Calotis lappulacea Yellow Burr-daisy 1079 WLA(1033), BBSPil(5), BBSSF(1), 


BBSpil2(1) 

Asteraceae Calotis hispidula Bogan Flea 39 WLA(17), MMVS(15), Moree(4), 


Asteraceae Calotis erinacea Tangled Burr-daisy 23 WLA 

Asteraceae Calotis cymbacantha Showy Burr-daisy 14 WLA(10), WFS(3), Wombeira(1) 

Asteraceae Calotis cuneifolia Purple Burr-Daisy 59 WLA(15), BBSPil(6), BBSSF&NR(1), 

BBSSF(1), NLNRVS(21), NWB(10), 

BBSpil2(2), WFS(3)


Records 

Dataset 

Asteraceae Calotis cuneata var cuneata Mountain Burr- 

Daisy 

19 WLA(8), Moree(3), NWB(8) 

Asteraceae Calotis cuneata Mountain Burr- 

Daisy 

3 WLA(1), NWB(1), WFS(1) 

Asteraceae Calocephalus sonderi Pale Beauty-heads 5 WLA(3), NLNRVS(2) 

Asteraceae Calendula arvensis Field Marigold 13 WLA 

Asteraceae Bracteantha viscosa Sticky Everlasting 1 BBSSF&NR(1) 

Asteraceae Bracteantha bracteata Golden Everlasting 11 WLA(3), BBSPil(1), MMVS(1), 


Asteraceae Brachyscome whitei Spreading Daisy 11 WLA(5), MMVS(3), NWB(3) 

Asteraceae Brachyscome trachycarpa 3 Moree(3) 

Asteraceae Brachyscome smithwhitei 5WLA(3), NWB(2) 

Asteraceae Brachyscome scapigera 1 NLNRVS(1) 

Asteraceae Brachyscome multifida var multifida 4 BBSPil(4) 

Asteraceae Brachyscome multifida 3 Moree(3) 

Asteraceae Brachyscome microcarpa 2 Moree(2) 

Asteraceae Brachyscome melanocarpa Black-seeded Daisy 17 WLA(9), Moree(6), Wombeira(2) 

Asteraceae Brachyscome lineariloba Hard-headed Daisy 17 WLA(16), MMVS(1) 

Asteraceae Brachyscome leptocarpa 1 MMVS(1) 

Asteraceae Brachyscome heterodonta var 

heterodonta 

26 Moree(26) 

Asteraceae Brachyscome heterodonta 153 WLA(120), MMVS(22), NWB(11) 

Asteraceae Brachyscome gracilis 1 Moree(1) 

Asteraceae Brachyscome goniocarpa 1 NLNRVS(1) 

Asteraceae Brachyscome debilis 9 MMVS(9) 

Asteraceae Brachyscome curvicarpa 21 WLA(15), NWB(5), Wombeira(1) 

Asteraceae Brachyscome ciliocarpa Showy Daisy 1 WLA 

Asteraceae Brachyscome ciliaris var 

subintegrifolia 

Variable Daisy 2 WLA(1), NWB(1) 

Asteraceae Brachyscome ciliaris var ciliaris Variable Daisy 8 WLA(3), NLNRVS(4), NWB(1) 

Asteraceae Brachyscome ciliaris Variable Daisy 34 WLA(30), NWB(3), Wombeira(1) 

Asteraceae Brachyscome basaltica var gracilis Swamp Daisy 15 WLA(6), MMVS(5), Wombeira(4) 

Asteraceae Brachyscome angustifolia var 

heterophylla 

Asteraceae Brachyscome angustifolia var 

angustifolia 

3NWB(3) 

3WLA 

Asteraceae Angianthus brachypappus Spreading Cupflower 


Asteraceae Anemocarpa podolepidium Rock Everlasting 1 WLA 

Asteraceae Actinobole uliginosum Flannel Cudweed 16 WLA(8), NLNRVS(8) 

Solanaceae Solanum tetrathecum 4 BBSPil(3), BBSpil2(1) 

Solanaceae Solanum sturtianum Thargomindah 

Nightshade 

18 WLA(1), Moree(14), NLNRVS(2), 

NWB(1) 

Solanaceae Solanum parvifolium 18 WLA(9), NWB(9) 

Solanaceae Solanum lacunarium Lagoon Nightshade 1 WLA 

Solanaceae Solanum ferocissimum 18 WLA(8), BBSSF(1), NLNRVS(3), 

NWB(6) 

Solanaceae Solanum esuriale Quena 469 WLA(248), MMVS(94), Moree(86), 

NWB(34), Namoi(1), WFS(4), 

Wombeira(2) 

Solanaceae Solanum coactiliferum Western 

Nightshade 

5WLA(3), NWB(2) 

Solanaceae Solanum cleistogamum 1 NLNRVS(1) 

Solanaceae Nicotiana velutina 48 WLA(38), MMVS(5), Wombeira(5) 

Solanaceae Nicotiana simulans 13 MMVS(1), Moree(1), NLNRVS(11) 

Solanaceae Nicotiana megalosiphon subsp. 

megalosiphon 

9 WLA(6), Moree(2), NWB(1)


Records 

Dataset 

Solanaceae Lycium australe Australian Boxthorn 3 WLA(2), NWB(1) 

Convolvulaceae Polymeria pusilla 119 WLA(100), Moree(19) 

Convolvulaceae Polymeria longifolia 18 WLA(1), Moree(17) 

Convolvulaceae Ipomoea lonchophylla 25 WLA(10), Moree(15) 

Convolvulaceae Evolvulus alsinoides var decumbens 14 WLA(4), BBSPil(4), BBSSF(1), 

MMVS(1), NWB(4) 

Convolvulaceae Evolvulus alsinoides 13 WLA(3), NLNRVS(6), NWB(2), 

BBSpil2(1), Wombeira(1) 

Convolvulaceae Dichondra species A 5 BBSPil(3), BBSSF(1), BBSpil2(1) 

Convolvulaceae Dichondra repens Kidney Weed 35 WLA(11), MMVS(4), Moree(8), 

NWB(11), Namoi(1) 

Convolvulaceae Cuscuta victoriana 11 MMVS(11) 

Convolvulaceae Convolvulus remotus 1 Moree(1) 

Convolvulaceae Convolvulus erubescens 177 WLA(43), MMVS(62), Moree(61), 


WFS(1) 

Boraginaceae Plagiobothrys plurisepalus 4WLA 

Boraginaceae Plagiobothrys plurisepaleus 1 MMVS(1) 

Boraginaceae Plagiobothrys elachanthus 1WLA 

Boraginaceae Omphalolappula concava Burr Stickseed 3 WLA 

Boraginaceae Ehretia membranifolia Peach Bush 15 WLA(8), NWB(7) 

Boraginaceae Cynoglossum australe 19 WLA(5), BBSPil(2), MMVS(2), 


Epacridaceae Styphelia triflora 2WLA(1), NWB(1) 

Epacridaceae Melichrus urceolatus Urn Heath 5 WLA(2), NWB(2), BBSpil2(1) 

Epacridaceae Melichrus erubescens Ruby Urn Heath 2 WLA(1), NWB(1) 

Epacridaceae Leucopogon muticus 1 BBSpil2(1) 

Epacridaceae Leucopogon attenuatus 1 BBSSF&NR(1) 

Epacridaceae Brachyloma daphnoides 4 WLA(1), BBSSF&NR(1), NWB(1), 

BBSpil2(1) 

Epacridaceae Astroloma humifusum 1 BBSSF&NR(1) 

Sambucaceae Sambucus gaudichaudiana White Elderberry 2 WLA(1), NWB(1) 

Goodeniaceae Velleia paradoxa 1 MMVS(1) 

Goodeniaceae Velleia arguta 9 NLNRVS(9) 

Goodeniaceae Scaevola spinescens 14 WLA(10), NWB(4) 

Goodeniaceae Scaevola humilis 1 BBSPil(1) 

Goodeniaceae Goodenia willisiana 1WLA 

Goodeniaceae Goodenia pusilliflora 1WLA 

Goodeniaceae Goodenia pinnatifida 6WLA 

Goodeniaceae Goodenia lunata 2 MMVS(2) 

Goodeniaceae Goodenia heteromera 17 WLA 

Goodeniaceae Goodenia hederacea subsp. 

hederacea 

7 NLNRVS(7) 

Goodeniaceae Goodenia hederacea 5 MMVS(5) 

Goodeniaceae Goodenia glauca 74 WLA(27), MMVS(26), NLNRVS(3), 

Wombeira(18) 

Goodeniaceae Goodenia glabra 7 WLA(2), BBSPil(3), NWB(1), 

Namoi(1) 

Goodeniaceae Goodenia fascicularis 263 WLA(153), MMVS(16), Moree(44), 


Goodeniaceae Goodenia delicata 1 NLNRVS(1) 

Goodeniaceae Goodenia cycloptera 20 WLA(10), BBSPil(4), BBSSF(1), 


Goodeniaceae Dampiera lanceolata var lanceolata 2WLA 

Goodeniaceae Brunonia australis 8 NLNRVS(8) 

Loganiaceae Logania albiflora 2WLA(1), NWB(1)


Records 

Dataset 

Rubiaceae Synaptantha tillaeacea 2 WLA(1), NLNRVS(1) 

Rubiaceae Pomax umbellata 1 BBSpil2(1) 

Rubiaceae Opercularia diphylla 1 BBSpil2(1) 

Rubiaceae Galium gaudichaudii Rough Bedstraw 6 WLA(3), NWB(3) 

Rubiaceae Coprosma hirtella 3WLA 

Rubiaceae Canthium oleifolium Wild Lemon 32 WLA(16), BBSPil(1), BBSSF(1), 

MMVS(1), NLNRVS(2), NWB(11) 

Rubiaceae Canthium odoratum Shiny-leaved 

Canthium 

4WLA(2), NWB(2) 

Rubiaceae Canthium latifolium Native Currant 2 WLA(1), NWB(1) 

Rubiaceae Asperula gemella Twin-leaved 

Bedstraw 

46 WLA(23), Wombeira(23) 

Rubiaceae Asperula cunninghamii Twining Woodruff 2 WLA(1), NWB(1) 

Rubiaceae Asperula conferta Common Woodruff 141 WLA(114), Moree(15), NWB(12) 

Menyanthaceae Nymphoides spinulosperma 2RBG 

Menyanthaceae Nymphoides crenata 4 MMVS(4) 

Gentianaceae Centaurium spicatum Spike Centaury 90 WLA (50), Moree(9), NLNRVS(4), 

Wombeira(27) 

Apocynaceae Parsonsia lanceolata 8WLA(4), NWB(4) 

Apocynaceae Parsonsia eucalyptophylla Gargaloo 41 WLA(19), BBSPil(2), BBSSF(1), 


Apocynaceae Carissa ovata Currant Bush 7 WLA(4), NWB(3) 

Apocynaceae Alstonia constricta Quinine Bush 74 WLA(37), MMVS(2), NLNRVS(4), 

NWB(29), WFS(2) 

Asclepiadaceae Marsdenia australis Doubah 12 WLA(6), Brigfauna(1), MMVS(1), 

NWB(4) 

Bignoniaceae Pandorea pandorana Wonga Wonga Vine 8 WLA(4), MMVS(2), NWB(2) 

Myoporaceae Myoporum platycarpum Sugarwood 25 WLA(12), BBSSF&NR(1), MMVS(11), 

NWB(1) 

Myoporaceae Myoporum montanum Western Boobialla 49 WLA(21), BBSPil(6), BBSSF(1), 


Wombeira(1) 

Myoporaceae Eremophila sturtii Turpentine Bush 34 WLA 

Myoporaceae Eremophila polyclada Flowering Lignum 6 WLA(5), NWB(1) 

Myoporaceae Eremophila mitchellii Budda 292 WLA(132), BBSPil(2), BrigOut(2), 

Brigfauna(1), MMVS(8), NLNRVS(8), 

NWB(126), WFS(13) 

Myoporaceae Eremophila maculata Spotted Fuchsia 50 WLA(30), Moree(3), NWB(16), 

WFS(1) 

Myoporaceae Eremophila longifolia Emubush 69 WLA(33), BBSPil(6), BBSSF(1), 

MMVS(1), NLNRVS(1), NWB(26), 

WFS(1) 

Myoporaceae Eremophila glabra Tar Bush 4 WLA(3), NWB(1) 

Myoporaceae Eremophila divaricata Spreading 

Emubush 

3WLA 

Myoporaceae Eremophila deserti Turkeybush 17 WLA(10), MMVS(1), NWB(6) 

Myoporaceae Eremophila debilis Amulla 36 WLA(22), MMVS(3), NWB(11) 

Myoporaceae Eremophila bowmanii Silver Turkeybush 1 WLA 

Myoporaceae Eremophila bignoniiflora Eurah 129 WLA(64), Moree(6), NLNRVS(4), 


Scrophulariaceae Veronica plebeia Trailing Speedwell 2 WLA(1), NWB(1) 

Scrophulariaceae Stemodia glabella 5 WLA(1), Moree(4) 

Scrophulariaceae Stemodia florulenta Bluerod 33 WLA(31), Moree(2) 

Scrophulariaceae Misopates orontium Lesser Snapdragon 2 WLA 

Scrophulariaceae Mimulus repens Creeping Monkeyflower 

Scrophulariaceae Mimulus prostratus Small Monkeyflower 

8WLA(4), NWB(4) 

8WLA(5), NWB(3)


Records 

Scrophulariaceae Mimulus gracilis Slender Monkeyflower 

Dataset 

Scrophulariaceae Limosella curdieana Large Mudwort 1 WLA 

253 WLA(226), MMVS(5), Moree(1), 


Scrophulariaceae Limosella australis Australian Mudwort 4 WLA(3), NLNRVS(1) 

Scrophulariaceae Glossostigma diandrum 1 NLNRVS(1) 

Scrophulariaceae Euphrasia collina subsp. paludosa 2 Moree(2) 

Plantaginaceae Plantago varia 16 WLA(3), NLNRVS(13) 

Plantaginaceae Plantago turrifera 27 WLA(25), MMVS(1), NWB(1) 

Plantaginaceae Plantago drummondii 39 WLA(28), Moree(3), NWB(2), 


Plantaginaceae Plantago debilis 4 WLA(1), Moree(2), Namoi(1) 

Plantaginaceae Plantago cunninghamii 117 WLA(61), MMVS(1), Moree(14), 


Acanthaceae Rostellularia adscendens subsp. adscendens var 

pogonanthera 

Acanthaceae Rostellularia adscendens subsp. adscendens var 

adscendens 

Acanthaceae Rostellularia adscendens subsp. 

adscendens 

1000 WLA 

1 BBSSF(1) 

50 WLA(23), BBSPil(2), Moree(2), 


Acanthaceae Pseuderanthemum variabile Pastel Flower 4 BBSPil(3), BBSpil2(1) 

Acanthaceae Brunoniella australis Blue Trumpet 125 WLA(111), BBSSF(1), NLNRVS(2), 

NWB(11) 

Chloanthaceae Spartothamnella puberula 1 BBSPil(1) 

Callitrichaceae Callitriche sonderi 1WLA 

Lamiaceae Teucrium racemosum Grey Germander 56 WLA(39), Brigfauna(1), MMVS(6), 


Wombeira(3) 

Lamiaceae Prostanthera nivea 2 Moree(2) 

Lamiaceae Plectranthus parviflorus 2WLA(1), NWB(1) 

Lamiaceae Mentha satureioides Native Pennyroyal 2 WLA(1), NWB(1) 

Lamiaceae Mentha diemenica Slender Mint 2 WLA(1), Moree(1) 

Lamiaceae Mentha australis River Mint 14 WLA(12), MMVS(1), Wombeira(1) 

Lamiaceae Lycopus australis Australian 

Gypsywort 

1 NLNRVS(1) 

Lamiaceae Ajuga australis Austral Bugle 7 WLA(3), NLNRVS(1), NWB(3) 

Hydrocharitaceae Vallisneria gigantea Eelweed 5 WLA(4), NWB(1) 

Alismataceae Damasonium minus Starfruit 14 WLA(1), MMVS(12), Wombeira(1) 

Juncaginaceae Triglochin procerum Water Ribbons 3 MMVS(3) 

Juncaginaceae Triglochin calcitrapum Spurred Arrowgrass 2 WLA 

Potamogetonaceae Potamogeton tricarinatus Floating Pondweed 2 WLA 

Potamogetonaceae Potamogeton crispus Curly Pondweed 3 WLA 

Lemnaceae Lemna disperma 106 WLA(101), MMVS(1), NLNRVS(4) 

Luzuriagaceae Eustrephus latifolius Wombat Berry 2 WLA(1), NWB(1) 

Lomandraceae Lomandra multiflora subsp. multiflora Many-flowered Mat 

Rush 

Lomandraceae Lomandra longifolia Spiny-headed Matrush 

Lomandraceae Lomandra leucocephala subsp. 

robusta 

Lomandraceae Lomandra leucocephala subsp. 

leucocephala 

Woolly Mat-rush 1 WLA 

Woolly Mat-rush 5 WLA 

12 WLA(2), BBSPil(4), BBSSF&NR(1), 

BBSSF(1), NWB(2), BBSpil2(2) 

10 WLA(5), NWB(5) 

Lomandraceae Lomandra leucocephala Woolly Mat-rush 2 WLA(1), NWB(1) 

Lomandraceae Lomandra filiformis Wattle Matt-rush 4 WLA(1), BBSSF&NR(1), NWB(1), 

BBSpil2(1) 

Hypoxidaceae Hypoxis glabella var glabella 3 MMVS(3) 

Phormiaceae Dianella sp. aff. revoluta 'Pilliga' 1 BBSpil2(1)


Records 

Dataset 

Phormiaceae Dianella revoluta var vinosa 4 BBSPil(4) 

Phormiaceae Dianella revoluta 9 WLA(3), MMVS(2), NLNRVS(1), 

NWB(3) 

Phormiaceae Dianella longifolia var longifolia 12 WLA(7), NLNRVS(1), NWB(4) 

Phormiaceae Dianella longifolia 2 BBSPil(1), BBSSF(1) 

Phormiaceae Dianella 'admixta' 1 BBSpil2(1) 

Asphodelaceae Bulbine semibarbata Wild Onion 68 WLA(32), Moree(3), NLNRVS(13), 


Asphodelaceae Bulbine bulbosa Bulbine Lily 18 WLA(14), NWB(1), Wombeira(3) 

Asphodelaceae Bulbine alata Native Leek 1 WLA 

Anthericaceae Tricoryne elatior Yellow Autumn-lily 5 WLA(2), NWB(2), WFS(1) 

Anthericaceae Thysanotus tuberosus subsp. 

tuberosus 

1 BBSPil(1) 

Anthericaceae Thysanotus baueri 2WLA 

Anthericaceae Laxmannia gracilis 3 BBSPil(2), BBSSF(1) 

Anthericaceae Dichopogon strictus Chocolate Lily 2 WLA(1), NWB(1) 

Anthericaceae Caesia calliantha 1 Moree(1) 

Anthericaceae Arthropodium minus 5 NLNRVS(5) 

Amaryllidaceae Crinum flaccidum Darling Lily 62 WLA(35), MMVS(7), Moree(1), 


Wombeira(1) 

Amaryllidaceae Calostemma purpureum Garland Lily 30 WLA(16), NWB(13), Namoi(1) 

Pontederiaceae Monochoria cyanea 3WLA(2), NWB(1) 

Philydraceae Philydrum lanuginosum Frogsmouth 20 WLA 

Typhaceae Typha orientalis Broad-leaved 

Cumbungi 

Typhaceae Typha domingensis Narrow-leaved 

Cumbungi 

501 WLA 

Commelinaceae Commelina ensifolia 2 Moree(2) 

67 WLA(16), MMVS(40), NWB(11) 

Commelinaceae Commelina cyanea 18 WLA(6), BBSPil(3), BBSSF(1), 


Juncaceae Juncus usitatus 22 WLA(14), NWB(2), Wombeira(6) 

Juncaceae Juncus subsecundus 10 BBSPil(2), MMVS(1), Moree(7) 

Juncaceae Juncus radula 2 MMVS(2) 

Juncaceae Juncus ochrocoleus 4WLA(2), NWB(2) 

Juncaceae Juncus flavidus 5 WLA(1), NLNRVS(3), NWB(1) 

Juncaceae Juncus filicaulis 2 BBSPil(2) 

Juncaceae Juncus continuus 4WLA(2), NWB(2) 

Juncaceae Juncus aridicola 64 WLA(27), MMVS(8), Moree(2), 


Juncaceae Juncus amabilis 17 MMVS(17) 

Cyperaceae Scleria mackaviensis 2 BBSPil(2) 

Cyperaceae Schoenus ericetorum 1 BBSpil2(1) 

Cyperaceae Schoenoplectus validus 2 MMVS(1), Namoi(1) 

Cyperaceae Gahnia aspera 1 BBSpil2(1) 

Cyperaceae Fimbristylis dichotoma 23 WLA(1), BBSPil(1), Moree(5), 


Cyperaceae Eleocharis sphacelata Tall Spike Rush 152 WLA(102), MMVS(48), NWB(2) 

Cyperaceae Eleocharis pusilla 27 WLA(9), MMVS(8), NLNRVS(2), 


Cyperaceae Eleocharis plana 1119 WLA(1033), MMVS(43), Moree(8), 


Cyperaceae Eleocharis pallens 126 WLA(45), MMVS(22), Moree(17), 


Cyperaceae Eleocharis acuta 2WLA


Records 

Dataset 

Cyperaceae Cyperus victoriensis 4 MMVS(1), Moree(3) 

Cyperaceae Cyperus subulatus 2WLA(1), Namoi(1) 

Cyperaceae Cyperus squarrosus 1WLA 

Cyperaceae Cyperus pygmaeus 14 WLA(8), MMVS(4), Wombeira(2) 

Cyperaceae Cyperus polystachyos 2WLA 

Cyperaceae Cyperus lucidus 5 WLA(1), Moree(3), NWB(1) 

Cyperaceae Cyperus iria 2WLA(1), NWB(1) 

Cyperaceae Cyperus involucratus 1 MMVS(1) 

Cyperaceae Cyperus gymnocaulos 29 WLA(22), NLNRVS(3), NWB(2), 

Namoi(2) 

Cyperaceae Cyperus gracilis 7 BBSPil(5), BBSSF(1), BBSpil2(1) 

Cyperaceae Cyperus fulvus 7 WLA(1), BBSPil(5), BBSpil2(1) 

Cyperaceae Cyperus flaccidus 1002 WLA(1000), NLNRVS(2) 

Cyperaceae Cyperus exaltatus 28 WLA(15), MMVS(2), NWB(3), 


Cyperaceae Cyperus difformis Dirty Dora 1030 WLA(1002), MMVS(26), NLNRVS(1), 

NWB(1) 

Cyperaceae Cyperus dactylotes 2 MMVS(2) 

Cyperaceae Cyperus concinnus 77 WLA(28), MMVS(1), Moree(20), 

Wombeira(28) 

Cyperaceae Cyperus bifax 100 WLA(2), MMVS(37), Moree(59), 

NLNRVS(2) 

Cyperaceae Carex inversa Knob Sedge 49 WLA(19), MMVS(10), Moree(1), 

NWB(17), BBSpil2(1), Namoi(1) 

Cyperaceae Carex appressa 5WLA(3), NWB(2) 

Cyperaceae Bulbostylis barbata 4 BBSSF(1), NLNRVS(3) 

Poaceae Zygochloa paradoxa Sandhill Canegrass 6 WLA 

Poaceae Vetiveria filipes Australian Vetiver 4 WLA(3), NWB(1) 

Poaceae Triraphis mollis Purple Needlegrass 14 WLA(12), NLNRVS(1), NWB(1) 

Poaceae Tripogon loliiformis Fiveminute Grass 28 WLA(7), Brigfauna(1), MMVS(1), 


WFS(2) 

Poaceae Triodia scariosa subsp. scariosa Porcupine Grass 1 WLA 

Poaceae Triodia mitchellii var breviloba Buck Spinifex 2 WLA 

Poaceae Triodia mitchellii 9 NLNRVS(9) 

Poaceae Triodia scariosa Porcupine Grass 6 WLA(4), NWB(2) 

Poaceae Tragus australianus Small Burrgrass 76 WLA(56), MMVS(1), Moree(9), 


WFS(5) 

Poaceae Thyridolepis xerophila 5 NLNRVS(5) 

Poaceae Thyridolepis mitchelliana Mulga Mitchell 

14 WLA(6), BBSPil(1), NLNRVS(2), 

Grass 

NWB(5) 

Poaceae Themeda avenacea Native Oatgrass 7 WLA(1), MMVS(1), Moree(5) 

Poaceae Themeda australis Kangaroo Grass 11 WLA(8), NWB(3) 

Poaceae Thellungia advena Coolibah Grass 28 WLA(19), NWB(9) 

Poaceae Sporobolus virginicus 2WLA(1), NWB(1) 

Poaceae Sporobolus mitchellii Rat's Tail Couch 1137 WLA(1013), MMVS(58), Moree(65), 

Namoi(1) 

Poaceae Sporobolus elongatus Slender Rat's Tail 

Grass 

41 Moree(41) 

Poaceae Sporobolus creber Slender Rat's Tail 

9 WLA(1), BBSPil(2), BBSSF(1), 

Grass 

Moree(4), Namoi(1) 

Poaceae Sporobolus contiguus 1 MMVS(1) 

Poaceae Sporobolus caroli Fairy Grass 1168 WLA(1023), MMVS(43), Moree(75), 



Poaceae Sporobolus actinocladus Katoora Grass 4 WLA(2), NLNRVS(2) 

Poaceae Pseudoraphis spinescens Spiny Mudgrass 1003 WLA


Records 

Dataset 

Poaceae Poa labillardierei var labillardierei Tussock 3 WLA (2), NWB(1) 

Poaceae Poa fordeana 21 WLA(11), Moree(1), NWB(5), 

Wombeira(4) 

Poaceae Phragmites australis Common Reed 29 WLA(9), MMVS(15), NLNRVS(1), 

NWB(4) 

Poaceae Paspalum distichum Water Couch 1088 WLA (1015), MMVS(69), NWB(2), 

Namoi(2) 

Poaceae Paspalidium jubiflorum Warrego Grass 256 WLA(58), MMVS(126), Moree(27), 



Poaceae Paspalidium gracile Slender Panic 43 WLA(20), BBSPil(2), MMVS(1), 


Poaceae Paspalidium globoideum 24 Moree(23), NWB(1) 

Poaceae Paspalidium distans 1021 WLA(1010), BBSPil(1), Moree(1), 

NWB(9) 

Poaceae Paspalidium criniforme 2WLA(1), NWB(1) 

Poaceae Paspalidium constrictum Knottybutt Grass 56 WLA(11), BBSPil(2), Brigfauna(1), 


BBSpil2(1) 

Poaceae Paspalidium aversum 45 WLA(22), BBSSF(1), NWB(20), 

Namoi(2) 

Poaceae Paractaenum novae-hollandiae Reflexed Panic 

Grass 

1WLA 

Poaceae Panicum subxerophilum Gilgai Grass 11 WLA(4), Moree(4), NWB(3) 

Poaceae Panicum queenslandicum var 

queenslandicum 

15 Moree(15) 

Poaceae Panicum queenslandicum 1NWB(1) 

Poaceae Panicum laevinode Pepper Grass 14 WLA(4), MMVS(5), Moree(5) 

Poaceae Panicum laevifolium 1 Namoi(1) 

Poaceae Panicum effusum Poison or Hairy 

Panic 

11 WLA(3), BBSPil(3), MMVS(1), 

Moree(1), NWB(1), BBSpil2(1), 

WFS(1) 

Poaceae Panicum decompositum Native Millet 1163 WLA(1019), MMVS(41), Moree(89), 

NWB(11), Namoi(2), WFS(1) 

Poaceae Panicum buncei 10 Moree(10) 

Poaceae Notodanthonia longifolia Long-leaved 

Wallaby Grass 

2WLA(1), NWB(1) 

Poaceae Monachather paradoxa Bandicoot Grass 2 WLA(1), NLNRVS(1) 

Poaceae Microlaena stipoides 1 BBSpil2(1) 

Poaceae Leptochloa divaricatissima 14 Moree(14) 

Poaceae Leptochloa digitata Umbrella 

114 WLA(81), MMVS(5), Moree(1), 

Canegrass 


Poaceae Leptochloa decipiens 1NWB(1) 

Poaceae Leptochloa ciliolata 3 WLA(1), NWB(1), BBSpil2(1) 

Poaceae Iseilema vaginiflorum Red Flinders Grass 22 WLA(1), Moree(21) 

Poaceae Iseilema membranaceum Small Flinders 

Grass 

21 WLA(12), Moree(9) 

Poaceae Homopholis proluta 24 WLA(13), NWB(5), Wombeira(6) 

Poaceae Heteropogon contortus Bunch Speargrass 50 WLA 

Poaceae Eulalia aurea Silky Browntop 105 WLA(100), Moree(5) 

Poaceae Eriochloa pseudoacrotricha Early Spring Grass 1012 WLA(1008), NWB(2), Namoi(2) 

Poaceae Eriochloa procera Spring Grass 2 WLA(1), Namoi(1) 

Poaceae Eriochloa crebra Cup Grass 1099 WLA(1005), MMVS(1), Moree(92), 

Wombeira(1) 

Poaceae Eriochloa australiensis 1201 WLA 

Poaceae Echinochloa inundata Marsh Millet 3 WLA(2), Moree(1) 

Poaceae Eriachne mucronata Mountain 

Wanderrie Grass 

4WLA(2), NWB(2)


Records 

Poaceae Eriachne helmsii Woollybutt 


Poaceae Eriachne aristidea Threeawn 


Dataset 

1WLA 

3WLA(2), NWB(1) 

Poaceae Eragrostis tenellula Delicate Lovegrass 2 WLA(1), NWB(1) 

Poaceae Eragrostis sororia 2 BBSPil(1), BBSpil2(1) 

Poaceae Eragrostis setifolia Neverfail 126 WLA(39), MMVS(7), Moree(42), 


Poaceae Eragrostis parviflora Weeping Lovegrass 231 WLA(205), MMVS(19), Moree(6), 

NLNRVS(1) 

Poaceae Eragrostis molybdea 33 WLA(1), Moree(31), NWB(1) 

Poaceae Eragrostis microcarpa 1WLA 

Poaceae Eragrostis megalosperma 10 WLA(5), NWB(5) 

Poaceae Eragrostis leptostachya Paddock Lovegrass 1 BBSSF&NR(1) 

Poaceae Eragrostis leptocarpa Drooping Lovegrass 2 WLA(1), Wombeira(1) 

Poaceae Eragrostis laniflora 6 NLNRVS(6) 

Poaceae Eragrostis lacunaria Purple Lovegrass 41 WLA(7), BBSPil(5), BBSSF(1), 


Poaceae Eragrostis kennedyae Small-flowered 

Lovegrass 


6 WLA(1), MMVS(5) 

Poaceae Eragrostis falcata Sickle Lovegrass 9 WLA(5), MMVS(1), NWB(3) 

Poaceae Eragrostis eriopoda Woollybutt 15 WLA(1), Moree(14) 

Poaceae Eragrostis elongata Clustered 

5 WLA(2), MMVS(1), NWB(1), 

Lovegrass 

Namoi(1) 

Poaceae Eragrostis dielsii Mallee Lovegrass 17 WLA(16), NLNRVS(1) 

Poaceae Eragrostis brownii Brown's Lovegrass 7 WLA(2), BBSSF(1), NWB(2), WFS(2) 

Poaceae Eragrostis australasica Canegrass 5 WLA 

Poaceae Enteropogon acicularis 1462 WLA(1237), BBSPil(5), Moree(81), 


Poaceae Enneapogon nigricans Niggerheads 3 WLA(1), MMVS(1), NWB(1) 

Poaceae Enneapogon intermedius 5WLA 

Poaceae Enneapogon gracilis Slender Nineawn 1005 WLA(1000), Moree(5) 

Poaceae Enneapogon cylindricus Jointed Nineawn 3 WLA 

Poaceae Enneapogon avenaceus Bottle Washers 39 WLA 

Poaceae Elytrophorus spicatus Spikegrass 2 WLA 

Poaceae Elymus scaber 19 WLA(12), Moree(6), NWB(1) 

Poaceae Echinochloa colona Awnless Barnyard 

Grass 

Poaceae Diplachne parviflora Small-flowered 

Beetle Grass 

42 WLA(4), MMVS(7), Moree(30), 

NWB(1) 

1001 WLA(1000), BBSPil(1) 

Poaceae Diplachne muelleri 4WLA(2), NWB(2) 

Poaceae Diplachne fusca 11 WLA(5), MMVS(1), Moree(3), 

NWB(2) 

Poaceae Digitaria divaricatissima Umbrella Grass 44 WLA(5), Moree(36), NWB(3) 

Poaceae Digitaria diffusa 5 BBSPil(4), BBSSF(1) 

Poaceae Digitaria brownii Cotton Panic Grass 106 WLA(101), BBSPil(2), BBSSF(1), 


Poaceae Digitaria breviglumis 4 Moree(2), BBSpil2(1), WFS(1) 

Poaceae Digitaria ammophila 8 Moree(6), NLNRVS(1), WFS(1) 

Poaceae Dichelachne micrantha Shorthair 

Plumegrass 

Poaceae Dichanthium sericeum subsp. Queensland 

sericeum 

Bluegrass 

Poaceae Dichanthium sericeum Queensland 

Bluegrass 

2WLA(1), NWB(1) 

64 WLA(3), Moree(58), NWB(3) 

20 WLA(10), NWB(3), Namoi(3), WFS(4)


Records 

Dataset 

Poaceae Dactyloctenium radulans Button Grass 1155 WLA(1108), MMVS(15), Moree(24), 


Poaceae Cynodon dactylon Common Couch 1135 WLA(1046), Brigfauna(1), MMVS(55), 



Poaceae Cymbopogon refractus Barbed Wire Grass 4 WLA(2), NWB(2) 

Poaceae Cymbopogon obtectus Silky Heads 5 WLA(3), NWB(2) 

Poaceae Chloris ventricosa Tall Chloris 1000 WLA 

Poaceae Chloris truncata Windmill Grass 2347 WLA(2170), BBSPil(4), MMVS(45), 



Poaceae Chloris divaricata var divaricata Slender Chloris 88 WLA(6), MMVS(80), NWB(2) 

Poaceae Bromus arenarius 1NWB(1) 

Poaceae Brachyachne convergens Common Native 

Couch 

1000 WLA 

Poaceae Bothriochloa macra Red Grass 1003 WLA(1001), Moree(1), Namoi(1) 

Poaceae Bothriochloa ewartiana Desert Bluegrass 22 WLA 

Poaceae Bothriochloa decipiens Red Grass 9 WLA(3), Moree(3), NWB(3) 

Poaceae Bothriochloa bladhii subsp bladhii Forest Bluegrass 4 WLA(2), Namoi(2) 

Poaceae Austrostipa verticillata 49 WLA(32), BBSPil(3), Moree(2), 


Poaceae Austrostipa setacea Corkscrew Grass 5 WLA(2), NWB(2), BBSpil2(1) 

Poaceae Austrostipa scabra subsp scabra 31 WLA(11), BBSPil(7), BBSSF(1), 


Poaceae Austrostipa scabra subsp falcata 2NWB(2) 

Poaceae Austrostipa scabra Speargrass 282 WLA(197), BBSSF&NR(1), 



Poaceae Austrostipa ramosissima Stout Bamboo 

Grass 

8WLA(5), NWB(3) 

Poaceae Austrostipa nodosa 1WLA 

Poaceae Austrostipa nitida 1WLA 

Poaceae Austrostipa elegantissima Feather Speargrass 1 WLA 

Poaceae Austrostipa drummondii 1WLA 

Poaceae Austrostipa aristiglumis Plains Grass 13 WLA(5), Moree(4), NWB(3), Namoi(1) 

Poaceae Austrodanthonia setacea 5 WLA(4), Moree(1) 

Poaceae Austrodanthonia richardsonii Wallaby Grass 1 Moree(1) 

Poaceae Austrodanthonia pilosa Smooth-flowered 

Wallaby Grass 

1 BBSpil2(1) 

Poaceae Austrodanthonia fulva 2WLA(1), NWB(1) 

Poaceae Austrodanthonia eriantha 2 WLA(1), BBSSF&NR(1) 

Poaceae Austrodanthonia caespitosa Ringed Wallaby 

Grass 

7 WLA(2), MMVS(5) 

Poaceae Austrodanthonia bipartita Wallaby Grass 1132 WLA(1112), Moree(4), NWB(13), 

BBSpil2(1), Namoi(2) 

Poaceae Astrebla squarrosa 3 Moree(3) 

Poaceae Astrebla pectinata Barley Mitchell 

54 WLA(5), MMVS(1), Moree(43), 

Grass 


Poaceae Astrebla lappacea Curly Mitchell Grass 1225 WLA(1209), Moree(7), NWB(4), 

WFS(5) 

Poaceae Astrebla elymoides 33 Moree(31), WFS(2) 

Poaceae Aristida ramosa var speciosa 5 WLA(2), NWB(2), BBSpil2(1) 

Poaceae Aristida ramosa var scaberula 5 WLA(2), BBSPil(2), NWB(1) 

Poaceae Aristida ramosa var ramosa 1 BBSpil2(1) 

Poaceae Aristida ramosa 109 WLA(105), NWB(4) 

Poaceae Aristida psammophila 100 WLA 

Poaceae Aristida platychaeta 1005 WLA(1001), Moree(3), NWB(1)


Records 

Dataset 

Poaceae Aristida obscura 2WLA(1), NWB(1) 

Poaceae Aristida muricata 7 WLA(2), BBSPil(2), MMVS(1), 

NWB(2) 

Poaceae Aristida longicollis 1WLA 

Poaceae Aristida leptopoda White Speargrass 1021 WLA(1002), Moree(19) 

Poaceae Aristida leichhardtiana 1 Moree(1) 

Poaceae Aristida latifolia 1 Moree(1) 

Poaceae Aristida jerichoensis var 

subspinulifera 

4 WLA(1), NLNRVS(2), BBSpil2(1) 

Poaceae Aristida jerichoensis var jerichoensis 8WLA(4), NWB(4) 

Poaceae Aristida jerichoensis Jericho Wiregrass 8 WLA(3), BBSPil(2), BBSSF&NR(1), 

BBSSF(1), NWB(1) 

Poaceae Aristida holathera var holathera Erect Kerosene 

Grass 

Poaceae Aristida contorta Bunched Kerosene 

Grass 

2WLA 

2WLA 

Poaceae Aristida caput-medusae 1 BBSPil(1) 

Poaceae Aristida calycina 1014 WLA(1007), NWB(7) 

Poaceae Ancistrachne uncinulata Hooked-hairy Panic 

Grass 

26 WLA(25), BBSPil(1) 

Poaceae Amphipogon caricinus var caricinus 1 NLNRVS(1) 

Poaceae Amphipogon caricinus Long Greybeard 

Grass 

2WLA 

Poaceae Agrostis avenacea var avenacea 160 WLA(69), MMVS(15), Moree(18), 


Poaceae Agrostis aemula var aemula 24 NLNRVS(24) 

Poaceae Agrostis aemula Blowngrass 2 WLA 

Key 


RBG Royal Botanic Gardens, Sydney 


BBSSF Forestry survey of the Pillga forests 

Moree Moree Plains Grasslands survey of Moree Plains Shire and Walgett Shire east of the Barwon River 



NH National Herbarium, Canberra 








Namoi Vegetation survey of riparian zones within the Namoi River catchment, north-west New South Wales

Appendix D: Exotic Flora Recorded Within the DRP 

Family Scientific Name Common Name No 

Records 

Dataset 

Ranunculaceae Ranunculus muricatus Sharp Buttercup 2 WLA(1), NWB(1) 

Ranunculaceae Ranunculus sceleratus Celery Buttercup 1 WLA 

Papaveraceae Argemone ochroleuca subsp. 

ochroleuca 

Mexican Poppy 22 WLA (15), Moree(2), NWB(5) 

Papaveraceae Papaver aculeatum 1NWB(1) 

Fumariaceae Fumaria densiflora Narrow-leaved 

Fumitory 

2WLA 

Fumariaceae Fumaria indica Fumitory 4 WLA (2), NWB(2) 

Phytolaccaceae Phytolacca octandra Inkweed 2 WLA(1), NWB(1) 

Portulacaceae Calandrinia menziesii 1WLA 

Aizoaceae Psilocaulon tenue Wiry Noon-flower 1 WLA 

Cactaceae Eriocereus martinii Moonlight Cactus 200 WLA 

Cactaceae Opuntia aurantiaca Tiger Pear 121 WLA(111), NWB(9), BBSpil2(1) 

Cactaceae Opuntia stricta Prickly Pear 69 WLA(33), BBSSF(1), Moree(4), 


Cactaceae Opuntia stricta var stricta Common Prickly Pear 7 WLA(2), BBSPil(4), BBSpil2(1) 

Chenopodiaceae Chenopodium album Fat Hen 4 WLA (2), NWB(1), Namoi(1) 

Chenopodiaceae Chenopodium murale Nettle-leaf Goosefoot 13 WLA (2), MMVS(11) 

Amaranthaceae Alternanthera pungens Khaki Weed 30 WLA (23), MMVS(2), Moree(4), 

Namoi(1) 

Amaranthaceae Amaranthus viridis Green Amaranth 1 WLA (1), Namoi(1) 

Amaranthaceae Gomphrena celosioides Gomphrena Weed 13 WLA(12), Namoi(1) 

Caryophyllaceae Moenchia erecta Erect Chickweed 1 WLA 

Caryophyllaceae Polycarpon tetraphyllum Four-leaved Allseed 1 WLA 

Caryophyllaceae Silene gallica Catchfly 3 WLA 

Caryophyllaceae Spergula arvensis 2 NLNRVS(2) 

Caryophyllaceae Spergularia marina 1 Moree(1) 

Caryophyllaceae Spergularia rubra Sandspurry 19 WLA(8), MMVS(10), NLNRVS(1) 

Caryophyllaceae Stellaria media Common Chickweed 7 WLA(3), MMVS(1), NWB(3) 

Caryophyllaceae Vaccaria hispanica Cow Soapwort 1 MMVS(1) 

Polygonaceae Acetosa vesicaria Bladder Dock 4 WLA 

Polygonaceae Acetosella vulgaris Sorrel, Sheep Sorrel 8 WLA (4), NWB(2), Wombeira(2) 

Polygonaceae Emex australis Spiny Emex 25 WLA(14), Moree(1), NWB(6), 


Polygonaceae Persicaria orientalis 15 MMVS(15) 

Polygonaceae Polygonum arenastrum Wireweed 6 WLA(1), Moree(5) 

Polygonaceae Polygonum aviculare Wireweed 40 WLA(12), Brigfauna(1), 

MMVS(24), NWB(2), Wombeira(1) 

Polygonaceae Polygonum patulum 1 Moree(1) 

Polygonaceae Rumex crispus Curled Dock 5 WLA(2), Moree(3) 

Malvaceae Abutilon theophrasti 4 WLA (1), MMVS (2), Namoi (1) 

Malvaceae Malva neglecta 4 Moree(4) 

Malvaceae Malva sylvestris 1 MMVS(1) 

Malvaceae Malva parviflora Small-flowered Mallow 140 WLA(41), MMVS(86), NWB(12), 

Namoi(1) 

Malvaceae Malva verticillata 1 Moree(1) 

Malvaceae Malvastrum americanum Spiked Malvastrum 226 WLA(67), MMVS(71), Moree(65), 


Malvaceae Modiola caroliniana Red-flowered Mallow 12 WLA(5), Moree(3), NWB(4)


Records 

Dataset 

Malvaceae Pavonia hastata 14 WLA(7), NWB(7) 

Malvaceae Sida rhombifolia Paddy's Lucerne 49 WLA(27), MMVS(15), NWB(5), 

Namoi(2) 

Moraceae Maclura pomifera Osage Orange 2 WLA(1), Namoi(1) 

Urticaceae Urtica urens Small Nettle 11 WLA(5), MMVS(3), NWB(3) 

Euphorbiaceae Chamaesyce prostrata Red Caustic Weed 3 WLA (2), NWB(1) 

Euphorbiaceae Euphorbia peplus Petty Spurge 1 WLA 

Euphorbiaceae Ricinus communis Castor Oil Plant 14 WLA(12), NWB(1), Namoi(1) 

Cucurbitaceae Citrullus colocynthis 9 MMVS(3), Moree(6) 

Cucurbitaceae Citrullus lanatus var lanatus Wild Melon, Camel 

Melon,Bitter 

12 WLA (9), Namoi(2), WFS(1) 

Cucurbitaceae Cucumis myriocarpus subsp Paddy Melon 101 WLA (15), MMVS(45), Moree(39), 

leptodermis 

WFS(2) 

Cucurbitaceae Cucumis zeyheri 3 Moree 

Salicaceae Salix babylonica Weeping Willow 11 WLA(7), NWB(3), Namoi(1) 

Brassicaceae Alyssum linifolium Flax-leaf Alyssum 18 WLA 

Brassicaceae Brassica juncea Indian Mustard 2 WLA (1), Wombeira(1) 

Brassicaceae Brassica rapa subsp. sylvestris Turnip 2 WLA 

Brassicaceae Brassica tournefortii Mediterranean Turnip 25 WLA (20), MMVS(4), Wombeira(1) 

Brassicaceae Capsella bursa-pastoris Shepherd's Purse 11 WLA (3), MMVS(6), Moree(2) 

Brassicaceae Carrichtera annua Ward's Weed 62 WLA 

Brassicaceae Coronopus didymus 1 Moree(1) 

Brassicaceae Diplotaxis muralis Wall Rocket 2 WLA 

Brassicaceae Hirschfeldia incana Buchan Weed 12 WLA(1), Moree(11) 

Brassicaceae Lepidium africanum 4WLA(3), NWB(1) 

Brassicaceae Lepidium bonariense 16 WLA(12), Moree(2), NLNRVS(1), 

NWB(1) 

Brassicaceae Raphanus raphanistrum Wild Radish 2 WLA 

Brassicaceae Rapistrum rugosum Turnip Weed 239 WLA(77), MMVS(15), Moree(86), 

NWB(61) 

Brassicaceae Rorippa palustris Yellow Cress 7 WLA(6), MMVS(1) 

Brassicaceae Sinapis alba White Mustard 1 WLA 

Brassicaceae Sinapis arvensis 12 Moree(8), WFS(4) 

Brassicaceae Sisymbrium irio London Rocket 32 WLA(15), MMVS(5), Moree(4), 

NWB(8) 

Brassicaceae Sisymbrium officinale Hedge Mustard 3 WLA(2), NWB(1) 

Primulaceae Anagallis arvensis Scarlet/Blue Pimpernel 21 WLA (16), MMVS(1), NWB(4) 

Onagraceae Oenothera mollissima 6 NLNRVS(6) 

Onagraceae Oenothera indecora subsp. 

bonariensis 

3 MMVS(3) 

Onagraceae Oenothera rosea 2 Moree(2) 

Onagraceae Ludwigia peploides subsp. 

montevidensis 

Water Primrose 1078 WLA(1024), MMVS(46), 


Anacardiaceae Schinus areira Pepper Tree 8 WLA(6), NWB(1), Namoi(1) 

Meliaceae Melia azedarach White Cedar 5 WLA(3), NWB(1), Namoi(1) 

Fabaceae 


Fabaceae 

(Mimosoideae) 

Fabaceae 

(Faboideae) 

Fabaceae 

(Faboideae) 

Senna occidentalis 3WLA(1), Namoi(2) 

Acacia farnesiana Mimosa Bush 206 WLA(137), Moree(34), NWB(34), 

Namoi(1) 

Lotus uliginosus Birds-foot Trefoil 1 WLA 

Medicago arabica Spotted Burr Medic 15 WLA(7), Moree(1), NWB(7)


Records 

Dataset 

Fabaceae 

Medicago laciniata Cut-leaved Medic 114 WLA(18), MMVS(77), Moree(13), 

(Faboideae) 


Fabaceae 

Medicago minima Woolly Burr Medic 60 WLA(27), MMVS(12), Moree(12), 

(Faboideae) 


Fabaceae 

Medicago polymorpha Burr Medic 353 WLA(124), MMVS(69), Moree(53), 

(Faboideae) 

NWB(105), Namoi(1), 

Wombeira(1) 

Fabaceae 

Medicago praecox Small-leaved Burr 

4WLA(2), NWB(2) 

(Faboideae) 

Medic 

Fabaceae 

(Faboideae) 

Medicago sativa Lucerne 1 WLA 

Fabaceae 

Medicago truncatula Barrel Medic 10 WLA(3), Moree(5), NWB(1), 

(Faboideae) 

WFS(1) 

Fabaceae 

(Faboideae) 

Melilotus indicus Hexham Scent 19 WLA 

Fabaceae 

(Faboideae) 

Vicia monantha subsp. monantha Square-stemmed Vetch 2 WLA 

Fabaceae 

(Faboideae) 

Vicia sativa subsp. angustifolia Narrow-leaved Vetch 1 WLA 

Zygophyllaceae Tribulus terrestris Catshead 225 WLA (122), MMVS(54), 

Moree(30), NWB(16), Namoi(1), 

WFS(2) 

Oxalidaceae Oxalis corniculata Creeping Oxalis 241 WLA(138), MMVS(94), WFS(3), 

Wombeira(6) 

Oxalidaceae Oxalis pes-caprae Soursob 1 WLA 

Geraniaceae Erodium malacoides 6 MMVS(6) 

Apiaceae Ammi majus Bishop's Weed 2 WLA (2), Namoi(2) 

Apiaceae Ammi visnaga 1 MMVS(1) 

Apiaceae Apium graveolens Celery 2 WLA (1), NWB(1) 

Apiaceae Cyclospermum leptophyllum Slender Celery 23 WLA (21), Moree(1), NWB(1) 

Apiaceae Foeniculum vulgare Fennel 8 WLA (4), NWB(4) 

Asteraceae Arctotheca calendula Capeweed 6 WLA 

Asteraceae Aster subulatus Wild Aster 161 WLA (104), MMVS(54), Moree(1), 


Asteraceae Bidens pilosa Cobbler's Pegs 8 WLA (3), Moree(1), NWB(2), 


Asteraceae Bidens subalternans Greater Beggar's Ticks 2 WLA (1), Namoi(1) 

Asteraceae Calendula arvensis 4 Moree(4) 

Asteraceae Carduus tenuiflorus Winged Slender Thistle 1 WLA 

Asteraceae Carthamus lanatus Saffron Thistle 1017 WLA (1004), MMVS(9), Moree(4) 

Asteraceae Carthamus tinctorius 4 Moree(4) 

Asteraceae Centaurea melitensis Maltese Cockspur 1133 WLA (1075), MMVS(31), 


Asteraceae Centaurea solstitialis St Barnabys Thistle 7 WLA (2), NLNRVS(3), NWB(2) 

Asteraceae Centaurea spp. 2WFS(2) 

Asteraceae Chondrilla juncea Skeleton Weed 10 WLA (2), BBSPil(6), Moree(2) 

Asteraceae Chrysanthemoides monilifera Bitou Bush 2 WLA 

Asteraceae Cirsium vulgare Spear Thistle 111 WLA (49), BBSPil(2), MMVS(46), 

Moree(12), NWB(2) 

Asteraceae Conyza albida Tall Fleabane 31 WLA (2), MMVS(21), NLNRVS(6), 

NWB(2) 

Asteraceae Conyza bonariensis Flaxleaf Fleabane 112 WLA (41), BBSPil(5), MMVS(5), 

Moree(54), NWB(3), BBSpil2(1), 

Namoi(3) 

Asteraceae Cotula coronopifolia Water Buttons 4 WLA (1), MMVS(3) 

Asteraceae Dittrichia graveolens Stinkwort 15 WLA 

Asteraceae Hedypnois rhagadioloides subsp. Cretan Weed 25 WLA(18), Moree(6), NWB(1)

Family Scientific Name 

cretica 

Common Name No 

Records 

Asteraceae Helianthus annuus Common Sunflower 1 WLA 

Dataset 

Asteraceae Hypochaeris glabra Smooth Catsear 28 WLA(2), BBSPil(3), MMVS(3), 

Moree(2), NLNRVS(18) 

Asteraceae Hypochaeris radicata Catsear 40 WLA(20), MMVS(14), Moree(1), 

NWB(5) 

Asteraceae Lactuca saligna Willow-leaved Lettuce 8 WLA(1), MMVS(1), Moree(5), 

Namoi(1) 

Asteraceae Lactuca serriola Prickly Lettuce 31 WLA(18), MMVS(4), Moree(1), 


Wombeira(2) 

Asteraceae Leontodon taraxacoides subsp. 

taraxacoides 

Lesser Hawkbit 1 MMVS(1) 

Asteraceae Onopordum acanthium subsp. 

acanthium 

Scotch Thistle 21 WLA (10), MMVS(4), NWB(7) 

Asteraceae Picris hieracioides 1 MMVS(1) 

Asteraceae Silybum marianum Variegated Thistle 36 WLA(19), MMVS(6), Moree(7), 


Asteraceae Sonchus asper subsp. glaucescens Prickly Sowthistle 19 WLA (18), Wombeira(1) 

Asteraceae Sonchus oleraceus Common Sowthistle 217 WLA(70), BBSPil(6), 

BBSSF&NR(1), MMVS(41), 


Wombeira(15) 

Asteraceae Taraxacum officinale Dandelion 21 WLA(11), NWB(8), Wombeira(2) 

Asteraceae Urospermum picroides False Hawkbit 1 WLA 

Asteraceae Verbesina encelioides subsp. Crownbeard 21 WLA(8), MMVS(1), NLNRVS(6), 

encelioides 

NWB(6) 

Asteraceae Xanthium occidentale Noogoora Burr, Cockle 113 WLA(50), MMVS(40), Moree(13), 

Burr 


Asteraceae Xanthium orientale Californian Burr 5 WLA (4), MMVS(1) 

Asteraceae Xanthium spinosum Bathurst Burr 159 WLA(36), MMVS(77), Moree(39), 


WFS(1) 

Solanaceae Cestrum parqui Green Cestrum 1 WLA 

Solanaceae Datura ferox Fierce Thornapple 10 WLA (6), Moree(3), Namoi(1) 

Solanaceae Datura inoxia Downy Thornapple 1 WLA 

Solanaceae Lycium ferocissimum African Boxthorn 112 WLA(65), MMVS(7), Moree(4), 


Solanaceae Nicotiana glauca Tree Tobacco 14 WLA(13), MMVS(1) 

Solanaceae Physalis ixocarpa Ground Cherry 12 WLA(8), MMVS(1), Namoi(3) 

Solanaceae Solanum nigrum Black-berry Nightshade 62 WLA(29), BBSPil(2), MMVS(22), 

Moree(5), NWB(3), Namoi(1) 

Solanaceae Solanum pseudocapsicum Madeira Winter Cherry 4 WLA(2), NWB(2) 

Solanaceae Solanum rostratum Pincushion Nightshade 3 WLA(2), NWB(1) 

Convolvulaceae Convolvulus arvensis 15 Moree(14), WFS(1) 

Convolvulaceae Cuscuta campestris Golden Dodder 1007 WLA (1006), Namoi(1) 

Boraginaceae Amsinckia calycina 4WLA 

Boraginaceae Amsinckia intermedia Common Fiddleneck 1 WLA 

Boraginaceae Buglossoides arvensis Sheepweed 1 WLA 

Boraginaceae Echium plantagineum Patterson's Curse 1040 WLA (1025), BBSPil(1), 


Boraginaceae Heliotropium amplexicaule Blue Heliotrope 20 WLA 

Boraginaceae Heliotropium curassavicum Smooth Heliotrope 22 WLA 

Boraginaceae Heliotropium europaeum Common Heliotrope 3 WLA 

Boraginaceae Heliotropium supinum Prostrate Heliotrope 19 WLA(9), MMVS(8), NWB(2) 

Rubiaceae Galium aparine Goosegrass 4 WLA (2), (2), NWB(2)


Records 

Dataset 

Gentianaceae Centaurium tenuiflorum 10 WLA (10), Wombeira(10) 

Asclepiadaceae Gomphocarpus fruticosus Narrow-leaved Cotton 

Bush 

2WLA(1), Namoi(1) 

Scrophulariaceae Verbascum virgatum Twiggy Mullein 10 WLA (3), MMVS(4), NWB(3) 

Scrophulariaceae Veronica peregrina Wandering Speedwell 1 WLA 

Plantaginaceae Plantago lanceolata Lamb's Tongues 5 WLA(2), Moree(1), Wombeira(2) 

Martyniaceae Ibicella lutea Yellow-flowered Devil's 

Claw 

6 WLA(1), Moree(4), NWB(1) 

Verbenaceae Phyla nodiflora Carpet Weed 10013 WLA 

Verbenaceae Phyla nodiflora var nodiflora Lippia 68 MMVS(44), Moree(12), 


Verbenaceae Verbena aristigera 109 WLA(101), Moree(7), NWB(1) 

Verbenaceae Verbena bonariensis Purpletop 5 WLA(2), MMVS(1), Moree(1), 

Namoi(1) 

Verbenaceae Verbena hispida 2 Moree(2) 

Verbenaceae Verbena officinalis Common Verbena 349 WLA(142), MMVS(43), Moree(94), 


Wombeira(39) 

Verbenaceae Verbena rigida Veined Verbena 4 WLA(1), BBSPil(1), NWB(1), 

Namoi(1) 

Verbenaceae Verbena supina Trailing Verbena 7 WLA 

Callitrichaceae Callitriche stagnalis Common Starwort 1 WLA 

Lamiaceae Lamium amplexicaule Dead Nettle 4 WLA(1), MMVS(2), NWB(1) 

Lamiaceae Marrubium vulgare Horehound 51 WLA(27), MMVS(6), Moree(1), 


Lamiaceae Salvia reflexa Mintweed 11 WLA(3), Moree(7), Namoi(1) 

Lamiaceae Salvia verbenaca Wild Sage 6 WLA(3), MMVS(1), Moree(1), 

NWB(1) 

Lamiaceae Stachys arvensis Stagger Weed 6 WLA(1), MMVS(4), NWB(1) 

Asphodelaceae Asphodelus fistulosus Onion Weed 14 WLA 

Cyperaceae Cyperus aggregatus 2 WLA (1), NWB(1) 

Cyperaceae Cyperus eragrostis 2 BBSSF&NR(1), NLNRVS(1) 

Cyperaceae Cyperus involucratus 1WLA 

Cyperaceae Cyperus rotundus Nutgrass 2 WLA (1), Namoi(1) 

Poaceae Aira cupaniana 5 BBSSF&NR(1), NLNRVS(4) 

Poaceae Alopecurus geniculatus Marsh Foxtail 6 WLA 

Poaceae Alopecurus pratensis Meadow Foxtail 2 WLA (1), NWB(1) 

Poaceae Arundo donax Giant Reed 5 WLA 

Poaceae Avena fatua Wild Oats 7 WLA (1), MMVS(1), Moree(4), 

NWB(1) 

Poaceae Avena ludoviciana Ludo Wild Oats 1 WLA 

Poaceae Avena sativa 1 Moree(1) 

Poaceae Bromus catharticus Prairie Grass 13 WLA (7), Moree(2), NWB(3), 

Namoi(1) 

Poaceae Bromus diandrus Great Brome 1 WLA 

Poaceae Bromus racemosus 1 Moree(1) 

Poaceae Bromus rubens Red Brome 17 WLA 

Poaceae Cenchrus ciliaris Buffel Grass 35 WLA (23), Moree(6), NLNRVS(1), 


Poaceae Cenchrus echinatus Mossman River Grass 3 WLA (2), Namoi(1) 

Poaceae Cenchrus incertus 2WFS(2) 

Poaceae Chloris gayana Rhodes Grass 208 WLA (205), NWB(1), Namoi(2) 

Poaceae Chloris virgata Feathertop Rhodes 

Grass 

10 WLA (2), Moree(8)


Records 

Dataset 

Poaceae Cynodon incompletus 5 MMVS(5) 

Poaceae Echinochloa crusgalli Barnyard Grass 110 WLA (106), NWB(1), Namoi(3) 

Poaceae Ehrharta longiflora Annual Veldtgrass 1 WLA 

Poaceae Eleusine indica Crowsfoot Grass 2 WLA (1), NWB(1) 

Poaceae Eleusine tristachya Goose Grass 1 WLA 

Poaceae Eragrostis cilianensis Stinkgrass 52 WLA (7), MMVS(19), Moree(23), 


Poaceae Eragrostis curvula 23 Moree(23) 

Poaceae Eragrostis pilosa 2 MMVS(1), Moree(1) 

Poaceae Festuca pratensis 1 NLNRVS(1) 

Poaceae Holcus lanatus Yorkshire Fog 1 WFS(1) 

Poaceae Hordeum glaucum Northern Barley Grass 1 WLA 

Poaceae Hordeum leporinum Barley Grass 198 WLA(148), MMVS(13), Moree(18), 


Poaceae Lamarckia aurea Goldentop 5 WLA 

Poaceae Lolium loliaceum Stiff Ryegrass 5 WLA 

Poaceae Lolium rigidum 1 Moree(1) 

Poaceae Panicum capillare Witchgrass 2 WLA(1), Wombeira(1) 

Poaceae Panicum coloratum Coolah Grass 2 WLA(1), Wombeira(1) 

Poaceae Panicum coloratum var 

makarikariense 

2 Moree(2) 

Poaceae Panicum gilvum 1Namoi(1) 

Poaceae Panicum miliaceum 1 MMVS(1) 

Poaceae Parapholis incurva Coast Barb Grass 1 WLA 

Poaceae Paspalum dilatatum Paspalum 8 WLA(4), MMVS(2), Moree(1), 

NWB(1) 

Poaceae Pennisetum villosum Feathertop 1 WLA 

Poaceae Phalaris aquatica Phalaris 2 WLA 

Poaceae Phalaris paradoxa Paradoxa Grass 119 WLA(109), Moree(5), NWB(3), 

Wombeira(2) 

Poaceae Piptatherum miliacea Rice Millet 1 WLA 

Poaceae Poa annua Winter Grass 11 WLA(2), MMVS(9) 

Poaceae Poa pratensis Kentucky Bluegrass 2 WLA(1), WFS(1) 

Poaceae Polypogon monspeliensis Annual Beardgrass 5 WLA(3), Wombeira(2) 

Poaceae Rostraria cristata Annual Cat's Tail 1 WLA 

Poaceae Rostraria pumila Roughtail 8 WLA 

Poaceae Schismus barbatus Arabian Grass 89 WLA 

Poaceae Sorghum halepense Johnson Grass 2 WLA(1), Namoi(1) 

Poaceae Sporobolus indicus 3 Moree(3) 

Poaceae Urochloa panicoides Urochloa Grass 81 WLA(54), Moree(25), Namoi(2) 

Poaceae Vulpia bromoides Squirrel Tail Fesque 2 WLA(1), NWB(1) 

Poaceae Vulpia muralis Rat'sTail Fescue 2 WLA 

Poaceae Vulpia myuros forma megalura Rat'sTail Fescue 1 WLA 

Key 



BBSSF Forestry survey of the Pilliga forests 

Moree Moree Plains Grasslands survey of Moree Plains Shire and Walgett Shire east of the Barwon River










Namoi Vegetation survey of riparian zones within the Namoi River catchment, north-west New South Wales

APPENDIX E: Fauna Other than Those of Conservation Significance 

Recorded Within the DRP 

Common Name Scientific Name No 

Records 

Dataset 

Crinia deserticola 34 WLA 

Plains Froglet Crinia parinsignifera 88 AM (7), WLA (19), CSIRO (4), MD (52), Gwy (6) 

Common Eastern Froglet Crinia signifera 113 AM (31), WLA (63), Bor (15), MD (4) 

Sloane's Toadlet Crinia sloanei 25 AM (2), Cul (1), MD (22) 

Cyclorana cultripes 3 AM (2), WLA (1) 

Cyclorana novaehollandiae 10 WLA 

Water-holding Frog Cyclorana platycephala 54 AM (14), WLA (37), CSIRO (3) 

Cyclorana verrucosa 20 AM (2), WLA (18) 

Eastern Banjo Frog Limnodynastes dumerilii 5 AM (1), WLA (1), MD (3) 

Long-thumbed Frog Limnodynastes fletcheri 7,262 AM (91), WLA (160), CSIRO (2), MD (61), Nara, 

Gwy (6948) 

Giant Banjo Frog Limnodynastes interioris 1WLA 

Ornate Burrowing Frog Limnodynastes interioris 85 AM (18), WLA (67), Boo 

Salmon-striped Frog Limnodynastes salmini 601 AM (34), WLA (96), CSIRO (9), Cul (1), Lum, Nara, 

Gwy (461) 

Spotted Grass Frog Limnodynastes tasmaniensis 2,954 AM (149), WLA (273), CSIRO (9), Bor (10), Boo, Cul 

(2), Lum, Tra (16), MD (189), Nara, Gwy (2306) 

Striped Burrowing Frog Litoria alboguttata 233 AM (12), WLA (211), CSIRO (2), Gwy (8) 

Green Tree Frog Litoria caerulea 395 AM (84), WLA (272), CSIRO (4), Cul (1), MD (8), 

Gwy (26) 

Litoria latopalmata 148 AM (12), WLA (81), CSIRO (1), Gwy (54) 

Peron's Tree Frog Litoria peronii 526 AM (60), WLA (447), CSIRO (4), Cul (1), Lum, Nara, 

Gwy (14) 

Desert Tree Frog Litoria rubella 355 AM (79), WLA (267), CSIRO (7), Cul (1), Lum, Tra 

(1), Gwy (1) 

Common Spadefoot Toad Neobatrachus sudelli 40 AM (8), WLA (29), CSIRO (1), MD (1), Gwy (1) 

Crucifix Frog Notaden bennettii 317 AM (23), WLA (278), CSIRO (5), Bor (9), Boo, Gwy 

(2) 

Bibron's Toadlet Pseudophryne bibronii Nara 

Uperoleia capitulata 22 AM (8), Bor (14) 

Uperoleia rugosa 66 AM (31), WLA (29), CSIRO (6) 

Jacky Lizard Amphibolurus muricatus 7 AM (1), WLA (6) 

Nobbi Amphibolurus nobbi 26 AM (7), WLA (10), CSIRO (9) 

Southern Rainbow Skink Carlia tetradactyla 1CSIRO 

Marbled Gecko Christinus marmoratus 34 WLA (21), MD (13) 

Carnaby's Wall Skink Cryptoblepharus carnabyi 300 AM (112), WLA (131), CSIRO (10), Cul (12), Nar (1), 

Tra (4), MD (3), Gwy (27) 

Cryptoblepharus 

plagiocephalus 

1CSIRO 

Central Netted Dragon Ctenophorus nuchalis 1WLA 

Painted Dragon Ctenophorus pictus 16 AM (2), WLA (14) 

Ctenotus allotropis 18 AM (5), WLA (7), CSIRO (5), Nar (1) 

Ctenotus leonhardii 3 AM (1), WLA (2) 

Ctenotus regius 61 AM (28), WLA (32), MD (1) 

Striped Skink Ctenotus robustus 39 AM (16), WLA (21), CSIRO (1), Lum, Tra (1) 

Ctenotus schomburgkii 1WLA 

Olive Legless Lizard Delma inornata 31 AM (15), WLA (14), CSIRO (1), Cul (1) 

Delma tincta 3 AM (2), WLA (1) 

Yellow-faced Whip Snake Demansia psammophis 20 AM (17), WLA (3) 

De Vis' Banded Snake Denisonia devisi 120 AM (48), WLA (61), CSIRO (10), Cul (1), Gwy (3) 

Spiny-tailed Gecko Diplodactylus ciliaris 8 AM (3), WLA (5) 

Eastern Spiny-tailed Gecko Diplodactylus intermedius 16 AM (5), WLA (9), CSIRO (2) 

Diplodactylus steindachneri 33 AM (3), WLA (26), Nar (1), MD (3) 

Tesselated Gecko Diplodactylus tessellatus 153 AM (36), WLA (85), CSIRO (6), Cul (22), MD (3), 

Gwy (1) 

Stone Gecko Diplodactylus vittatus 30 AM (3), WLA (27) 

Soft-tailed Gecko Diplodactylus williamsi 18 AM (6), WLA (10), CSIRO (2) 

Drysdalia rhodogaster 1AM


Records 

Dataset 

Tree Skink Egernia striolata 275 AM (49), WLA (138), CSIRO (23), Cul (5), Nar (17), 

MD (10), Gwy (33) 

Saw-shelled Tortoise Elseya latisternum 1WLA 

Narrow-banded Sand 

Swimmer 

Eremiascincus fasciolatus 5 AM (1), WLA (4) 

Broad-banded Sand 

Swimmer 

Eremiascincus richardsonii 14 AM (3), WLA (8), MD (3) 

Barred-side Skink Eulamprus tenuis 4WLA 

Red-naped Snake Furina diadema 40 AM (17), WLA (21), CSIRO (1), Gwy (1) 

Furina ornata 1AM 

Gehyra dubia 132 AM (25), WLA (79), Cul (1), Gwy (27) 

Tree Dtella Gehyra variegata 359 AM (163), WLA (116), CSIRO (28), Cul (12), Lum, 

Nar (11), Tra (1), MD (23), Gwy (5) 

Grey Snake Hemiaspis damelii 88 AM (30), WLA (39), CSIRO (12), Gwy (7) 

Bynoe's Gecko Heteronotia binoei 348 AM (92), WLA (167), CSIRO (6), Cul (21), Nar (1), 

MD (2), Gwy (59) 

Grass Skink Lampropholis delicata 1WLA 

Lerista aericeps 3CSIRO 

Lerista labialis 1AM 

Lerista muelleri 95 AM (48), WLA (32), CSIRO (7), Bor (1), Cul (7) 

Lerista punctatovittata 171 AM (53), WLA (22), CSIRO (7), Gwy (2) 

Burton's Legless Lizard Lialis burtonis 36 AM (15), WLA (19), CSIRO (1), Gwy (1) 

Gilbert's Dragon Lophognathus gilberti 77 AM (38), WLA (20), CSIRO (5), Cul (3), Nar (1), Gwy 

(10) 

Beaded Gecko Lucasium damaeum 79 AM (26), WLA (48), MD (5) 

Grey's Skink Menetia greyii 109 AM (40), WLA (36), CSIRO (9), Cul (10), Nar (1), 

Tra (4), MD (9) 

Carpet or Diamond Python Morelia spilota 11 AM (5), WLA (6) 

Morethia adelaidensis 7 AM (3), WLA (4) 

Boulenger's Skink Morethia boulengeri 508 AM (262), WLA (132), CSIRO (17), Bor(1), Cul (14), 

Nar (2), Tra (9), MD (36), Gwy (35) 

Smooth Knob-tailed Gecko Nephrurus levis 10 AM (6), WLA (4) 

Marbled Velvet Gecko Oedura marmorata 44 AM (29), WLA (11), CSIRO (1), Cul (2), Nar (1) 

Eastern Water Dragon Physignathus lesueurii 6WLA 

Bearded Dragon Pogona barbata 127 AM (36), WLA (81), CSIRO (3), Boo, Cul (2), Lum, 

Gwy (5) 

Central Bearded Dragon Pogona vitticeps 25 AM (5), WLA (17), MD (3) 

Mulga Snake Pseudechis australis 44 AM (19), WLA (13), CSIRO (5), MD (7) 

Eastern Brown Snake Pseudonaja textilis 161 AM (100), WLA (54), CSIRO (5), MD (1), Gwy (1) 

Common Scaly-foot Pygopus lepidopodus 4 AM (2), WLA (2) 

Hooded Scaly-foot Pygopus nigriceps 67 AM (32), WLA (33), CSIRO (2) 

Ramphotyphlops 

bituberculatus 

26 AM (10), WLA (14), CSIRO (2) 

Ramphotyphlops ligatus 6 AM (5), WLA (1) 

Ramphotyphlops wiedii 24 AM (12), WLA (12) 

Beaked Gecko Rhynchoedura ornata 34 AM (6), WLA (27), Lum, Nar (1) 

Coral Snake Simoselaps australis 14 AM (6), WLA (6), CSIRO (2) 

Suta spectabilis dwyeri 31 AM (14), WLA (13), CSIRO (3), Gwy (1) 

Curl Snake Suta suta 88 AM (57), WLA (19), CSIRO (7), Cul (3), MD (1), Gwy 

(1) 

Eastern Blue-tongued 

Lizard 

Tiliqua scincoides 134 AM (44), WLA (84), Boo, Lum, Gwy (6) 

Shingleback Trachydosaurus rugosus 133 AM (31), WLA (88), CSIRO (3), Lum, MD (10), Gwy 

(1) 

Lined Earless Dragon Tympanocryptis lineata 37 AM (10), WLA (23), CSIRO (2), Cul (1), Nar (1) 

Tympanocryptis 

tetraporophora 

4 WLA (1), CSIRO (3) 

Thick-tailed Gecko Underwoodisaurus milii 11 AM (5), WLA (6) 

Gould's Goanna Varanus gouldii 73 AM (13), WLA (53), CSIRO (1), Cul (1), Lum, Gwy 

(5) 

Varanus tristis 20 AM (12), WLA (6), CSIRO (1), Nar (1)


Records 

Dataset 

Lace Monitor Varanus varius 223 AM (8), WLA (183), CSIRO (4), Bor(1), Boo, Cul (8), 

MD (8), Gwy (11) 

Spiny-cheeked Honeyeater Acanthagenys rufogularis 532 BA (314), AM (16), WLA (174), Cul (10), Nar (17), 

MD (1), Gwy (1) 

Inland Thornbill Acanthiza apicalis 104 BA (44), ABBBS (1), WLA (32), Cul (2), Lum, MD 

(25) 

Yellow-rumped Thornbill Acanthiza chrysorrhoa 691 BA (479), AM (4), ABBBS (11), WLA (164), CSIRO 

(2), Cul (1), Nar (1), MD (29) 

Yellow Thornbill Acanthiza nana 279 BA (178), ABBBS (2), WLA (86), Bor, Cul (10), Nar 

(3) 

Brown Thornbill Acanthiza pusilla 10 WLA 

Buff-rumped Thornbill Acanthiza reguloides 20 BA (7), WLA (10), Gwy (3) 

Chestnut-rumped Thornbill Acanthiza uropygialis 391 BA (208), AM (9), ABBBS (3), WLA (141), CSIRO 

(1), Cul (8), Lum, MD (21) 

Collared Sparrowhawk Accipiter cirrhocephalus 63 BA (48), WLA (13), Cul (2) 

Brown Goshawk Accipiter fasciatus 105 BA (85), WLA (18), Tra (1), MD (1) 

Grey Goshawk Accipiter novaehollandiae 4 BA (1), AM (1), WLA (2) 

Clamorous Reed-Warbler Acrocephalus stentoreus 314 BA (178), AM (5), ABBBS (1), WLA (112), MD (17), 

Gwy (1) 

Australian Owlet-nightjar Aegotheles cristatus 232 BA (68), AM (5), WLA (122), Cul (24), Lum, Gwy 

(13) 

Azure Kingfisher Alcedo azurea 7 BA (3), AM (2), WLA (2) 

Australian King-Parrot Alisterus scapularis 1BA 

Chestnut Teal Anas castanea 63 BA (22), AM (17), WLA (22), MD (2) 

Grey Teal Anas gracilis 289,110 BA (548), AM (14), ABBBS (2), WLA (286688), Cul 

(3), Lum, Narw (1361), Tra (7), MD (487) 

Australasian Shoveler Anas rhynchotis 6,212 BA (84), AM (3), WLA (6052), Lum, Narw (68), MD 

(5) 

Pacific Black Duck Anas superciliosa 60,194 BA (589), AM (13), WLA (59432), Lum, Narw (85), 

Tra (25), MD (50) 

Darter Anhinga melanogaster 5,119 BA (228), AM (2), ABBBS (6), WLA (4757), Lum, 

Narw (118), Tra (4), MD (4) 

Red Wattlebird Anthochaera carunculata 12 BA (2), WLA (6), Bor, MD (4) 

Richard's Pipit Anthus novaeseelandiae 616 BA (461), AM (5), ABBBS (1), WLA (139), Cul (2), 

Lum, Nar (1), Tra, MD (7) 

Southern Whiteface Aphelocephala leucopsis 304 BA (150), AM (12), WLA (99), Cul (3), MD (40) 

Red-winged Parrot Aprosmictus erythropterus 353 BA (269), AM (9), WLA (272), Bor, Cul (29), Lum, 

Nar (10), MD (7), Gwy (2) 

Wedge-tailed Eagle Aquila audax 536 BA (340), AM (13), WLA (171), Mid, Cul(7), Lum, 

Nar (3), Tra, Gwy (2) 

Intermediate Egret Ardea intermedia 25,575 BA (76), AM (2), ABBBS (4), WLA (25492), Narw 

(6), Tra, Gwy (1) 

White-necked Heron Ardea pacifica 2,370 BA (657), AM (6), WLA (1641), Boo, Cul (6), Lum, 

Narw (15), Tra, MD (36), Gwy (3) 

Black-faced Woodswallow Artamus cinereus 728 BA (542), AM (30), WLA (128), CSIRO (1), Cul (15), 

MD (12) 

Dusky Woodswallow Artamus cyanopterus 180 BA (119), WLA (48), Boo, Cul (6), MD (7) 

White-breasted 

Artamus leucorhynchus 574 BA (285), AM (12), WLA (178), Boo, Cul (60), Lum, 

Woodswallow 

Nar (2), MD (36), Gwy (1) 

Little Woodswallow Artamus minor 112 BA (28), WLA (74), Cul (4), Nar (6) 

Masked Woodswallow Artamus personatus 325 BA (116), AM (11), WLA (191), Cul (6), MD (1) 

White-browed 

Artamus superciliosus 1,166 BA (313), AM (16), WLA (743), Cul (89), Lum, Nar 

Woodswallow 

(4), MD (1) 

Pacific Baza Aviceda subcristata 6 BA (4), AM (1), WLA (1) 

Hardhead Aythya australis 17,527 BA (193), AM (2), WLA (17196), Lum, Narw (91), 

MD (45) 

Mallee Ringneck Barnardius zonarius barnardi 954 BA (493), AM (24), ABBBS (3), WLA (324), Mid, Cul 

(45), Lum, Nar (15), Tra (9), MD (41), Gwy (2) 

Musk Duck Biziura lobata 1,529 BA (106), AM (2), WLA (1421) 

Sulphur-crested Cockatoo Cacatua galerita 538 BA (239), AM (5), ABBBS (2), WLA (204), Mid, Bor, 

Boo, Cul (2), Tra, MD (85), Gwy (1) 

Galah Cacatua roseicapilla 3,058 BA (1160), AM (15), ABBBS (3), WLA (1341),


Records 

Dataset 

CSIRO (2), Mid, Bor, Boo, Cul (69), Lum, Nar (16), 

Tra (>261), MD (188), Gwy (3) 

Little Corella Cacatua sanguinea 391 BA (95), WLA (215), CSIRO (8), MD (73) 

Fan-tailed Cuckoo Cacomantis flabelliformis 47 BA (35), WLA (12) 

Brush Cuckoo Cacomantis variolosus 2 BA (1), WLA (1) 

Yellow-tailed Black- 

Cockatoo 

Calyptorhynchus funereus 1BA 

Black Honeyeater Certhionyx niger 16 BA (5), WLA (11) 

Inland Dotterel Charadrius australis 4 AM (1), WLA (1), CSIRO (2) 

Double-banded Plover Charadrius bicinctus 1WLA 

Red-capped Plover Charadrius ruficapillus 603 BA (6), WLA (442), Narw (154), MD (1) 

Australian Wood Duck Chenonetta jubata 28,519 BA (637), AM (10), ABBBS (3), WLA (26922), Boo, 

Cul (27), Lum, Narw (581), Tra (90), MD (248), Gwy 

(1) 

White-backed Swallow Cheramoeca leucosternus 90 BA (67), WLA (21), Nar (1), MD (1) 

Spotted Bowerbird Chlamydera maculata 300 BA (204), AM (37), ABBBS (6), WLA (49), Nar (3), 

Gwy (1) 

Whiskered Tern Chlidonias hybridus 4,971 BA (69), AM (3), WLA (4407), Lum, Narw (492) 

Horsfield's Bronze-Cuckoo Chrysococcyx basalis 197 BA (141), AM (2), ABBBS (2), WLA (36), Cul (1), 

Nar (2), MD (12), Gwy (1) 

Shining Bronze-Cuckoo Chrysococcyx lucidus 22 BA (7), WLA (8), MD (7) 

Black-eared Cuckoo Chrysococcyx osculans 26 BA (16), AM (1), WLA (8), MD (1) 

Brown Songlark Cinclorhamphus cruralis 214 BA (161), AM (3), WLA (48), MD (2) 

Rufous Songlark Cinclorhamphus mathewsi 367 BA (278), AM (15), ABBBS (1), WLA (69), CSIRO 

(1), MD (3) 

Swamp Harrier Circus approximans 130 BA (95), WLA (35) 

Spotted Harrier Circus assimilis 122 BA (104), WLA (17), Tra, MD (1) 

Golden-headed Cisticola Cisticola exilis 70 BA (51), ABBBS (3), WLA (16) 

Banded Stilt Cladorhynchus leucocephalus 2 BA (1), WLA (1) 

White-browed Treecreeper Climacteris affinis 41 BA (5), AM (1), WLA (10), Cul (4), MD (21) 

Brown Treecreeper Climacteris picumnus 865 BA (479), AM (33), ABBBS (1), WLA (234), CSIRO 

(1), Boo, Cul (51), Nar (8), MD (57), Gwy (1) 

Grey Shrike-thrush Colluricincla harmonica 802 BA (444), AM (4), WLA (189), CSIRO (1), Boo, Cul 

(40), Lum, Nar (17), MD (105), Gwy (2) 

Ground Cuckoo-shrike Coracina maxima 181 BA (129), AM (2), WLA (50) 

Black-faced Cuckoo-shrike Coracina novaehollandiae 1,032 BA (743), AM (5), WLA (193), Bor, Boo, Cul (22), 

Nar (16), Tra, MD (49), Gwy (4) 

White-bellied Cuckooshrike 

Coracina papuensis 167 BA (84), AM (1), WLA (58), Cul (10), Nar (5), MD (9) 

Cicadabird Coracina tenuirostris 2WLA 

White-winged Chough Corcorax melanorhamphos 1,296 BA (581), AM (28), WLA (544), Bor, Boo, Cul (12), 

Lum, Nar (1), Tra (52), MD (77), Gwy (1) 

White-throated Treecreeper Cormobates leucophaeus 31 BA (4), AM (4), ABBBS (3), WLA (2), MD (18) 

Little Crow Corvus bennetti 299 BA (101), WLA (184), CSIRO (4), Cul (2), MD (8) 

Australian Raven Corvus coronoides 1,664 BA (732), AM (12), WLA (378), CSIRO (1), Bor, Cul 


Little Raven Corvus mellori 1,272 BA (92), WLA (1112), CSIRO (3), Mid, Cul (4), Tra 

(>61) 

Torresian Crow Corvus orru 9 BA (1), AM (3), WLA (5) 

King Quail Coturnix chinensis 1WLA 

Stubble Quail Coturnix pectoralis 95 BA (56), AM (16), WLA (23) 

Pied Butcherbird Cracticus nigrogularis 1,328 BA (1012), AM (25), ABBBS (1), WLA (231), CSIRO 

(2), Mid, Bor, Cul (26), Lum, Nar (14), Tra (7), MD 

(15), Gwy (2) 

Grey Butcherbird Cracticus torquatus 698 BA (484), AM (6), ABBBS (2), WLA (145), Bor, Cul 

(16), Nar (5), Tra, MD (31), Gwy (2) 

Pallid Cuckoo Cuculus pallidus 272 BA (209), AM (4), WLA (55), MD (4) 

Black Swan Cygnus atratus 24,031 BA (298), AM (2), ABBBS (2), WLA (24331), Lum, 

Narw (355), Tra, MD (43) 

Laughing Kookaburra Dacelo novaeguineae 917 BA (650), AM (14), ABBBS (1), WLA (189), Mid, Bor, 

Boo, Cul (11), Lum, Nar (2), Tra (1), MD (45), Gwy 

(4)


Records 

Dataset 

Varied Sittella Daphoenositta chrysoptera 71 BA (10), AM (1), WLA (24), CSIRO (3), MD (33) 

Wandering Whistling-Duck Dendrocygna arcuata 42 BA (1), AM (2), WLA (39) 

Plumed Whistling-Duck Dendrocygna eytoni 29,814 BA (76), AM (4), WLA (29719), Lum, Tra (15) 

Mistletoebird Dicaeum hirundinaceum 538 BA (379), AM (7), WLA (99), CSIRO (1), Mid, Cul 

(22), Nar (9), MD (18), Gwy (3) 

Spangled Drongo Dicrurus bracteatus 4WLA 

Emu Dromaius novaehollandiae 3,257 BA (597), AM (14), WLA (2583), Mid, Bor, Cul (53), 

Lum, MD (5), Gwy (5) 

Little Egret Egretta garzetta 1,550 BA (79), WLA (1470), CSIRO (1) 

White-faced Heron Egretta novaehollandiae 4,364 BA (790), AM (6), WLA (3363), Cul (7), Lum, Narw 

(159), Tra (1), MD (36), Gwy (2) 

Black-shouldered Kite Elanus axillaris 311 BA (254), AM (4), WLA (48), Mid, Tra, MD (5) 

Black-fronted Dotterel Elseyornis melanops 2,436 BA (345), AM (14), ABBBS (6), WLA (2011), Boo, 

Cul (9), Lum, Narw (19), MD (32) 

Blue-faced Honeyeater Entomyzon cyanotis 461 BA (337), AM (7), WLA (103), Cul (5), Tra (3), MD 

(3), Gwy (3) 

Eastern Yellow Robin Eopsaltria australis 70 BA (40), AM (3), ABBBS (3), WLA (22), Bor, Lum, 

Nar (2) 

White-fronted Chat Epthianura albifrons 250 BA (99), AM (8), WLA (140), Lum, Nar (3) 

Orange Chat Epthianura aurifrons 56 WLA 

Crimson Chat Epthianura tricolor 170 BA (63), AM (7), WLA (100) 

Red-kneed Dotterel Erythogonys cinctus 2,881 BA (111), AM (6), WLA (2606), CSIRO (1), Narw 

(142), MD (15) 

Spotted Nightjar Eurostopodus argus 24 BA (14), WLA (10), Lum 

Dollarbird Eurystomus orientalis 123 BA (107), ABBBS (1), WLA (15) 

Brown Falcon Falco berigora 542 BA (412), AM (4), ABBBS (1), WLA (119), CSIRO 

(2), Bor, Cul (1), Lum, Nar (1), Tra, MD (2) 

Nankeen Kestrel Falco cenchroides 1,180 BA (944), AM (19), ABBBS (1), WLA (179), CSIRO 

(1), Cul (26), Nar (6), Tra (1), MD (2), Gwy (1) 

Australian Hobby Falco longipennis 210 BA (157), WLA (50), Bor, Cul (1), Nar (1), Tra, Gwy 

(1) 

Peregrine Falcon Falco peregrinus 51 BA (27), AM (1), ABBBS (1), WLA (18), CSIRO (2), 

Tra (1), MD (1) 

Black Falcon Falco subniger 76 BA (52), WLA (24) 

Eurasian Coot Fulica atra 95,389 BA (243), AM (6), ABBBS (1), WLA (94757), Lum, 

Narw (341), Tra (1), MD (40) 

Dusky Moorhen Gallinula tenebrosa 914 BA (143), AM (1), WLA (762), MD (8) 

Black-tailed Native-hen Gallinula ventralis 7,719 BA (132), AM (4), WLA (5761), Lum, Narw (1733), 

Tra (3), MD (86) 

Buff-banded Rail Gallirallus philippensis 16 BA (1), AM (3), WLA (12) 

Diamond Dove Geopelia cuneata 150 BA (66), AM (7), WLA (62), Lum, MD (15) 

Bar-shouldered Dove Geopelia humeralis 184 BA (104), AM (1), WLA (72), Nar (6), Gwy (1) 

Peaceful Dove Geopelia striata 823 BA (472), AM (12), WLA (284), Bor, Boo, Cul (11), 

Nar (4), MD (39), Gwy (1) 

Western Gerygone Gerygone fusca 201 BA (111), AM (3), ABBBS (2), WLA (34), Bor, Boo, 

Cul (1), Lum, MD (50) 

White-throated Gerygone Gerygone olivacea 20 BA (7), WLA (10), Mid, Boo, Gwy (3) 

Little Lorikeet Glossopsitta pusilla 2BA 

Magpie-lark Grallina cyanoleuca 2,219 BA (1266), AM (14), ABBBS (7), WLA (674), CSIRO 

(1), Bor, Cul (53), Lum, Nar (10), Tra (14), MD (176), 

Gwy (4) 

Australian Magpie Gymnorhina tibicen 1,862 BA (1172), AM (9), ABBBS (3), WLA (436), CSIRO 

(2), Mid, Bor, Boo, Cul (83), Lum, Nar (20), Tra (38), 

MD (99), Gwy (3) 

Whistling Kite Haliastur sphenurus 731 BA (471), AM (8), ABBBS (1), WLA (217), CSIRO 

(2), Cul (7), Lum, Nar (4), MD (25) 

Little Eagle Hieraaetus morphnoides 200 BA (132), WLA (45), Bor, Boo, Nar (1), MD (21), 

Gwy (1) 

Black-winged Stilt Himantopus himantopus 11,035 BA (188), AM (4), WLA (10189), Lum, Narw (649), 

Tra (5) 

Fairy Martin Hirundo ariel 808 BA (322), WLA (428), CSIRO (1), Cul (2), MD (55) 

Welcome Swallow Hirundo neoxena 1,835 BA (678), AM (6), ABBBS (1), WLA (1037), Cul (30),


Records 

Dataset 

Lum, Nar (3), Tra (>30), MD (49), Gwy (1) 

Tree Martin Hirundo nigricans 849 BA (452), AM (2), WLA (310), Cul (18), Nar (5), MD 

(61), Gwy (1) 

Chestnut-rumped 

Heathwren 

Hylacola pyrrhopygia 2BA 

White-winged Triller Lalage sueurii 343 BA (223), AM (23), WLA (91), Bor, Lum, MD (6) 

Silver Gull Larus novaehollandiae 3,772 BA (158), AM (1), ABBBS (1), WLA (3585), Narw 

(21), MD (6) 

Franklin's Gull Larus pipixcan 1WLA 

Yellow-faced Honeyeater Lichenostomus chrysops 11 BA (5), AM (2), ABBBS (3), WLA (1) 

Fuscous Honeyeater Lichenostomus fuscus 3 BA (1), AM (1), Gwy (1) 

White-eared Honeyeater Lichenostomus leucotis 6 BA (2), MD (4) 

Yellow-plumed Honeyeater Lichenostomus ornatus 20 BA (4), AM (1), WLA (15) 

White-plumed Honeyeater Lichenostomus penicillatus 2,528 BA (760), AM (40), ABBBS (10), WLA (1017), Mid, 

Bor, Cul (220), Lum, Nar (25), Tra (21), MD (435) 

Grey-fronted Honeyeater Lichenostomus plumulus 5 BA (1), AM (3), MD (1) 

Singing Honeyeater Lichenostomus virescens 276 BA (202), AM (6), WLA (63), Boo, Cul (2), Nar (2), 

MD (1) 

Brown Honeyeater Lichmera indistincta 19 BA (6), WLA (7), Boo, MD (6) 

Chestnut-breasted 

Mannikin 

Lonchura castaneothorax 1WLA 

Pink-eared Duck Malacorhynchus 

40,321 BA (104), AM (4), WLA (38863), Lum, Narw (1325), 

membranaceus 

MD (25) 

Superb Fairy-wren Malurus cyaneus 487 BA (143), AM (4), ABBBS (20), WLA (139), MD 

(179), Gwy (2) 

Variegated Fairy-wren Malurus lamberti 509 BA (223), ABBBS (1), WLA (129), Mid, Cul (8), Nar 

(11), MD (137) 

White-winged Fairy-wren Malurus leucopterus 495 BA (311), AM (11), ABBBS (60), WLA (106), Cul (1), 

Nar (6), MD (16) 

Splendid Fairy-wren Malurus splendens 49 BA (9), AM (1), WLA (35), Nar (4) 

Yellow-throated Miner Manorina flavigula 1,673 BA (861), AM (30), ABBBS (8), WLA (631), CSIRO 

(5), Cul (111), Nar (7), MD (20) 

Noisy Miner Manorina melanocephala 1,190 BA (442), AM (5), ABBBS (57), WLA (314), Mid, Bor, 

Boo, Lum, Tra (>179), MD (187), Gwy (6) 

Little Grassbird Megalurus gramineus 134 BA (86), AM (7), ABBBS (2), WLA (39) 

Tawny Grassbird Megalurus timoriensis 5BA 

Brown-headed Honeyeater Melithreptus brevirostris 122 BA (32), AM (1), ABBBS (3), WLA (31), Lum, MD 

(55) 

White-naped Honeyeater Melithreptus lunatus 3 WLA (1), Boo, Tra (1), Gwy (1) 

Budgerigar Melopsittacus undulatus 2,146 BA (81), AM (10), WLA (2040), CSIRO (1), Cul (4), 

Nar (2), MD (8) 

Rainbow Bee-eater Merops ornatus 555 BA (197), AM (54), WLA (295), Boo, Cul (1), Lum, 

MD (7), Gwy (1) 

Jacky Winter Microeca fascinans 756 BA (439), AM (9), ABBBS (3), WLA (194), CSIRO 

(2), Mid, Bor, Boo, Cul (46), Lum, Nar (16), MD (46), 

Gwy (1) 

Black Kite Milvus migrans 573 BA (326), AM (2), ABBBS (7), WLA (195), Tra, MD 

(42), Gwy (1) 

Singing Bushlark Mirafra javanica 173 BA (111), AM (5), WLA (54), CSIRO (2), Cul (1) 

Satin Flycatcher Myiagra cyanoleuca 5 BA (2), WLA (3) 

Restless Flycatcher Myiagra inquieta 557 BA (418), AM (11), WLA (106), Cul (14), Nar (6), MD 

(2) 

Leaden Flycatcher Myiagra rubecula 11 BA (3), WLA (7), MD (1) 

Plum-headed Finch Neochmia modesta 445 BA (47), WLA (398) 

Red-browed Finch Neochmia temporalis 7 BA (1), AM (3), ABBBS (2), WLA (1) 

Blue-winged Parrot Neophema chrysostoma 15 BA (3), WLA (2), MD (10) 

Green Pygmy-Goose Nettapus pulchellus 2WLA 

Southern Boobook Ninox novaeseelandiae 122 BA (76), ABBBS (3), WLA (38), CSIRO (1), Bor, Cul 

(2), Lum, MD (2), Gwy (1) 

Blue Bonnet Northiella haematogaster 1,182 BA (679), AM (33), WLA (389), CSIRO (16), Cul (5), 

Lum, Nar (1), Tra (18), MD (39), Gwy (3) 

Nankeen Night Heron Nycticorax caledonicus 19,573 BA (142), AM (5), ABBBS (2), WLA (19409), Cul (2),


Records 

Dataset 

Narw (10), MD (2), Gwy (1) 

Cockatiel Nymphicus hollandicus 1,420 BA (717), AM (16), WLA (660), CSIRO (2), Cul (13), 

Lum, Nar (9), Tra (21), Gwy (3) 

Crested Pigeon Ocyphaps lophotes 1,783 BA (1009), AM (42), ABBBS (3), WLA (507), Mid, 

Bor, Boo, Cul (66), Lum, Nar (12), Tra (58), MD (80), 

Gwy (6) 

Crested Bellbird Oreoica gutturalis 311 BA (168), AM (2), WLA (105), Cul (20), Lum, Nar 

(3), MD (13) 

Rufous Whistler Pachycephala rufiventris 510 BA (337), AM (1), ABBBS (2), WLA (134), Mid, Cul 


Spotted Pardalote Pardalotus punctatus 36 BA (27), WLA (9) 

Yellow-rumped Pardalote Pardalotus punctatus 

xanthopygus 

1BA 

Striated Pardalote Pardalotus striatus 650 BA (474), AM (3), ABBBS (3), WLA (120), CSIRO 

(1), Bor, Cul (5), Nar (7), MD (37) 

Australian Pelican Pelecanus conspicillatus 50,481 BA (385), AM (4), ABBBS (6), WLA (45620), Boo, 

Cul (1), Lum, Narw (4230), Tra (1), MD (234) 

Red-capped Robin Petroica goodenovii 418 BA (223), AM (9), ABBBS (4), WLA (120), Boo, Cul 

(3), Lum, Nar (6), MD (53) 

Scarlet Robin Petroica multicolor 3 BA (2), WLA (1) 

Flame Robin Petroica phoenicea 4 BA (1), AM (3) 

Great Cormorant Phalacrocorax carbo 3,326 BA (315), ABBBS (103), WLA (2346), CSIRO (2), 

Cul (1), Narw (310), MD (249) 

Little Pied Cormorant Phalacrocorax melanoleucos 15,185 BA (340), AM (5), WLA (14819), Narw (3), Tra (2), 

MD (16) 

Little Black Cormorant Phalacrocorax sulcirostris 14,660 BA (313), AM (3), ABBBS (1), WLA (14135), Narw 

(28), Tra (21), MD (159) 

Pied Cormorant Phalacrocorax varius 2,107 BA (121), ABBBS (82), WLA (1095), Lum, Narw 

(781), MD (28) 

Common Bronzewing Phaps chalcoptera 262 BA (121), ABBBS (2), WLA (109), Cul (12), Lum, 

Nar (4), MD (13), Gwy (1) 

Little Friarbird Philemon citreogularis 772 BA (375), AM (9), WLA (227), CSIRO (1), Mid, Bor, 

Cul (17), Lum, Nar (15), Tra (3), MD (126) 

White-fronted Honeyeater Phylidonyris albifrons 17 BA (9), WLA (8) 

Yellow-billed Spoonbill Platalea flavipes 10,162 BA (502), AM (4), ABBBS (2) WLA (9431), Lum, 

Narw (267), Tra (6), MD (28), Gwy (2) 

Royal Spoonbill Platalea regia 11,246 BA (164), AM (1), ABBBS (3), WLA (10948), Lum, 

Narw (124), Tra (3), MD (3) 

Pale-headed Rosella Platycercus adscitus 181 BA (72), AM (2), WLA (99), Mid, Bor, Cul (4), Lum, 

Nar (1), Gwy (3) 

Crimson Rosella Platycercus elegans 8 BA (1), WLA (1), MD (6) 

Yellow Rosella Platycercus elegans flaveolus 287 BA (24), WLA (12), MD (251) 

Eastern Rosella Platycercus eximius 108 BA (60), AM (4), ABBBS (2), WLA (19), CSIRO (2), 

Tra (19), Gwy (2) 

Striped Honeyeater Plectorhyncha lanceolata 399 BA (288), AM (13), ABBBS (2), WLA (91), Bor, Cul 

(5), Lum, Nar (5) 

Tawny Frogmouth Podargus strigoides 223 BA (150), AM (4), WLA (48), Boo, Cul (12), Lum, 

Tra, MD (1), Gwy (8) 

Great Crested Grebe Podiceps cristatus 527 BA (56), AM (2), WLA (469) 

Hoary-headed Grebe Poliocephalus poliocephalus 10,064 BA (122), AM (1), WLA (9881), Narw (51), Tra, MD 

(9) 

Chestnut-crowned Babbler Pomatostomus ruficeps 199 BA (120), AM (9), WLA (52), MD (18) 

White-browed Babbler Pomatostomus superciliosus 636 BA (69), AM (1), WLA (552), Mid, Cul (3), Lum, MD 

(11) 

Purple Swamphen Porphyrio porphyrio 8,871 BA (126), AM (1), WLA (8740), Narw (2), Tra (1), 

MD (1) 

Australian Spotted Crake Porzana fluminea 16 BA (4), AM (6), WLA (5), Narw (1) 

Baillon's Crake Porzana pusilla 18 BA (3), AM (7), WLA (8) 

Spotless Crake Porzana tabuensis 11 BA (5), WLA (6) 

Red-rumped Parrot Psephotus haematonotus 1,711 BA (720), AM (15), ABBBS (4), WLA (559), CSIRO 

(1), Mid, Bor, Boo, Cul (114), Nar (1), Tra (28), MD 

(267), Gwy (3)


Records 

Dataset 

Mulga Parrot Psephotus varius 179 BA (61), AM (10), WLA (83), Cul (7), Lum, Nar (2), 

MD (16) 

Chirruping Wedgebill Psophodes cristatus 84 BA (41), AM (1), WLA (39), MD (3) 

Red-necked Avocet Recurvirostra 

13,754 BA (16), AM (1), WLA (13321), Lum, Narw (411), 

novaehollandiae 

MD (5) 

Grey Fantail Rhipidura fuliginosa 301 BA (199), ABBBS (13), WLA (77), CSIRO (3), Bor, 

Cul (3), Lum, Nar (1), Tra (4), Gwy (1) 

Willie Wagtail Rhipidura leucophrys 1,758 BA (1059), AM (13), ABBBS (3), WLA (444), Bor, 

Boo, Cul (56), Lum, Nar (23), Tra (7), MD (148), 

Gwy (5) 

Rufous Fantail Rhipidura rufifrons 2 BA (1), WLA (1) 

Channel-billed Cuckoo Scythrops novaehollandiae 3 BA (2), WLA (1) 

White-browed Scrubwren Sericornis frontalis 2 ABBBS 

Weebill Smicrornis brevirostris 630 BA (337), AM (10), ABBBS (1), WLA (121), CSIRO 

(5), Cul (19), Nar (1), MD (134), Gwy (2) 

Gull-billed Tern Sterna nilotica 1,549 BA (22), WLA (1527) 

Australian Pratincole Stiltia isabella 66 BA (37), AM (2), WLA (29) 

Pied Currawong Strepera graculina 27 BA (23), AM (1), WLA (3) 

Apostlebird Struthidea cinerea 1,932 BA (724), AM (48), ABBBS (23), WLA (1004), 

CSIRO (1), Mid, Bor, Cul (11), Lum, Tra (69), MD 

(47), Gwy (5) 

Australasian Grebe Tachybaptus novaehollandiae 3,912 BA (258), AM (6), WLA (3541), Lum, Narw (99), Tra 

(8) 

Australian Shelduck Tadorna tadornoides 1,347 BA (51), ABBBS (1), WLA (1272), MD (23) 

Double-barred Finch Taeniopygia bichenovii 472 BA (242), AM (9), ABBBS (8), WLA (211), Bor, Gwy 

(2) 

Zebra Finch Taeniopygia guttata 651 BA (320), AM (12), ABBBS (12), WLA (305), Nar (1), 

Tra, Gwy (1) 

Australian White Ibis Threskiornis molucca 580,807 BA (385), AM (6), WLA (580284), CSIRO (4), Cul 

(1), Lum, Narw (48), Tra, MD (78), Gwy (1) 

Straw-necked Ibis Threskiornis spinicollis 862,349 BA (512), AM (5), ABBBS (6), WLA (861628), 

CSIRO (12), Lum, Narw (177), Tra, MD (8), Gwy (1) 

Forest Kingfisher Todiramphus macleayii 1WLA 

Red-backed Kingfisher Todiramphus pyrrhopygia 124 BA (92), AM (10), WLA (15), MD (7) 

Sacred Kingfisher Todiramphus sanctus 56 BA (322), AM (7), ABBBS (2), WLA (107), CSIRO 

(3), Boo, Cul (9), Lum, MD (8), Gwy (3) 

Scaly-breasted Lorikeet Trichoglossus chlorolepidotus 6WLA 

Rainbow Lorikeet Trichoglossus haematodus 4 BA (2), WLA (2) 

Painted Button-quail Turnix varia 3 BA (1), AM (1), WLA (1) 

Little Button-quail Turnix velox 36 BA (13), AM (2), WLA (21) 

Barn Owl Tyto alba 70 BA (38), AM (2), WLA (24), CSIRO (1), Tra, Gwy (5) 

Masked Lapwing Vanellus miles 5,178 BA (562), AM (7), WLA (4262), Mid, Lum, Narw 

(284), Tra (14), MD (48), Gwy (1) 

Banded Lapwing Vanellus tricolor 880 BA (226), AM (6), WLA (628), Cul (1), Lum, Narw 

(14), MD (5) 

Silvereye Zosterops lateralis 71 BA (30), ABBBS (10), WLA (30), Mid, MD (1) 

Gould's Wattled Bat Chalinolobus gouldii 205 AM (88), WLA (48), Cul (4), Nar (4), MD (58), Gwy 

(3) 

Water Rat Hydromys chrysogaster 58 AM (5), WLA (38), Cul (1), MD (10), Gwy (4) 

Northern Brown Bandicoot Isoodon macrourus 6 AM (2), WLA (4) 

Western Grey Kangaroo Macropus fuliginosus 382 WLA (311), CSIRO (4), MD (67) 

Eastern Grey Kangaroo Macropus giganteus 1,750 AM (14), WLA (1420), CSIRO (4), Mid, Bor(55), Boo, 

Cul (207), Lum, Nar (18), MD (15), Gwy (17) 

Common Wallaroo Macropus robustus 35 WLA (19), CSIRO (3), Tra (1), MD (11), Gwy (1) 

Red-necked Wallaby Macropus rufogriseus 3WLA(3), Mid 

Red Kangaroo Macropus rufus 833 AM (22), WLA (630), CSIRO (142), Boo, Cul (25), 

Lum, Nar (6), MD (3), Gwy (5) 

Little Freetail Bat Mormopterus loriae 7 AM (1), Cul (1), Nar (5) 

Little Mastiff-bat Mormopterus planiceps 31 AM (4), WLA (22), MD (4), Gwy (1) 

Mormopterus sp. (big penis) 29 WLA (1), MD (28) 

Mormopterus sp. (little penis) 58 WLA (51), MD (7) 

White-striped Mastiff-bat Nyctinomus australis 76 AM (50), WLA (14), MD (12)


Records 

Dataset 

Lesser Long-eared Bat Nyctophilus geoffroyi 127 AM (29), WLA (71), Cul (10), Nar (2), MD (10), Gwy 

(5) 

Paucident Planigale Planigale gilesi 55 AM (13), WLA (26), CSIRO (3), Cul (8), MD (5) 

Narrow-nosed Planigale Planigale tenuirostris 46 AM (5), WLA (21), CSIRO (5), Cul (7), Nar (6), Gwy 

(2) 

Little Red Flying-fox Pteropus scapulatus 5,719 AM (2), WLA (5716), Gwy (1) 

Western Broad-nosed Bat Scotorepens balstoni 45 AM (4), WLA (36), Nar (1), MD (2), Gwy (2) 

Little Broad-nosed Bat Scotorepens greyii 97 AM (22), WLA (50), Cul (15), MD (9), Gwy (1) 

Fat-tailed Dunnart Sminthopsis crassicaudata 146 AM (59), WLA (64), CSIRO (3), Cul (15), Lum, Nar 

(4), Tra (1) 

Common Dunnart Sminthopsis murina 4 AM (2), WLA (2) 

Short-beaked Echidna Tachyglossus aculeatus 47 WLA (40), Boo, Cul (1), Lum, Nar (1), MD (2), Gwy 

(3) 

Little Forest Eptesicus Vespadelus vulturnus 117 AM (20), WLA (34), Cul (14), Nar (9), MD (33), Gwy 

(7) 

Common Wombat Vombatus ursinus 1WLA 

WLA = Atlas of NSW Wildlife 

AM = Australian Museum 

CSIRO = CSIRO dataset 

BA = Birds Australia 

ABBBS = Australian Bird and Bat Banding Scheme 

Mid = Midkin NR Flora Fauna Survey 

Bor = Boronga NR Biodiversity Survey 

Boo = Boomi and Boomi West NRs Survey 

Cul = Culgoa and Birrie River Floodplain Vertebrate Fauna Survey 

Lum = Lumeah (Narran Lake NR) Biodiversity Survey 

Nar = Vertebrate Fauna Survey of Narran River Floodplain 

Narw = Narran Lake NR Waterbird Monitoring Program 

Tra = Trangie Agricultural Research Centre - Faunal Biodiversity Survey 

MD = Murray Darling Water Management Action Plan - Natural Resources Study 

Nara = Narran Lake Amphibian Survey 

Gwy = Fauna Survey for the Gwydir Watercourse

Appendix F – Waterbird Survey Data for Menindee Lakes and Macquarie Marshes 

(Kingsford et al) 

Menindee Lakes Data 

Common 1983 1984 1985 1986 1987 1988 1989 1990 1991 1992 1993 1995 1996 1997 1998 1999 2000 2001 Total Smallest Year Largest Year 

Name 

Individuals Value Recorded Value Recorded 

Australasian 

Shoveler 

2 24 4 2 22 71 20 145 2 1985, 1992 71 1997 

Australian 

Pelican 

1574 1798 2946 276 2900 1128 134 384 969 573 1020 163 282 410 306 190 183 414 15650 134 1989 2946 1985 

Australian 

Shelduck 

178 7 4 19 7 8 5 220 20 279 2 144 114 6 1013 2 1996 279 1995 

Australian White 

Ibis 

2 1 4 2 9 1 1992 4 1995 

Australian 

Wood Duck 

76 533 100 57 257 80 25 50 1178 25 1998 533 1985 

Banded 

Lapwing 

6 6 6 1987 6 1987 

Banded Stilt 82 82 82 1995 82 1995 

Black Swan 52 584 12 18 166 7 7 41 33 68 1360 40 12 193 34 1 9 2637 1 2000 1360 1995 

Black-tailed 

Native-hen 

690 4 61 1743 11 4 88 2601 4 1990, 1998 1743 1995 

Black-winged 

Stilt 

1 10 45 4 1690 1750 1 1985 1690 1995 

Caspian Tern 70 14 44 1 158 8 14 309 1 1993 158 1995 

Darter 16 11 48 2 5 7 6 11 2 12 27 8 6 19 180 2 1987, 1995 48 1985 

Egrets 3 59 2 120 22 142 4 72 4 4 30 462 2 1986 142 1995 

Eurasian Coot 36 2414 207 2780 29 27 55 1655 224 14 60 84 7585 14 1998 2780 1987 

Freckled Duck 2 20 25 27 3 11 2 90 2 1983, 1999 27 1992 

Glossy Ibis 32 231 263 32 1983 231 1995 

Great 

Cormorant 

292 259 3 48 628 292 33 10 92 36 13 3 2 3 4 14 10 33 1775 2 1996 628 1987 

Great Crested 

Grebe 

34 11 4 1 3 53 1 1993 34 1984 

Great Egret 3 1 5 3 2 20 17 2 53 1 1988 20 1999 

Grey Teal 202 962 273 8 50 7 18 108 605 452 276 44923 151 2 842 28 70 48977 2 1998 44923 1995

Common 1983 1984 1985 1986 1987 1988 1989 1990 1991 1992 1993 1995 1996 1997 1998 1999 2000 2001 Total Smallest Year Largest Year 

Name 

Individuals Value Recorded Value Recorded 

Gull-billed Tern 13 17 2 32 2 2000 17 1995 

Hardhead 17 486 5 190 10 479 1138 110 9 5 2449 5 1989, 2001 1138 1995 

Little Black 

Cormorant 

48 3164 839 650 885 221 20 2 570 222 32 27 10 224 7 1175 8096 2 1990 3164 1984 

Little Pied 

Cormorant 

1347 36 73 625 8 3 34 104 15 53 71 116 16 12 2513 3 1990 1347 1983 

Masked 

Lapwing 

10 2 2 126 140 2 1991, 1992 126 1995 

Musk Duck 1 6 8 2 10 27 1 1983 10 1991 

Pacific Black 

Duck 

6 132 47 4 35 48 353 418 472 109 6 72 72 1774 4 1987 472 1995 

Pied Cormorant 907 1650 42 624 256 72 105 176 68 1465 92 106 123 4 32 218 227 6167 4 1998 1650 1985 

Pink-eared 

Duck 

11 312 449 4 197 169 13832 167 280 250 15671 4 1990 13832 1995 

Purple 

Swamphen 

709 709 709 1995 709 1995 

Red-necked 

Avocet 

144 46 2220 2410 46 1991 2220 1995 

Royal Spoonbill 48 4 1 3 5 61 1 1990 48 1983 

Silver Gull 340 399 148 86 138 36 7 61 127 65 55 742 84 2 12 27 2 2331 2 1997, 2001 742 1995 

Small Grebes 1 12 13 1 1983 12 1990 

Small Waders 5 200 13 5798 7 6023 5 1985 5798 1995 

Straw-necked 

Ibis 

6 4 1 4 0 20 3 38 1 1988 20 2000 

Terns 2 2 2 1999 2 1999 

Whiskered Tern 16 10 90 32 1 62 60 271 1 1993 90 1987 

White-faced 

6 1 19 1 1 3 2 1 34 1 1987, 1991, 19 1990 

Heron 

1992, 2000 

White-necked 

Heron 

13 6 19 6 1991 13 1990 

Yellow-billed 

Spoonbill 

35 28 12 280 6 3 101 7 17 503 2 10 12 3 4 1023 2 1996 503 1995 

Grand Total 4330 11549 8214 1223 9530 1986 365 1078 3675 3154 3120 78177 591 1751 776 2148 543 2411 134621 365 1989 78177 1995

Common 

Name 

Macquarie Marshes Data 

1983 1984 1985 1986 1987 1988 1989 1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 Total 

Individuals 

Smallest 

Count 

Year 

Recorded 

Largest 

Count 

Year 

Recorded 

Australasian 

Shoveler 

312 29 32 49 4 50 476 4 1995 312 1983 

Australian 

Pelican 

171 9 486 245 74 62 1303 8 42 150 5 3 110 2668 3 2000 1303 1992 

Australian 

Shelduck 

21 40 61 21 1992 40 2001 

Australian 

White Ibis 

6739 560 23 623 963 3411 667 1369 84 31 66 4 32 507 94 5 3 46 15227 3 2000 6739 1983 

Australian 

Wood Duck 

1180 82 91 497 1751 99 140 211 399 44 200 60 13 5 4772 5 2001 1751 1989 

Black Swan 2652 88 46 264 224 214 24 42 21 5 67 21 18 3686 5 1994 2652 1983 

Black-winged 

Stilt 

624 2242 105 1960 298 390 149 5768 105 1985 2242 1984 

Brolga 49 50 99 49 1988 50 1989 

Caspian Tern 25 25 25 1989 25 1989 

Darter 15 29 151 37 49 25 2 5 5 328 2 1994 151 1986 

Dusky 

Moorhen 

15 24 39 15 1983 24 1990 

Egrets 2464 324 42 167 491 592 199 63 66 19 32 127 1010 322 100 4 54 6076 4 2000 2464 1983 

Eurasian Coot 1201 9 212 377 1269 768 33 0 4 2532 10 75 6490 4 1995 2532 1996 

Freckled Duck 15 15 15 1983 15 1983 

Glossy Ibis 5460 177 19 167 207 49 176 995 21 40 700 148 88 8247 19 1985 5460 1983 

Great 

Cormorant 

31 105 136 31 1983 105 1992 

Great Crested 

Grebe 

118 49 167 49 1988 118 1984 

Great Egret 236 24 25 74 14 12 278 10 8 681 8 2001 278 1996 

Grey Teal 16754 48881 214 4651 321 1244 3401 2639 84 2172 1165 90 348 215 101 98 82378 84 1991 48881 1984 

Gull-billed 

Tern 

50 50 50 1996 50 1996 

Hardhead 1794 2065 37 24 27 21 8 3976 8 2001 2065 1984 

Little Black 

Cormorant 

15 236 106 248 88 24 13 5 38 773 5 2000 248 1988

Common 

Name 

1983 1984 1985 1986 1987 1988 1989 1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 Total 

Individuals 

Smallest 

Count 

Year 

Recorded 

Largest 

Count 

Year 

Recorded 

Little Pied 

Cormorant 

88 12 49 66 10 4 229 4 2001 88 1984 

Magpie Goose 25 25 25 1996 25 1996 

Masked 

Lapwing 

19 12 1145 40 1216 12 1989 1145 1990 

Musk Duck 46 174 220 46 1983 174 1988 

Pacific Black 

Duck 

6006 1239 174 197 226 323 1549 2539 339 632 5 190 304 3500 107 55 6 35 17426 5 1994 6006 1983 

Pied 

Cormorant 

25 248 10 283 10 2001 248 1990 

Pink-eared 

Duck 

60 60 60 1986 60 1986 

Plumed 

Whistling-duck 

93 50 536 679 50 1996 536 1998 

Purple 

Swamphen 

15 6 31 133 2 187 2 2001 133 1993 

Royal 

Spoonbill 

59 25 10 33 4 54 25 5 2 217 2 2001 59 1984 

Silver Gull 62 62 62 1983 62 1983 

Small Grebes 15 15 50 28 108 15 1983, 1986 50 1989 

Straw-necked 

Ibis 

10155 11269 7341 4876 273 2507 4955 1198 4736 362 19 15 47706 15 2001 11269 1984 

Whiskered 

Tern 

1060 2389 303 50 506 4308 50 1989 2389 1984 

White-faced 

Heron 

31 118 15 18 163 348 14 10 2 25 27 8 779 2 1995 348 1990 

White-necked 

Heron 

46 324 334 94 24 88 248 14 199 2304 10 13 20 3 45 3766 3 2000 2304 1996 

Yellow-billed 

Spoonbill 

78 59 32 212 75 88 622 42 254 99 11 60 330 10 40 75 6 216 2309 6 2000 622 1990 

Totals 55869 71710 812 17091 8231 8303 12803 15799 434 4602 4089 148 892 11849 5600 2011 330 223 922 221718 148 1994 71710 1984

APPENDIX G: Invertebrates Recorded Within the DRP 

Taxa No Records Dataset 

Phylum Platyhelminthes 

Class Temnocephalidea 

Temnocephala sp. 1 Bray, 1994 

Temnocephalidea sp. 3 Bray, 1994 

Phylum Nemertea 

Class Nematoda 

Nematoda sp. 11 Bray, 1994 

Phylum Mollusca 

Class Bivalvia 

Corbiculina australis 4 Bray, 1994 

Sphaerium tasmanicum 7 Bray, 1994 

Sphaerium sp. 25 Sheldon, 1995 

Class Gastropoda 

Austropeplea lessoni 14 Bray, 1994 

Austropeplea tomentosa 21 Bray, 1994 

Ferrissia petterdi 17 Bray, 1994 

Ferrissia spp. 534 Sheldon, 1995 

Gyraulus meridionalis 764 Bray, 1994 

Physastra sp. 1 Bray, 1994 

Segnitila victoriae 88 Bray, 1994 

Physa / Isidorella sp. 1,205 Bray, 1994 (1197), Sheldon, 1995 (8) 

Physa acuta 168 Sheldon, 1995 

Gastropoda sp. 1 Bray, 1994 

Phylum Annelida 

Class Hirudinea 

Hirudinea sp. 3 Bray, 1994 

Class Oligochaeta 

Branchiura sowerbyi 3 Bray, 1994 

Dero sp. 2 Bray, 1994 

Oligochaeta sp. 9,645 Bray, 1994 (9515), Sheldon, 1995 (130) 

Annelida sp. 2 Bray, 1994 

Phylum Rotifer 

Class Monogononta 

Order Ploimida 

Family Brachionidae 

Brachionus urceolatus Jenkins and Briggs, 1995 

Brachionus novaezealandia Jenkins and Briggs, 1995 

Brachionus lyratus Jenkins and Briggs, 1995 

Brachionus angulatus Jenkins and Briggs, 1995 

Keratella sp. Jenkins and Briggs, 1995 

Family Asplanchnidae 

Asplancha sieboldi Jenkins and Briggs, 1995 

Family Lecanidae 

Lecane s. str. papuana Jenkins and Briggs, 1995 

Order Gnesiotrocha 

Family Testudinellidae 

Testudinella patina Jenkins and Briggs, 1995 

Phylum Arthropoda


Class Arachnida 

Hydracarina sp. 74 Bray, 1994 (72), Sheldon, 1995 (2) 

Araneae sp. 74 Bray, 1994 

Class Crustacea 

Subclass Branchiopoda 

Order Cladocera 

Conchostraca sp. 7 Bray, 1994 

Cladocera sp. 961 Bray, 1994 

Suborder Anomopoda 

Family Daphniidae 

Daphnia carinata ND Jenkins and Briggs, 1995 

Ceriodaphnia sp. ND Jenkins and Briggs, 1995 

Family Macrothrichidae 

Macrothrix cf. indistincta ND Jenkins and Briggs, 1995 

Family Moinidae 

Moina cf. tenuicornis ND Jenkins and Briggs, 1995 

Moina cf. micrura ND Jenkins and Briggs, 1995 

Moina sp. ND Jenkins and Briggs, 1995 

Family Chydoridae 

Pleuroxus sp. ND Jenkins and Briggs, 1995 

Alona sp. ND Jenkins and Briggs, 1995 

Biapertua rigidicaudis ND Jenkins and Briggs, 1995 

Leberis cf aenigmatosa ND Jenkins and Briggs, 1995 

Order Ctenopoda 

Family Sididae 

Diaphanosoma sp. ND Jenkins and Briggs, 1995 

Subclass Ostracoda 

Ostracoda sp. 382 Bray, 1994 

Subclass Copepoda 

Boeckella cf symmetrica ND Jenkins and Briggs, 1995 

Boeckella triarticulata ND Jenkins and Briggs, 1995 

Cyclopoid copepod 198 Bray, 1994 

Calanoid copepod 244 Bray, 1994 

Subclass Malacostraca 

Order Isopoda 

Austroargathona sp. 47 Bray, 1994 

Austroargathona picta 326 Sheldon, 1995 

Order Decapoda 

Caradinia mccullochi 153 Sheldon, 1995 

Parataya australiensis 115 Bray, 1994 (41), Sheldon, 1995 (74) 

Macrobrachium cf australiense 2,216 Bray, 1994 (277), Sheldon, 1995 (1939) 

Cherax destructor 244 Bray, 1994 (223), Sheldon, 1995 (21) 

Class Insecta 

Order Collembola 

Collembola sp 1 529 Bray, 1994 



Collembola sp. 2 Bray, 1994 

Order Ephemeroptera 

Family Letophlebiidae


Atalophlebia cf MMBW sp 1 271 Bray, 1994 

Atalophlebia australis 7 Sheldon, 1995 

Immature Atalophlebia sp. 22 Bray, 1994 

Letophlebiidae sp. 1 Bray, 1994 

Family Caenidae 

Tasmanocoenis tillyardi 614 Bray, 1994 

Tasmanocoenis arcuata 410 Sheldon, 1995 

Immature Tasmanocoenis sp. 19 Bray, 1994 

Immature Caenidae 52 Bray, 1994 

Family Baetidae 

Cloeon sp. 837 Bray, 1994 (93), Sheldon, 1995 (744) 

Baetidae spp. 1 Bray, 1994 

Order Odonata 

Suborder Zygoptera 

Family Gomphidae 

Austrogomphus sp. 6 Sheldon, 1995 

Family Coenagrionidae 

Ischnura aurora aurora 18 Bray, 1994 

Ischnura heterostica 19 Bray, 1994 

Xanthagrion erythroneurum 48 Sheldon, 1995 

Austragrion watsoni 64 Sheldon, 1995 

Calagrion billinghursti 1 Sheldon, 1995 

Immature Ischnura sp. 68 Bray, 1994 

Immature Coenagrionidae 21 Bray, 1994 

Immature Zygopteran 2 Bray, 1994 

Tiny Zygoptera 201 Sheldon, 1995 

Family Lestidae 

Austolestes analis / leda 1 Bray, 1994 

Suborder Anisoptera 

Family Aeschnidae 

Hemianax papuensis 4 Bray, 1994 

Aeschnidae sp. 1 Bray, 1994 

Family Corduliidae 

Hemicordulia tau 18 Bray, 1994 

Immature Cordullidae 4 Bray, 1994 

Order Hemiptera 

Family Hydrometridae 

Hydrometra sp. 1 Bray, 1994 

Family Gerridae 

Gerridae sp. 25 Sheldon, 1995 

Gerridae sp 1 5 Bray, 1994 

Gerridae sp 2 1 Bray, 1994 

Family Veliidae 

Microvelia oceanica 24 Bray, 1994 

Microvelia sp. 24 Sheldon, 1995 

Veliidae sp 1 3 Bray, 1994 




Veliidae sp 6 6 Bray, 1994


Family Hebridae 

Hebrus sp 2 2 Bray, 1994 

Family Mesoveliidae 

Mesovelia sp 1 96 Sheldon, 1995 

Mesoveliidae sp 1 5 Bray, 1994 




Mesoveliidae sp 1 Bray, 1994 

Family Corixidae 

Agraptocorixa sp 157 Bray, 1994 (14), Sheldon, 1995 (143) 

Micronecta major 846 Bray, 1994 

Micronecta spp. 6,557 Sheldon, 1995 

Sigara sp 44 Bray, 1994 (31), Sheldon, 1995 (13) 

Family Naucoridae 

Naucoris congrex 19 Bray, 1994 

Naucoris sp 2 22 Bray, 1994 

Family Belostimatidae 

Belostimatidae sp 1 16 Bray, 1994 

Belostimatidae sp 2 81 Bray, 1994 

Family Notonectidae 

Anisops spp. 330 Bray, 1994 (147), Sheldon, 1995 (183) 

Family Pleidae 

Plea sp. 2 Bray, 1994 

Hemipteran sp. 17 Bray, 1994 

Order Diptera 

Family Tipulidae 

Tipulidae sp 1 8 Bray, 1994 



Family Simulidae 

Simulium ornatipes 48 Bray, 1994 

Immature Simuliidae sp 17 Bray, 1994 

Family Culicidae 

Culicini sp. 5 Bray, 1994 

Culicidae sp 7 Bray, 1994 (1), Sheldon, 1995 (6) 

Family Ceratopogonidae 

Bezzia sp. 459 Sheldon, 1995 

Family Psychodidae 

Psychodidae sp 17 Bray, 1994 

Family Chironomidae 

Subfamily Tanypodinae 

Ablabesmyia sp. 160 Bray, 1994 (97), Sheldon, 1995 (63) 

Clinotanypus sp. 1 Bray, 1994 

Coelopynia pruinosa 3 Bray, 1994 

Coelopynia sp. 624 Sheldon, 1995 

Larsia sp. 47 Bray, 1994 

Monopelopia sp. 3 Bray, 1994 

Paramerina sp. 542 Bray, 1994 

Procladius sp. 395 Bray, 1994 (142), Sheldon, 1995 (253)


Tanypodinae sp 2 Bray, 1994 

Subfamily Orthocladiinae 

Corynoneura sp. 81 Bray, 1994 

Cricotopus spp. 362 Sheldon, 1995 

Cricotopus / Paratrichocladius sp. 87 Bray, 1994 

Nanocladius sp 94 Bray, 1994 

Parakiefferiella sp. 148 Bray, 1994 (76), Sheldon, 1995 (72) 

Paralimnophyes sp. 4 Bray, 1994 

Parametriconemus sp. 8 Bray, 1994 

Rheocricotopus sp. 312 Bray, 1994 

Thienmanniella sp. 14 Bray, 1994 

Immature Orthocladiinae sp. 5 Bray, 1994 

Subfamily Chironominae 

Cladotanytarsus sp. 165 Bray, 1994 (31), Sheldon, 1995 (134) 

Paratanytarsus sp. 16 Bray, 1994 

Rheotanytarsus sp. 78 Bray, 1994 

Tanytarsus sp. 941 Bray, 1994 (773), Sheldon, 1995 (168) 

Virgatanytarsus sp. 1 Sheldon, 1995 

Immature Tanytarsini 3 Bray, 1994 

Chironomus sp. 942 Bray, 1994 (931), Sheldon, 1995 (11) 

Chironomus cloacalis 30 Sheldon, 1995 

Cladopelma sp. 233 Bray, 1994 (26), Sheldon, 1995 (207) 

Cryptochironomus sp. 116 Bray, 1994 (48), Sheldon, 1995 (68) 

Stenochironomus sp. 45 Sheldon, 1995 

Dicrotendipes sp. 2,243 Bray, 1994 (311), Sheldon, 1995 (1932) 

Dicrotendipes conjunctus 301 Sheldon, 1995 

Harnischia sp. 72 Bray, 1994 (71), Sheldon, 1995 (1) 

Kiefferulus martini 7 Bray, 1994 (1), Sheldon, 1995 (6) 

Kiefferulus sp. 8,118 Bray, 1994 

Microchironomus sp. 27 Bray, 1994 

Parachironomus sp. 357 Bray, 1994 (156), Sheldon, 1995 (201) 

Paracladopelma sp. 1 Bray, 1994 

Paratendipes sp. 38 Sheldon, 1995 

Polypedilum nubifer 142 Bray, 1994 

Polypedilum prasiogaster 6 Bray, 1994 

Polypedilum sp. 411 Bray, 1994 (226), Sheldon, 1995 (185) 

Chironominae sp 2 Bray, 1994 

Chironomid pupa 415 Bray, 1994 

Tiny Chironomids 43 Sheldon, 1995 

Family Ceratopogonidae 

Ceratopogoninae sp 1 41 Bray, 1994 




Forcipomyiinae sp 2 3 Bray, 1994 

Forcipomyiinae sp 3 1 Bray, 1994 

Family Stratiomyidae 

Stratiomyidae sp 1 13 Bray, 1994 

Stratiomyidae sp 2 2 Bray, 1994 

Family Tabanidae


Tabanidae sp 5 Bray, 1994 (3), Sheldon, 1995 (2) 

Family Empididae 

Empidiae sp. 140 Bray, 1994 (112), Sheldon, 1995 (28) 

Family Sciomyzidae 4 Bray, 1994 

Sciomyzidae sp. 16 Bray, 1994 

Family Muscidae 

Muscidae sp 1 2 Bray, 1994 (1), Sheldon, 1995 (1) 

Muscidae sp 2 3 Bray, 1994 

Muscidae sp 3 5 Bray, 1994 

Muscidae pupa 5 Bray, 1994 

Famiy Ephydridae 

Ephydridae sp. 14 Bray, 1994 

Ephydridae pupa 7 Bray, 1994 

Immature Dipteran larvae 2 Bray, 1994 

Dipteran pupa 86 Bray, 1994 

Order Lepidoptera 

Pyralidae MDFRC sp 7 

Pyralidae sp 2 42 Bray, 1994 

Pyralidae sp 3 1 Bray, 1994 

Order Trichoptera 

Family Hydroptilidae 

Hellyethira simplex 15 Bray, 1994 

Orthotrichia sp. 1 Bray, 1994 

Hydroptilidae pupa 1 Bray, 1994 

Family Ecnomidae 

Ecnomus cygnitus 134 Bray, 1994 

Ecnomus pansus 289 Bray, 1994 

Ecnomus turgidus 43 Bray, 1994 

Economus sp. 202 Sheldon, 1995 

Immature Ecnomus sp. 55 Bray, 1994 

Family Hydropsychidae 

Cheumatopsyche sp 2 4 Bray, 1994 

Cheumatopsyche sp. 8 Sheldon, 1995 

Family Leptoceridae 

Oecetis sp. 608 Bray, 1994 (5), Sheldon, 1995 (603) 

Triaenodes sp. 9 Bray, 1994 

Triplectides australis 231 Bray, 1994 (46), Sheldon, 1995 (185) 

Notolina spira 1 Sheldon, 1995 

Immature Triplectides sp. 3 Bray, 1994 

Immature Leptoceridae sp 2 Bray, 1994 

Immature Limnnephiloidea 1 Bray, 1994 

Order Coleoptera 

Family Carabidae 

Carabidae sp 1 (A) 4 Bray, 1994 




Carabidae sp (A) 1 Bray, 1994 

Carabidae sp (L) 1 Bray, 1994 

Family Haliplidae


Haliplus sp. 1 Bray, 1994 

Family Dytiscidae 

Allodessus bistrigatus (A) 13 Bray, 1994 

Allodessus sp. 21 Sheldon, 1995 

Antiporus gilberti (A) 6 Bray, 1994 (4), Sheldon (2) 

Antiporus femoralis 18 Sheldon, 1995 

Cybister tripunctatus (L) 5 Bray, 1994 

Eretes sp. (L) 1 Sheldon, 1995 

Hydaticus pulcher 1 Bray, 1994 

Hydrovatus armstongi (A) 4 Bray, 1994 

Hydrovatus opacus (A) 8 Bray, 1994 

Laccophilus sp. (A) 2 Bray, 1994 

Limbodessus compactus (A) 49 Bray, 1994 

Limbodessus sp. 1 (A) 1 Bray, 1994 

Liodessus praelargus (A) 5 Bray, 1994 

Liodessus sp. 25 Bray, 1994 (23), Shledon, 1995 (2) 

Megaporus sp. 12 Bray, 1994 (1), Sheldon, 1995 (11) 

Paroster sp. 31 Sheldon, 1995 

Platynectes decempunctatus var 

polygrammus (A) 

1 Bray, 1994 

Rhantus suturalis (A) 9 Bray, 1994 

Rhantus suturalis (L) 2 Bray, 1994 

Sternopriscus multimaculatus (A) 4 Bray, 1994 

Dytiscidae sp (L) 29 Bray, 1994 

Family Gyrinidae 

Macrogyrus sp. (L) 1 Sheldon, 1995 

Family Hydraenidae 

Hydraena sp. 29 Sheldon, 1995 

Hydraena sp 1 (A) 47 Bray, 1994 

Hydraena sp 2 (A) 16 Bray, 1994 

Ochthebius sp (A) 29 Bray, 1994 (26), Sheldon, 1995 (3) 

Hydraenidae sp (L) 3 Bray, 1994 

Family Staphylinidae 

Staphylinidae sp 1 (A) 23 Bray, 1994 












Staphylinidae sp (A) 4 Bray, 1994 

Family Hydrophilidae 

Berosus approximans (A) 13 Bray, 1994 

Berosus discolor (A) 1 Bray, 1994 

Berosus majusculus (A) 31 Bray, 1994


Berosus sp 4 (A) 1 Bray, 1994 

Berosus sp. 68 Bray, 1994 (67), Sheldon, 1995 (1) 

Enochrus sp. 4 Sheldon, 1995 

Enochrus sp 1 (A) 9 Bray, 1994 

Enochrus sp 2 (A) 37 Bray, 1994 

Helochares nr sp (mareensis) (A) 36 Bray, 1994 

Hydrochus cf MDFRC sp 2 (A) 94 Bray, 1994 

Hydrophilus sp (A) 1 Bray, 1994 

Limnoxenus zealandicus (A) 7 Bray, 1994 

Paracymus pygmaeus (A) 24 Bray, 1994 

Paracymus sp. 27 Sheldon, 1995 

Spercheus sp (A) 3 Bray, 1994 

Sternolophus marginicollis (A) 2 Bray, 1994 

Hydrophilidae sp (L) 67 Bray, 1994 (64), Sheldon, 1995 (3) 

Family Brentidae 

Brentidae sp 1 (A) 8 Bray, 1994 

Brentidae sp (L) 5 Bray, 1994 

Family Curculionidae 

Curculionidae sp 1 (A) 5 Bray, 1994 








Curculionidae sp (L) 1 Bray, 1994 

Family Chrysomelidae 

Chrysomelidae sp 1 (A) 199 Bray, 1994 






Chrysomelidae sp (L) 36 Bray, 1994 

Family Scirtidae 

Scirtidae sp 3 (A) 1 Bray, 1994 

Scirtidae sp 4 (A) 1 Bray, 1994 

Scirtidae sp (L) 1 Bray, 1994 

Family Elmidae 

Elmidae sp (L) 1 Bray, 1994 

Coxelmis sp. (L) 7 Sheldon, 1995 

Coleopteran sp (A) 7 Bray, 1994 

Coleopteran sp (L) 2 Bray, 1994

DARLING RIVERINE PLAINS BIOREGION Background Report

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