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Page 1: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

VEGETATON STUDY

of

Page 2: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare
Page 3: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Bradshaw Field Training Area

Baseline Vegetation Survey andVegetation Management

Prepared for ConnellWagner- September, 997

,

A M Lane

ERA Environmental Services Pty Ltd

T M Orr

Tropintel Environmental Consultancy

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Page 5: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

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;.^ ERA Environmental Services Pty LtdACN 000 955 171

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Darwin Office 482 Stuart Highway, Winnellie NT 0820PO Box 39443. Winnellie NT 0821Tel: (08) 8984 3255 Fax (08) 8984 4161

. Bradshaw Field Training AreaBaseline Vegetation Survey and

Vegetation Management

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for

Connell Wagner

by

A M Lane

ERA Environmental Services Pty Ltd

and

T M Orr

Tropintel Environmental Consultancy

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COMMERCIAL-IN-CONFIDENCE

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Prepared by: ERA Environmental Services Pty Ltd. ERA Environmental Services Pty Ltd (ERAES)is a legal entity separateand distinctfrom Energy Resources of Australia Ltd (ERA) (AC. N. 008 550 865). ERA is not responsible for,makes no representations or warranty, and gives no guarantee in relation to any services performed by ERAES.

Job NO XI32

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ERA Environmental Services Pty Ltd has had to rely on information from other persons inpreparing this report (including the party for whom it is prepared) and is not in a position to,and has not, verified the accuracy or completeness of such information. Accordingly,ERAES takes no responsibility for, and assumes no liability in respect of, any informationprovided to it by others for the purposes of preparing this report, or the consequences fromthe use of such information.

This document is prepared only forthe person to whom it is addressed and the report andany information or conclusion in it, is not intended to be, and should not be, relied upon orused by any other person. ERAES accepts no liability where any person so uses or reliesupon it contrary to the preceding sentence.

DISCLAIMER

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8/10/97Job NO XI32

Page 8: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

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Page 9: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

EXECUTIVE SUMMARYINTRODUCTIONMETHODS2Site selection2. I

2.2 Datacollection

Data from past surveys2.3

Data storage and processing2.4

SPECIES3

Species of conservation significance3.1

Species new to the region3.23.3 Weeds

DESCRIPTION OF VEGETATION COMMUNITIES4

DESCRIPTION OF MAPPING UNITS5

Mapping Units within Training Sectors5. IIMPACTS ASSOCIATED WITH INFRASTRUCTURE6DEVELOPMENTEXERCISE IMPACTS AND MANAGEMENTOF7

DISTURBANCE

Impacts on habitats7.17.2 Sensitive habitats7.21 Sandstonehabitats7.2.2 Monsoonforests

7.2.3 Riparianhabitats7.2.4 Coastal habitats

Habitats of conservation significance7.3

Management of species of conservation significance7.4

7.5 Groundcover

Weed management7.6

7.61 Preventing introduction and spread76.2 Ensuring weeds management is an integral part of land

management7.63 Learning more about weeds -research and monitoring7.6.4 Increasing awareness and education

MONITORING8

Recovery of degraded areas after destocking8.1

Impact of military activities8.2

Education of military personnel8.3CONCLUSIONS ANDACTIONS9

9.1 Sensitive habitatsHabitats of conservation significance9.2

9.3 Weeds

Monitoring9.4ACKNOWLEDGEMENTS10REFERENCES ...11

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TABLE OFCONTENTS

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16

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1820

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... 22. 23

2325

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28. 30

30......... 30

31....... 31

3333

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34.. 35

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Page 11: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Tables

I Landsat Them atIC Mapper(TM) scenes that were used to select vegetation sites

2 Structural formation from Specht (1981)

3 Rare species recorded on BFTA in June 1997

4 Rare species recorded on BFTA prior to June 1997

5 Weed species recorded on BFTA in June 1997

6 Vegetation units within training sectors

7 Impact of military exercises on vegetation mapping units

.

Maps

I Location of vegetation sites

2 Vegetation mapping units

I Species listfor June 1997

2 Species and location of occurrence in June 1997

3 Species notrecorded on BFTA before June 1997

4 Species recorded on BFTA before June 1997

5 Vegetation communities

6 Vegetation structural categories and classes contained within

7 Photographs of vegetation classes

8 Impactrankings on vegetation mapping units

Appendices

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Page 13: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

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EXECUTIVE SUMMARY

A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From151 sites, a total of 422 species were identified including three rare species, one new

species, 14 weed species, and 139 species that had not previously been recorded on theproperty.

Seventy vegetation communities were classified under eight broad structural classes into 45mapping units. The broad structural classes were monsoon forest, riparian forest, eucalyptopen-forest/woodland, low open-forest!'woodland, eucalypt open-woodland, otheropen-woodland, shrubland, and grassland.

The impacts of military activity on vegetation may include direct damage from ordnance andvehicle manoeuvre, and indirect impacts including weed introduction, fire, and soil erosion.

Based on the characteristics of the vegetation classes, open woodland and low-open

woodland and grasslands are the most resilient vegetation types and are suitable for a wide

range of military exercises. Most sensitive to disturbance are monsoon forests, riparianhabitats and sandstone habitats. It is recommended that military activity be totally excluded

from monsoon forests, which occupy less than 0,059". of the training area, and be severely

restricted in riparian habitats which occupy approximately 3.59".. Only dismounted training is

recommended, or indeed likely to be feasible, in sandstone areas.

Two vegetation classes that occur on Bradshaw Station, MeIaieuca minutifolia low woodland

and Xerochloa grassland, are not currently protected in the Northern Territory's parks and

reserves. These vegetation assemblages are largely restricted to the Victoria River District

in the NT. Impactfrom military activities in these habitats should be minimised by conducting

only dismounted training in Xerochloa grasslands, and some areas of MeIaleuca minutifolia

woodland occurring in more remote areas could also be restricted to dismounted training.

The primary management objective of Bradshaw Station should be to maintain and enhance

the capability of the properly to meet Army's training requirements on a long-term

sustainable basis. This can only be achieved by maintaining the integrity of the landscape

and preserving biodiversity. Monitoring the impacts of military landuse on vegetation iscrucial to achieving this objective. Regular monitoring of key indicators such as vegetation

composition, cover, and structure, and soil surface condition, will assist managers to

determine when to rest impacted areas so that recovery can occur naturally or be

accelerated by prescribed management intervention practices. Monitoring should occur in a

range of vegetation classes within different habitats because the degree of impact will vary

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depending on the type and intensity of military activity and on environmental factors such as

condition prior to military landuse, soiltype, and slope.

The opportunity exists to monitor and document the post-grazing recovery of the natural

environment under Defence management, as well as the impact of military exercises on

vegetation and landscape processes and the rate of natural vegetation recovery. The

valuable information so gathered has the potential to significantly improve environmental

management of military training areas in the Northern Territory and in other areas ofAustralia.

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INTRODUCTION

Bradshaw Field Training Area (BFTA) lies within the Victoria River District (VRD) of

the Northern Territory, and the biogeographical region of Victoria-Bonaparte

(Connors at a/. 1996). The VRD comprises 30 properties (Dyer at a1. 1997) of which

BFTA, covering about 8700 kin', is the largest. Average annual rainfall in the area is

about 825 min (Bureau of Meteorology, pers. coinm. 1996), drier than more northern

areas of the NT and wetter than the Kiinberley area of Western Australia. The land

use in this area is predominantly grazing. The vegetation of BFTA represents a

transition between vegetation to the west and north-west of the NT, and the northern

Kiinber!ey.

This report discusses the results of a vegetation survey that was conducted in June1997.

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The objectives of the study were to:

describe, classify, and map the vegetation on BFTA;

describe the vegetation communities within mapping units;

record the occurrence of species of conservation significance;

record the occurrence of species that have not previously been recorded in

the region;

record the occurrence of introduced species; and

. assessthepotentialimpactsofDefenceactivitiesonvegetation.

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From this baseline data, recommendations were to be made on the management of

BFTA to:

. preserve biological diversity and to protect sensitive communities and rare

species; and

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. promote management practices that will enhance and maintain sustainableecosystems so that the use of BFTA as a military training area can beoptimised.

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2.1

METHODS

Site selection

The baseline vegetation survey was conducted in June 1997. Site selection wasmade from Four Landsat Thematic Mapper (TM) scenes (Table I) that covered

BFTA. The data sets were initially rectified using at least six ground control points

per scene, and were enhanced using a simple linear contrast stretch. The fourscenes were then mosaiced using the appropriate functions within the "ER Mapper"

image processing software. Spatial accuracy of the final mosaic was estimated to bein the order of 1.5 pixels for the whole dataset, and 0.5 pixels between scenes. Thismeets the Australian Defence Force (ADF) requirement for DIGEST Level 2

accuracy (+50 in) for digital data at this scale. The scenes were matched bymanually balancing the histograms in overlapping areas. The resulting image wasplotted as a series of raster maps in UTM projection at 1:100,000 scale, completewith Ikm grid, for use in the field.

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Table I

Landsat ThematIC Mapper(TM) scenes that were used to selectvegetation survey sites on BFTA in June 1997

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Scene

ath/row

106-70

106-71

Prior to field deployment, patterns in the image were manually interpreted to compilea set of map units which were consistent and repeatable throughout the dataset.These map units then formed the basis of the field data collection exercise. Groundtruth data were collected for each of the patterns identified in the image by

navigating towards the centre of the pattern using GPS so that the vegetationsurveyed was representative of the mapping unit. Every effort was made to avoidlocating ground truth sites near the edges of patterns, in very small occurences of apattern, or on disturbed or burnt areas.

105-70

AcquisitionDate

105-71

20 A rill99624 A rill992

27 Ma 1995

20 A rill993

Pre-processing level

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4/5

4/5

4/5

4/5

No. of control

oints

812

10

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One hundred and fifty one sites were surveyed over a two week period. Most sites

on the Angalarri Plain (sites I to 58) were accessed by 4x4 vehicle while all other

sites on the property (sites 59 to 151) were accessed by Jetranger helicopter.

Data collection

At each plot, observations were made on the landform pattern, slope, aspect,

geology, 9". rock outcrop, 9, '. gravel, 9. ". bare ground, and surface soil. The position of

each plot was recorded in AMG coordinates using GPS. A colour photograph wastaken of each plot.

Species abundance at each plot was estimated as the percentage cover of each

species in the upper, middle and lower strata. Lifeform data was collected for 12

categories and the projective foliage cover (PFC) of each estimated. The 12 lifeform

categories were:

(1) trees greater than eight metres in height; (2) trees less than eight metres in

height; (3) shrubs greater than two metres in height; (4) shrubs less than two metres

in height; (5) tussock grasses; (6) hummock grasses; (7) sedges; (8) forbs; (9) vines;

(10) ferns; (11) cycads; and (12) palms.

The overall percentage cover and average height of the upper, inid and lower strata

was estimated and, based on the cover of the dominant stratum, a structural

classification of the assemblage was given. The structural classification (Table I) is

based on the structural formation of Specht (1981).

Species that were not identified in the field were sampled and identified by staff at

the Northern Territory Herbarium. For some specimens, especially sedges and

grasses, identification to family or genus level only was possible due to lack of fertile

material.

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2.3 Data from past surveys

Data collected by NT Parks & Wildlife Commission in 1993 and by the MGI Unit of

the ADF in 1995 at a number of additional sites were included for the purposes of

improving the accuracy of the mapping unit classification and to increase the

collective knowledge of vegetation in the area. These sites are numbered 152 to

208. The location of each vegetation site is shown on Map I.

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Page 18: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Table 2

Structural formations from Specht(1981) based on height andfoliage cover of the dominant stratum

Life form and heightof strata

Trees 10-30m

Trees 5.0m

Shrubs>2m

Shrubs I-2m

Shrubs<2m

Hummock perennialgrasses

Graininoids

and grass

Sedges

Herbs

6

100-70

Closed-forest

Low closed-forest

Tall closed-shrubland

Closed-shrubland

Low closed-shrubland

Foliage projective cover (7")

30.070-30

Open-woodlandWoodlandOpen-forest

Low open-woodlandLowwoodlandLow open-forest

Tallopen-shrubland Tailsparse-shrublandTall shrubland

Open-shrubland Sparse-shrublandShrubland

Low open-shrubland Low sparse-shrublandLow shrubland

Hummockgrassland Open-hummock Sparse-hummockgrasslandgrassland

Open-grassland Sparse-grassland

Sparse-sedgeland

Sparse-herbland

A tree is defined as woody plant usually with a single stern. A shrub is usually a woody plant with many sternsarising within 2m of the base. Foliage cover of <17, is referred to as scattered individuals

Closed grassland

Closed sedgeland

Closed-herbland

2.4 Data storage and processing

Data from the plot sheets were entered onto a database (Microsoft Access) forstorage and retrieval. These data form the basis for an image training exercise oncomputer, using the "maximum likelihood" classifier in ER Mapper. A preliminarythem atic map for vegetation was then compiled.

All attribute data have been incorporated into a GIS which also overlays soil

descriptions from most of the 152 vegetation sites surveyed in June 1997 and alsofrom other soil sites on BFTA.

Grassland

1-10

Sedgeland

Herbland

Open-sedgeland

Open-herbland

3 SPECIES

A total of 422 species were recorded during the survey (Appendix I). A further 132species were not identified due to absence of fertile material. Many of theseunidentified records are likely to be duplicate species. One F1mbristylis species

(Cyperaceae) is possibly a new species of grass and has been sent to theappropriate taxonomist for verification. This species was collected from Lys4:)hyllumcunninghamii woodland (site 25; mapping unit 27) in the southern area of the

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Angalarri Plain. Appendix 2 gives a complete species list and the location(s) whereeach species was recorded.

Species of conservation significance

The Checklist of Vascular Plants of the Northern Territory, Australia (Dunlop at al.

1996) was consulted to assess the conservation status of species. Of the 422

species recorded on BFTA, four are currently classified as rare in the region (Table3).

An explanation of the conservation code relevant to these three species is asfollows:

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3 = the species has a range over 100 kin in Australia but occurs only in small

populations which are mainly restricted to highly specific and localised habitats;

K or k = poorly known, may be endangered, rare and vulnerable, but current field

information is inadequate;

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C or c = the species is known to be represented in a National Park or reserve.

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The use of capital letters indicates that the status of the species is considered to be

of national significance. Lower case letters are used where the status applies either

to the distribution of the species within the NT or to particular NT populations. "-"

indicates that the species has been recorded in a reserve but that the size of the

population within the reserve is unknown.

R or r = rare

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^ One of the four rare species is a forb, Uraria 1507 Litchfield, one is a shrub,

Grevil/ea myOSodes, and the third species, Acacia keneri, is a smalltree. The fourth

species, Adjantum hi^pidulum, is also rare but only in central Australia, and hencewill not be discussed further.

Uraria Litchfield, was collected from Eucalyptus woodland on the laterite plateau in

the eastern portion of the Yarnbarran Sector. Uraria is represented in Litchfield

National Park (Briggs and Leigh 1996) and Nitmiluk (Katherine Gorge) National Park

(N. Smith pers. coinm. 1997). The record on BFTA is a range extension for this

species.

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Table 3

Species from BFTA that are listed as rare in the Northern Territory(Dunlop at a1. 1996)

Species

UrariaLitchfield

Conservation

status

Grevillea

myOSodes

8

3RC-

Acaciakeneri

3KC-

Lifeform

prostrate forb

3r

Grevillea myOSodes was collected from eucalypt mixed woodland on a sandstone

rise where it was locally abundant. This site is close to the proposed Yarnbarran

campsite and airstrip. G. myOSodes is a multi-stemmed shrub, 0.8-2.2 in high, with

silvery green obovate leaves and cream to pale yellow flowers (Wheeler at a1. 1992).

G. myOSodes has previously been collected from Litchfield and Kakadu National

Parks and is not uncommon in the Kiinber!ey. The record on Bradshaw is a link

between the Am hem region and the Kiinberley populations and represents a range

extension forthe species.

Acacia keneriwas also collected from a sandstone habitat (site 70) in the Western

Hills region. It is a shrub or smalltree to 7 in high with drooping branches that give it

a weeping appearance' The flowers are yellow and cylindrical. Flowering occurs from

May to October and fruiting from May to November. A. Keneri also occurs in

sandstone regions in the Kiinberley (Wheeler at a1. 1992). It was collected previouslyon BFTA in 1987.

shrub

Habitat

shrub or smalltree

open eucalyptforest onsandstone

lateau

eucalyptwoodland,plains or gentleSIo es

Location

site 103;706680 N8322000 E

sandstone

,

site 131;622840 E8324290 N

,

site 70;588330 E8339/20 N

Previous surveys of BFTA have recorded a further eight species that are of

conservation significance in the region (Table 4). Bradshaw Station is on the border

of the Amhem and Kiinberley zones and so species that are rare in either of those

regions have been included.

The biogeographic region of Victoria-Bonaparte contains 39 plant species (2,991. of

species recorded from the bioregion) that are rare or threatened (Connors at al.

1996). Grevillea myOSodes and Uraria Litchfield are not included in that rare or

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threatened species list, so these two species increase the current number of rare or

threatened records for the Victoria-Bonapart bioregion to 41. It is likely that asignificant number of the 39 species are present on Bradshaw Field Training Areabecause each of the broad vegetation types of the bioregion (Connors at a1. 1996)occurs on the property.

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Table 4

Species of conservation significance that have been recordedpreviously on BFTA

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Species

Acacia semiifera

,

Hefroteresdentata

Marsdenialandulifera

r

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Polycarpaeastaini'nodina

Conservationstatus

Tacoa maculata

3K

Tephrosiamacrocar a

3K

Sesbaniaerubescens

3r

I

Zone

Utriculariahami/toriii

3R

3.2

Kiinberle

3rC-

Amhem

3kC-

Species new to the region

Of the 422 species recorded during the survey, 139 had no previous record on

BFTA. These species are listed in Appendix 3. A list of species that were recorded

from previous surveys is given in Appendix 4. The large number of new species to

the area is probably due to the relatively low collecting effort in the region prior to the

current survey. About 525 species that were recorded in previous surveys were not

recorded in the 1997 survey. Hence the fulllist of species identified for BFTAcontains about 950 species.

Amhem

3r

Lifeform

Amhem

3RC

shrub

Kiinberle

shrub/forb

Kiinberley

forb or shrub

Amhem

Habitat

forb

Amhem

I

unknown

3.3

eucalyptwoodland

erennialforb

shrub

Acaciathicket

Weeds

shrub

eucalyptwoodland

forb

During the June 1997 vegetation survey of BFTA, 14 introduced (weed) species

were recorded (Table 5). A weed is a plant growing out of place, and which has a

detrimental effect on economic, social, or conservation values (DPI&F 1996).

woodland

unknown

riparian

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The Northern Territory Noxious Weeds Act, which came into force in 1980, and

which contains the essence of the Noxious Weeds Ordnance 1962, provides the

legislative basis for weed control in the NT (DPI&F 1996). Under the Act, there are

three classes of noxious weeds (Miller 1995):

. Class A - to be eradicated. These weeds represent a significant threat but

occur over a relatively small area, and thus there is a reasonable chance of

eradication;

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. Class B - growth and spread is to be controlled. These weeds occur more

widely and, apart from satellite outbreaks, are impractical to eradicate; and

Class C - not to be introduced into the NT. These species could be a

significant threat if introduced. This class also includes all Class A and ClassB weeds since further introductions of these species would exacerbate the

existing problem. The legal responsibility for weed controllies with the owners

or managers of the land.

Twelve of the 14 weed species recorded in the survey occurred along water courses,

especially the Victoria River. Of these, six are declared noxious. Three of thenoxious species, Parkinsonia aculeata (parkinsonia), Xanthium strumarium

(noogoora burr), and Cabtropis procera (rubber bush), are serious weeds ofconservation throughout the Northern Territory and warrant priority control

measures. Weeds of conservation, or environmental weeds, are detrimentalto the

conservation of natural resources through adverse effects on the integrity,

conservation values or biodiversity of natural resources (DPI&F 1996).

Parkinsonia is a shrub or smalltree that is adapted to a wide range of soiltypes and

can form dense thorny thickets along watercourses and around bores and darns

(Queensland Dept of Lands 1995). Dispersal of seed is via water, mud on animalsand vehicles, and by bird and animal droppings (Smith 1995). Control can be

achieved by mechanical removal and follow-up herbicide treatment for smalltrees

(Parsons and Cutherbertson 1991), or herbicide treatment alone for large trees (vanRangelrooy and Miller 1993).

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Rubber bush is a shrub or smalltree that is well adapted to poor soils. It invades

roadsides, disturbed areas, water courses, river flats and coastal dunes (Smith

1995). Dispersal of seed is by wind and water and stands increase in size by

producing suckers (Smith 1995). Controlis difficult because mechanical control and

fire are ineffective due to vigorous regrowih from the tuberous root system (van

Haaren 1995). However, control may, be achieved by regular cultivation and

herbicide application (Crothers and Newbould 1993).

Noogoora burr is an annual woody herb that grows in a wide variety of habitats that

are often disturbed, such as roadsides, bores, and stockyards (Smith 1995). It

generally prefers unshaded positions in tropical climates but extends into semi-arid

regions when water availability is adequate (Parsons and Cutherbertson 1992).

Noogoora burr tolerates flooding. Biological control agents are available for this

species but, to date, appear to exert little controlin the NT (F1annagan 1993). Small

infestations can be removed by hand while large infestations can be treated with

herbicide (Pitt 1991). During the June 1997 survey, noogoora burr was recorded

along the Victoria River. It may be difficult to eliminate this species from that habitat

because floating seeds are transported from upstream. Prevention of spread to other

parts of the property, therefore, should be the priority under these circumstances.

With the removal of cattle, competition for light from native herbs and tree foliage

cover may bring about a decrease in noogoora burr vigour.

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Table 5

Weed species with common name, growth habit, and class of noxious weed (ifdeclared noxious)recorded in the June 1997 vegetation survey of BFTA.

Weed

s ecies

Altemanthera

pungens

Bidenspilosa

Cabtrop^sprocera

Common

name

12

khaki weed

Genchrusciliaris

Gynodondacty/on

Growth habit

rubber bush

Hyptissauveolens

annual forb

buffel grass

Parkinsoniaaculeata

annual forb

couch

Passiflorafoetida

shrub or smalltree.

Class of noxious

weed

Hyptis

Pennisetum

edice/Iatum

perennial grass

Class B, whole of NT

Sennaoccidental^^

parkinsonia

perennial grass

not declared in the NT

SIda acuta

wild passionfruit

B and C, S of 16'30' Slatitude

annual

perennial forb

S^^a cordifolia

annualennisetum

not declared in the NT

SIda

thornbifoli^

coffee senna

shrub or smalltree

Habitat and

no. of sites

Xanthiumstrumarium

not declared in the NT

spineyheadSIda

herbaceousvine

riparian; 2

or

flannel weed

annual grass

riot declared in the NT

riparian; I

4

Paddy'sIucerne

annual orerennial shrub

creek levee; I

B and C, whole of NT

annual or

perennial shrub

noogooraburr

DESCRIPTION OF VEGETATION COMMUNITIES

not declared in the NT

sandstone

plateau; I

annual orerennial shrub

not declared in the NT

The three broad habitats that are commonly found in the top end of the NT, namely

sandstone habitats, lowland habitats, and coastal habitats (Brock 1988), all occur on

BFTA. These can be further subdivided into vegetation communities (assemblages)

based on dominant species and foliage cover. Seventy communities were identified

from the survey data and these are described in Appendix 5.

creek levee; 3

annual orerennial shrub

B and C, whole of NT

f

annual herb

woodland,riparian; I

B and C, whole of NT

river levee; I

B and C, whole of NT

creek levee; 2

B and C, whole of NT

All of the vegetation communities on BFTA are well represented in the Kiinberley,

particularly the eastern Kiinberley, and in other parts of the Top End, except for the

Xerochloa grasslands on Mosquito Flat and in the south of the Western Hills Sector

river levee; I

B and C, whole of NT

river levee; 2

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river levee; I

river levee; 3

river levee; I

river levee; 2

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^

5 DESCRIPTION OFMAPPING UNITS

The 70 vegetation communities were grouped under eight broad structural classes.

Within these structural classes, plant assemblages were combined into a total of 51

land cover classes for the purposes of compiling the draft 1:250,000 VegetationMap. The eight structural classes and the number of mapping units contained ineach are:

13

I Monsoon forest- one mapping unit.

2 Riparian forest, open-forest-three mapping units.

3 EUCalypt open-forest, woodland - 18 mapping units.

4 Low open-forest, woodland - six mapping units.

5 EUCalypt open-woodland -five mapping units.

6 Other open-woodland - seven mapping units.

7 Shrubland - one mapping unit.

8 Grassland - five mapping units.

Appendix 6 describes the mapping units in each of the eight structural classes and

shows which sites were combined into each unit. Map 2 shows the distribution of

each mapping unit and Appendix 7 contains a representative photograph of eachunit.

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The dominant mapping class in sandstone habitats is Eucalyptus

miniata/E. phoenicea open-woodland, and in lowland habitats it is Eucalyptusmicrotheca/Gorymhia Iatifol^a open-woodland. Coastal habitats were not included in

this baseline study.

Mapping Units within Training Sectors

Currently, nine Training Sectors on BFTA have been identified. Table 6 shows the

major vegetation mapping units that occur within each sector. Two of the mappingunits on BFTA, Melabuca minutifolia low woodland (mapping unit 25) and Xerochloa

grassland (mapping unit 68), occur almost exclusively in the Victoria-Bonapart

biogeographic region and are currently not protected in the reserve system of the NT

(Connors at a1. 1996). M. minutifolia low woodland was relatively common on BFTA

occuring at 16 sites. Xerochloa grassland was restricted to the tidal Victoria River

levee and occurred at only one site. The occurrence of these units within trainingsectors is also noted in Table 6.

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Table 6.

in the nine training sectors ofOccurrence of major vegetation mapping units(Bold indicates communities referred to in the text that are potentia yBFTA.

susceptible to impact, or communities that are no r ,most

communities that have high conservation value).

SECTOR

14

ANGALARRl25 MeIaleuca minutifolia, MeIaleuca sencea over annual and perennia grass14 Gorymbia jarifolia over annual and perennial grasses with sedges28 Terminalia canescens, Erythrophleum chiorostachys over annual grasses32 Eucalyptus microtheca with mixed species over perennial grasses27 Lysiphyllum cunning hamii over perennial grasses42 Chrysopogonfallax, Sehima nervosum, Sorghum plumosum, Theme a rian r20 Eucalyptus microtheca (with Excoecaria parvifolia) over perennial grasses3 Eucalyptus microtheca, Terminalia platyphylla4 Eucalyptuscamaldulensis, EucalyptusmicrothecaI Monsoonspecies

VEGETATION CLASS

FITZMAURICE6 Eucalyptus miniata (with Eucalyptus tetrodonta, Gorymbia bleeseri, Gorymbia

dichromophloia) over hummocks12 Gorymbia phoenicea over hummock (with annual) grasses10 Eucalyptus tectifica over annual and perennial grasses28 Terminalia canescens, Erythrophleum chlorostachys over annual grasses2 MeIaleuca Ieucadendrawith mixed species13 Gorymbia phoenicea, Gorymbia dichromophloia over hummock grasses15 Gorymbia Iatifolia over hummock grassesI Monsoonspecies3 Eucalyptus microtheca, Terminalia platyphylla

IKYMBON13 Gorymbia phoenicea, Gorymbia dichromophloia over hummock grasses24 Me Ialeuca viridiflora over perennial grasses40 Terminalia spp, Owenia vernicosa (with mixed species) over hummock grasses12 Gorymbia phoenicea over hummock (with annual) grasses18 Gorymbia polycarpawith mixed species28 Terminmalia canescens, Erythrophleum chlorostachys over annual grasses27 Lysiphyllum cunning hamii over perennial grasses25 MeIaleuca minutifolia, MeIaieuca sencea over annual and perennial grasses4 Eucalyptuscamaldulensis, Eucalyptus microtheca2 MeIaleuca Ieucadendrawith mixed speciesI Monsoonspecies3 Eucalyptus microtheca, Terminalia platyphylla

%AREA

7.1

6.7

12.19.4

8.14.23.9

1.9

0.7

<0.05

KOOLENDONG

5 Eucalyptus miniata, Eucalyptus tetrodonta over annual and perennial grassesCOMMERCIAL-IN-CONFIDENCE

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.

29.821.610.18.9

7.66.83.4

O. I

<0.05

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I

24.89.89.38.16.8

6.04.3

3.4

0.3

0.1

<0.05

<0.05

.

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28 Terminalia canescens, Erythrophleum chiorostachys over annual grassesGorymbia Iatifolia over perennials30

Gorymbia Iatifolia over annual and perennial grasses with sedges14

Gorymbia phoenicea over hummock (with annual) grasses12

MeIaleuca minutifolia, MeIaleuca sericea over annual and perennial grasses25

2 MeIaleuca Ieucadendra with mixed species29 Gorymbia Iatifolia over hummock grassesI Monsoonspecies

LALNGANG6 Eucalyptus miniata (with Eucalyptus tetrodonta, Gorymbia bleeseri, Gorymbia

dichromophloia) over hummocks7 Eucalyptustetrodontawith mixed species12 Gorymbia phoenicea over hummock (with annual) grasses28 Terminalia cariescens, Erythrophleum chlorostachys over annual grasses

15

Gorymbia polycarpawith mixed speciesGorymbia Iatifolia over annual and perennial grasses with sedgesGorymbia dichromophloia (Eucalyptus tetrodonta, Eucalyptus miniata) over annuals

3.7and hummocks3.62 MeIaleuca Ieucadendrawith mixed species

43Xerochloasp, Eleocharissp. 0.525 MeIaieuca minutifolia, MeIaleuca sencea over annual and perennial grasses 0.2

0.1I Monsoonspecies

18

149

.

LITTLE FITZMAURICE12 Corymbia phoenicea over hummock (with annual) grasses10 Eucalyptus techfica over annual and perennial grasses6 Eucalyptus miniata (with Eucalyptus tetrodonta, Gorymbia bleeseri, Gorymbia

dichromophloia) over hummocks2 MeIaleuca Ieucadendrawith mixed species5 Eucalyptus miniata, Eucalyptus tetrodonta over annual and perennial grasses31 Eucalyptus papuana, Gorymbia polycarpa, Eucalyptus bigalerita over perennial

grasses28 Terminalia canescens, Erythrophleum chlorostachys over annual grasses13 Gorymbia phoenicea, Gorymbia dichromophloia over hummock grassesI Monsoonspecies

:

13.012.19.477

6.1

5.94.9

0.1

MTTHYMANAN25 MeIaieuca minutifolia, MeIaleuca sericea over annual and perennial grasses24 Me Ialeuca viridiflora over perennial grasses

Lysiphyllum cunning hamii over perennial grasses27

Gorymbia phoenicea over hummock (with annual) grasses12

Corymbia Iatifolia over annual and perennial grasses with sedges14

11 Eucalyptus techfica over hummock grasses32 Eucalyptus microtheca with mixed species over perennial grasses2 MeIaleuca Ieucadendrawith mixed species4 Eucalyptuscamaldulensis, Eucalyptus microtheca3 Eucalyptus microtheca, Terminalia platyphyllaI Monsoonspecies

22.115.0

11.78.88.1

6.1

WESTERN HILLS

40 Terminalia spp, Owenia vernicosa (with mixed species) over hummock grasses29 Gorymbia Iatifolia over hummock grasses

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29.2

23.4

13.0

11.57.5

3.43.2

2.8

0.1

19.2

16.28.5

7.96.5

4.94.6

1.5

0.9

0.2

<0.05

19.3

17.5

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Gorymbia phoenicea, Gorymbia dichromophloia over hummock grassesEucalyptus miniata (with Eucalyptus tetrodonta, Gorymbia bleeseri, Gorymbiadichromophloia) over hummocks

45 Pleatrachne spp41 Acacia spp over hummock grasses48 Mangrove43 Xerochloa sp, Eleocharis sp.I Monsoonspecies

MeIaleuca Ieucadendra with mixed species2

MeIaleuca minutifolia, MeIaleuca sencea over annual and perennia grasses25

136

YAMBARRAN33.0

Gorymbia phoenicea over hummock (with annual) grasses12

Eucalyptus miniata (with Eucalyptus tetrodonta, Gorymbia bleeseri, Gorymbia621.3

dichromophloia) over hummocks I 0.2Eucalyptus teatifica over annual and perennial grasses10

7.9MeIaleuca Ieucadendra with mixed species257

7 Eucalyptustetrodontawith mixed species28 Terminalia canescens, Erythrophleum chlorostachys over annual grasses

3.315 Gorymbia Iatifolia over hummock grasses5 Eucalyptusminiata, Eucalyptus tetrodonta over annual and perennial grasses

1.643 Xerochloa sp, Eleocharis sp.O. I

I Monsoonspecies4Eucalyptuscamaldulensis, Eucalyptusmicrotheca 0.125 MeIaleuca minutifolia, MeIaleuca sencea over annual and perennial grasses 0.1

<0053 Eucalyptus microtheca, Terminalia platyphylla

16

6 IMPACTS ASSOCIATEDWITH INFRASTRUCTURE DEVELOPMENT

Infrastructure development on BFTA as outlined in Anexe B to the BFTA RSB datedNovember 1996 is likely to exert a range of impacts on vegetation. Short-termhigh-impact effects are unavoidable during the actual construction of permanentcamps and airfields, while longer term impacts resulting from concentrated humanactivity, altered drainage patterns, and fire can be minimised by carefulmanagement. The location of infrastructure and the alignment of permanent accessroads can have long-term effects which impact on management success.

13.6

6.6

5.95.55.1

0.8

<0.05

<0.05

<0.05

I

.

No significant limitations on proposed infrastructure development are expected as aresult of vegetation, however the siting of the Yarnbarran Campsite and access roadwill need to be carefully planned to minimise potentially detrimentalimpacts on t eriparian habitats in the area. Generally, the site is occupied by eucalypt woodlan

however access to the KOIlendong Valley from the proposedand open-woodland,both of whichcampsite is likely to be through two gaps in the north-south ridge,

to vehicular traffic. Considerationcontain riparian habitats that may be sensitiveCOMMERCIAL-IN-CONFIDENCE

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should be given to providing alternative access from the Yarnbarran Campsite to the

KOIlendong Valley to avoid the streamlines.

Construction of the Yarnbarran Ring Road across the Yarnbarran Plateau has the

potential to impact significantly on a number of sensitive riparian and monsoon

habitats in the area. Careful siting is required to avoid potential damage to the

pockets of monsoon forest in the deeply dissected gorges in the headwaters of

Lobby Creek and the southern tributaries of the Little Fitzmaurice River. It is likely

that the road alignment would have to closely parallel the Little Fitzmaurice

headwaters to avoid steep cliffs and gorges, and this would necessitate the

construction of crossings on major tributaries and probably the Little Fitzmaurice

itself. The riparian habitats along these streamlines are considered sensitive and

should be avoided if at all possible.

Construction of primary access roads through woodland and open-woodland on

BFTA should be undertaken with a minimum of clearing. Cleared lanes of 50 to 80

metres width are often considered necessary for road construction, however much

narrower corridors should be specified, particularly on the plateaux. The practice of

pushing trees to the edge of the cleared lane should also be avoided. The dead logs

will usually catch fire and burn during the following dry season, and ifthey have been

pushed up against living trees, the intensity and duration of heat will killthe standing

trees and widen the corridor even further. Trees felled during road construction

should be pushed to the centre of the cleared lane and burnt.

17

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7 EXERCISEIMPACTS AND MANAGEMENTOF DISTURBANCE

Clearly, exercise activity on BFTA will have direct and indirect impacts on vegetation.

Vegetation will be directly damaged by firing ordnance and vehicle manoeuvres. The

degree of damage will vary with size of ordnance and class of vehicle, and with the

intensity of use. Those areas that are used most frequently and carry the heaviest

traffic will suffer the greatest impact. Longer term damage sustained from military

exercises will vary with vegetation and soil type. (The trafficability of soils is

discussed in the report dedicated to BFTA soils and will not be discussed in detail

here). Indirect changes include invasion of weed species (see section 6.5), changes

in the structure and composition of the vegetation, and loss of species. Changes to

the vegetation structure in impact areas however, may not always be derrimentalinthe context of the land use.

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7.1 Impacts on habitats

Table 7 gives a general ranking (low, medium, or high) of the sensitivity of the eight

vegetation structural classes to a range of military activities on BFTA. The sensitivityranking of each mapping unit within these structural classes is shown in Appendix 8.

The ranking takes into account the conservation status of the vegetation and theresilience of vegetation to disturbance from military exercises and associatedactivities. Important assumptions of the ranking are that:

. areas are monitored and rested when appropriate so that vegetation canrecover before further disturbance;

18

. exercises are not conducted during the rainy season. No areas on BFTA are

suitable for vehicle manoeuvre during the wet, except for bare sandstone

areas. On the Yarnbarran Plateau, a perched shallow water table exists

during the wet season, and vehicles will become bogged wherever soil depthexceeds vehicle ground clearance.

. firecontrolstrategieshavebeeneffectivelyimplemented

The degree of impact will vary within these rankings depending on the type andintensity of exercise. The main training areas are:

. High Explosive Impact Areas (HEIA's)in which live firing may be practicedwith all types of ammunitions which have the potential to contribute tounexploded ordnance (UXO) contamination.

. Field firing areaswhich are for field firing practices using ammunitions that donot have the potential to leave UXO. Hand grenades and pyrotechnics maybe fired in these areas.

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. Dismounted training areas which are for conducting operations that do notinclude vehicle manoeuvre. Such areas are suitable for infantry minor tactics,

survival and adventurous training.

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Manoeuvre training areas which allow land force combat and supportelements to manoeuvre and deploy on and off road on foot, in wheeled or

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tracked vehicles, or by aircraft, and offensive and defensive operations

practice.

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The vegetation communities that are likely to be the least affected by military

activities are open woodlands and grasslands on clay plains and sandy loams, apart

from Xeroch/oa (Table 7). Open woodlands on BFTA generally occur on plains with

clay soils which are relatively stable when dry. The foliage cover of trees in these

communities is relatively low at less than 109"., and hence the damage from

horizontally fired ordnance would be low compared to forest and closed forest

communities. Most tree and shrub species of tropical savanna woodlands have the

ability to regenerate from jignotubers or epicormic buds following disturbance such

as fire, and this could be expected to contribute to their recovery following damage

from ordnance or vehicles. It is important that trees are given time to recover to the

point where they can withstand further disturbance.

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The areas that would be most severely impacted by a range of military activities are

monsoon forests, riparian habitats, and sandstone habitats.

Table 7

Ranking of habitat sensitivity to exercise impact within training sectors onBFTA

.

,

Habitat

Monsoon forest'

Ri arian'

EUCalypt open-forest,woodland on sandstone1,2

EUCalypt open-forest,woodlandoncla lains

EUCalypt open-forestwoodland on sand loams

MeIaleuca minutifolia lowwoodland3Low o en-forest, woodland

HEl

I

EUCal

Hi

Other o

Hi

h

Shrublandon sandstonet. 2

Highh

t o en-woodland

Xerochloa rasslands3

Field firin

Other Grasslands

Medium

en-woodland

Hi h

Hi h

'indicates that habitat is relatively sensitive to disturbance, ' indicates that the habitatcontains rare species, 'indicates that the habitatis of conservation significance.

I

Medium

High

High

Low

Dismounted

Medium

Hi h

Low

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Low

Hi h

Low

Medium

High

Hi h

Hi h

Low

Low

Low

Manoeuvre

Low

Low

Hi h

Low

Hi h

Hi

Medium

High

Hi

h

Low

h

Low

Medium

Low

Low

High

Medium

Medium

High

Low

Medium

Low

Low

Hi h

Hi h

Low

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7.2 Sensitive habitats

Habitats may be regarded as ecologicalIy sensitive ifthey are adversely affected by,and have little resilience to, disturbance. Disturbance may be natural, for example

fire and cyclone, or human induced, for example cross-country vehicle manoeuvre.

7.2. I Sandstone habitats

Sandstone habitats may be indirectly impacted by military activities because they areadversely affected by frequent fire, and some military activities will be associatedwith a medium to high fire risk. Sector(s) in which an exercise is planned wouldrequire active fire management by fuelreduction burns prior to the commencementof exercise activity. Regeneration for many sandstone species occurs only from seedand many are unable to resprout after fire. Such species include Camris intratropica,of which the reduction in abundance as a result of changed fire regimes has been

well documented (eg. Bowman and Panton 1993). Whilst most species may befertile by the third growing season after fire, some may take up to five years or moreto produce seed, particularly those species that occupy harsher, rocky sites(Russell-Smith at a/. in press). Thus, if fire frequency is high, plants may be killedprior to seed production and, overtime, the local survival of obligate seeding speciescould be threatened. The Yarnbarran Plateau suffered an extensive late fire in 1995,

and it is strongly recommended that the area be protected from another hot fire overthe next few years' Clearly, the protection of sandstone habitats from frequent firewill be difficult to achieve, particularly in the Yarnbarran Sector. The Inaccessabilityof sandstone habitats in the Western Hills, and their relative unsuitability for mounted

exercise, should allow a desirably low fire frequency to be maintained in that area.Care would be needed to ensure that no late season fires occurred in the KOIlendong

Valley, which could move into the Western Hills Sector ahead of south-easterlywinds. Sandstone areas may be suitable for dismounted troop training and smallarms training, withoutthe need to burn each year.

20

7.2.2

.

Monsoon forests

Monsoon forests occupy a range of landforms including perennial springs (eg. site126), seasonalIy flooded lowland habitats (eg. site 144) and sandstone escarpments(eg. site 87) (Russell-Smith 1996). Monsoon forests generally occur as relativelysmallisolate pockets within Eucalyptus and MeIaleuca woodlands, and occupy onlyabout 330 ha, or considerably less than 0,059", of BFTA. Some of these areas are

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permanently wet and soils are highly organic peat. As such, they have no resistance

to trampling and their structure is quickly destroyed.

Whilst monsoon forest patches would provide ideal refuges from surveillance during

military exercises, these areas are considered too sensitive to be used for this

purpose. It is most strongly recommended that access to monsoon forest patches by

vehicles or personnel be strictly prohibited throughout the training area. Furthermore,

buffer zones to reduce the possibility of ammunition falling within at least 500 in of

monsoon forest patches is strongly recommended. It is important that monsoon

forests be protected from fire during the dry season, hence appropriate fire

protection measures are recommended prior to military exercises in such areas.

Burning back from the margins of monsoon patches very early in the dry season

could be actively undertaken to provide protection from late season wild fires that are

potentially destructive to fire sensitive habitats.

Monsoon forests also require protection from disturbances such as human activity,

feral animals, and weeds (section 6.5). Feral pigs favour such habitats because they

provide food and shelter, and were present in each of the monsoon forests recorded

in the 1997 survey. As a result, the soil was severely disturbed in localised areas.

Feral pig eradication should be attempted as a matter of priority. Feral animal control

and fire management are discussed in detail in other reports.

Riparian habitats

The banks of water courses are particularly sensitive to disturbance because they

are flooded during the wet season and soils are generally sandy. Removal of

vegetation from river banks results in erosion, often in the form of deep rills and

gullies. Erosion along river banks increases the sediment load in the water which

results in siltation of shallow areas and a consequent reduction in water quality. This

has an adverse impact on aquatic flora and fauna. Riparian zones are important as

movement corridors for wildlife (Bunn 1996).

Riparian areas are also susceptible to weed invasion because of water availabilitythrough most of the year, and the introduction of weeds by transportation of seeds

and propagules down the watercourse. This is demonstrated by the factthat 13 out

the 14 weed species recorded on the BFTA in June 1997 occurred along the Victoria

River. Weed infestations require active and regular management strategies.

Therefore, preventing introduction so that no active treatment is required is the most

effective means of weed management.

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To protect sensitive riparian areas from disturbance that will inevitably result inerosion and weed problems, it is recommended that large water courses on theBFTA such as the Victoria, Ariagalarri, Ikymbon and Fitzmaurice rivers, be protected

by an appropriate buffer zone, except at crossing points. Existing environmentaldegradation within those zones should be actively managed to minimise furtherdamage. For example, large gullies may need earthworks to prevent further loss ofsoil, and weed species may require treatment to prevent further spread. In areaswhere there is no ground cover vegetation, and depletion of the soil seed bank isevident, revegetation using appropriate native species may be necessary (seesection 6.4).

22

7.2.4 Coastal habitats

Coastal habitats were not assessed in this survey. Some general comments,

however, can be made on the characteristics of these areas. These areas will beextremely sensitive to vehicle movement because the sandy soils will have littleresistance to traffic. The marine habitat on the western boundary of the BFTA may

be important for a number of vulnerable species including dugong, turtles, andmigratory birds. Littoral habitats along the muddy tidal reaches of the major tidalcoastal river systems in the NT, such as the Victoria and Fitzmaurice, are speciesrich and diverse.

The littoral systems on BFTA should be regarded as sensitive to high impact militaryexercises. However, they may be suitable for dismounted training.

Habitats of conservation significance

Two vegetation types that are of conservation significance because they occuralmost exclusively in the VictoriaBonapart biogeographic region and are currentlynot protected in the reserve system of the NT, are MeIaieuca minutifofia lowwoodland (mapping unit 25) and Xerochloa grassland (mapping unit 43).Conservation of these units by minimising disturbance from military activities should

that maintain the habitat structure should bebe a priority. Burning regimes

implemented. For example, some grasslands may require occasional hot fires tosuppress the growth and abundance of tree and shrubs, and early dry season fires inmost other years'

7.3

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7.4 Management of species of conservation significance

Management of species of conservation significance is dependent on the habitat in

which such species occur. Thus, the management of rare and threatened species in

the wild can only be practiced at the habitat level rather then the species level. The

three species of conservation significance found during this survey were recorded in

sandstone habitats, the management of which is discussed in 6.2. I above.

7.5 Ground cover

23

Military exercises, especially vehicle manoeuvres, are known to reduce the cover of

understorey species by pulverisation (Preece at a1. 1996). Damage will be increased

by multiple tracking of wheeled and tracked vehicles overthe same ground.

Some herbaceous species will be more susceptible to disturbance by military traffic

than others' Annual species that rely on germination from seed for regeneration willbe most vulnerable to disturbance, and their distribution is significantly affected by

season and fire (Dyer at a1. 1997). Annual species generally germinate from seed

that has been produced in the previous wet season. During the dry season, seed of

some species, for example Brachyachne spp. and Sprorobolus spp. ,lie on the soil

surface. Seeds may be killed by fire, and thus the carry over seed bank for

germination in the following wet season is reduced.

The dominant herbaceous vegetation type in most areas of BFTA, however, is

perennial grass. Whilst above ground vegetative parts of these plants may be

damaged or severed by sustained military activity, they will readily regenerate fromestablished root stocks when relative humidity increases at the end of the dry

season, and with the first wet season rains. Should ground cover vegetation become

depleted by localised exercise activity, the areas should be rested prior to the wetseason, about late October, to allow time for re-establishment of foliage cover that

will provide protection from possible erosion caused by early wet season storms.

An indirect impact of a reduction in ground cover in some habitats is an increase in

erodability of the soil, and a change in fire regime. The frequency offire in areas withlow herbaceous cover will be reduced and this may eventually lead to a change in

species composition and structure, with an increase in abundance of inid-storeyshrubs (Dyer at a1. 1997).

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Revegetation of heavily impacted areas, either as a result of historical over-grazing

or associated with military activities, may be necessary during the operational and

decommissioning phases of BFTA. Native species only should be used so that

biodiversity is maintained and the integrity of natural systems is not compromised.

Many introduced species have the potential to become weed problems in the longer

term. These species possess characteristics that enable them to displace native

species, for example rapid growth rates, pro^C seed production, high germinationrate, high biomass, and a tolerance to unfavourable environmental conditions.Further, introduced species do not usually have natural predators and thus they are

able to grow unchecked. Most grassy weeds are species that were intentionallyintroduced as improved pasture species. In northern Australia, such species includePennisetum polystachion (mission grass), Androgpogan gayanus (gainba grass),and Brachiaria inutica (para grass). Whilst few native grass species are currently

used for revegetation, there is no reason why they would not be successful provided

application methods are appropriate. The advantages of using native species overintroduced species are:

. native grasses can successfully colonise disturbed areas, and survive and

reproduce;

. seeds are available locally and can bedirectseeded over large areas.

. fertiliser requirement for localspeciesislow;

. selected native grasses will notresult in aweed infestation that outcompetes

native species. Hence, ongoing management is notrequired;

. establishment of native grasses will provide dense cover close to the ground

to suppress weeds by shading; and

. native grasses are welladapted to cope with disturbances such as fire and

drought.

The revegetation of degraded areas on BFTA could provide a valuable opportunity toconduct investigations into the recovery of such areas after varying degrees ofdisturbance. It also presents an opportunity to conduct investigations into appropriatenative herbaceous species for revegetation.

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7.6

;

Weed management

The Northern Territory Weeds Management Strategy 1996 - 2005 (DPI&F 1996) has

a set of six strategic objectives designed to minimise the impact of weeds. Four of

these strategies relate directly to land managers and, therefore, to management ofBFTA:

25

2

3

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Preventing introduction and spread.

Ensuring weeds management is an integral part of land management.

Learning more about weeds, and increasing awarness and education,as an essential basis for land management.

To ensure that the approach to weed controlis strategic, effective, and

consequently, economic, it is necessary to develop a weed management plan. The

plan will essentially revolve around the above three strategies.

The weed management plan should integrate physical and chemical controlmethods, the use of fire, and biological controlif appropriate. The various

species-specific management options, and the optimum conditions under which

these strategies may be implemented, should be described. The treatment will be

appropriate to the weed species and the size of infestaton. Early detection of a weedoutbreak may mean that the treatment will often be a physical one such as hand

pulling or grubbing, or mechanical, such as cultivating. The weed management planshould be an evolving document driven by assessment of the effectiveness of

current strategies and changing land use options. This plan should be incorporated

into the Environmental Management Plan for BFTA.

I

7.6. I Preventing introduction and spread

One of the most powerful weapons in the strategic management of weeds is to

prevent their introduction in the first place. For weed invasion to occur, there mustbe an opportunity for invasion and this requires the availability of propagules of aninvasive species capable of dispersing into the area (Hobbs 1991). Inadvertentmovement of weed seed and propagules by humans has been recognised as the

majorfactor influencing the distribution of introduced species (Chaloupka and Do mm1986). Soil, construction materials and vehicles are likely to be carriers of alien plantmaterial into a region. Cowie and Wemer (1987) surveyed alien plants of Kakadu

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National Park and found that most of the naturalised alien species were associated

with human activity such as roadways, borrow pits, settlements, campgrounds, andother disturbed areas. Also, areas adjacent to floodplains and creeks were found to

be heavily infested with weeds.

Washdown of vehicles

Preventing the introduction of alien plants onto BFTA will require stringent quarantinemeasures. These measures must include washing down all off-road vehicles, before

entering and leaving the property. The provision of washdown points as part of theinfrastructure development is noted. Areas on BFTA with known weed infestallonsshould be considered off limits, particularly to vehicles, so that, as far as possible,infestations are contained within that area. Vehicles should travel along graded

tracks and roads, whenever non-tactical, rather than across country, to reduce the

likelihood of transporting weeds.

There is a heightened risk of new weed species introduction to the training areaconstruction workers andduring the infrastructure development phase, as

contractors are unlikely to appreciate the need for vehicle washdown, however thisshould be specified in the construction contracts, and actively policed.

Regularsurveillance

Routine surveys of susceptible areas such as roadsides and embankments shouldbe scheduled on a regular basis, particularly during the wet season when plants areactively growing and more easily detectable. Road sides represent a heavilydisturbed system and thus are highly susceptible to weed invasion. Weeds alongroadsides develop a reservoir of weed seed that is easily spread by roadmaintenance vehicles, passing traffic, and animals.

Mimosa pigra (mimosa) infests large areas of the Daly River system including theDaly River Aboriginal Reserve, north of the Fitzmaurice River. Mimosa is consideredto be one of Australia's worst environmental weeds because it can alter the floristic

composition of natural wetlands, thereby decreasing habitat diversity (Braithwaite ata1. 1989; Lonsdale 1993). It is a leguminous shrub that, in wetter areas such aschannel banks, billabongs and floodplains, forms dense thickets that are difficult to

penetrate. It currently covers more than 80 000 hectares in the Northern Territory,with severe infestations on the Adelaide, Mary, Finniss, Moyle and Daly Rivers

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systems. To date, mimosa on the Daiy River Reserve has spread as far as Palumpa

Station, about 20 kin from the mouth of the Fitzmaurice (F. Maurer pers. coinm.

1997). Due to the rugged terrain between the edge of the infestallon and the mouth

of the river, however, it is unlikely to naturally advance much further (F. Maurer pers.

coinm. 1997). However, mimosa could be inadvertently transported to the river by

vehicle and subsequently spread to BFTA via seed floating down the river. Aerial

surveys along the northern boundary of the Fitzmaurice River are recommended to

ensure that any outbreaks of mimosa in particular, but also other weed species, are

detected early.

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Liaison with neighbours

Weed populations are not usually confined by property boundaries. For a weed

control program to be effective, it is important that there is cooperation between

neighbouring land managers and local government agencies such as DPI&F weeds

section in Timber Creek. Effective control of some species, for example mimosa,

may need to be conducted at a catchment level rather than regional level. Liaison

with adjacent land managers will increase awareness of weed issues and lead to

more effective management and control on a regional level.:

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Early intervention

Studies on patterns of weed spread indicate that many species have a long lag

phase following introduction before they spread explosiveIy (Hobbs and Humphreys

1995). Therefore, it is important that smallinfestations be treated soon after

detection to reduce the likelihood of uncontrolled spread.

Clearly, the size and inaccessibility of BFTA means that weed species, habitats, and

weed infested areas need to be prioritised. Weed species that should be targeted

first are those that are rapid invaders and serious weeds of conservation. Such

species would include parkinsonia, noogoora burr, mimosa, and other species that

could potentially occur on BFTA, such as gainba grass and mission grass. Habitats

that should be given priority are those that are most susceptible to weed invasion, for

example riparian habitats and disturbed areas. Areas of infestaton that should be

given priority for control are those that are small enough to have a reasonable

chance of success. Weed outbreaks within training areas should also be given

priority treatment because the relatively high localised disturbance caused by military

activity may significantly increase the rate of spread of these infestations. If possible,.

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these areas should be avoided, or if necessary, the military exercises should be

redirected to another region.

Currently, the weeds that cover substantial areas of BFTA are noogoora burr along

the Victoria River and hyptis which is widespread (L. Corbett pers. coinm. 1997).

Further surveys of susceptible areas are needed to map infestatons of these and

other weed species. If major weed problems should develop, they may be too

intractable to be tackled economicalIy. Under these circumstances, the invaded

areas may be relegated to holding operations where efforts are put into preventing

further spread rather than into control(Hobbs and Humphries 1995).

Ensuring weeds management is an integral part of land management

Weed management is a component of sustainable land management and as such is

an integral part of active land management (DPI&F 1996). A focus on the invaded

ecosystem and its management, rather than simply on the invading species, is likely

to more effective (Hobbs and Humphries 1995). The changes that allow the initiation

or spread of weed invasion need to be addressed before effective control can be

achieved (Hobbs and Humphries 1995). The underlying causes of ecosystemmodification that enhance weed invasion therefore need to be identified in order to

develop effective management programs. All of the weed species recorded on BFTA

in June 1997 occurred in heavily grazed areas, particularly along water courses such

as the Victoria River. It is likely that the removal of grazing integrated with

appropriate active management strategies will, in the longer term, reduce theabundance of most weed species in these areas through competition with native

species.

28

7.6.2

Minimising disturbance

Should weed seed or propagules be introduced, suitable micro-sites have to be

available for successful establishment to occur. Disturbance is a major factor

affecting the susceptibility of natural ecosystems to invasion. Weeds are quick toinvade disturbed areas such as overgrazed pastures, construction sites, and

roadsides. Disturbances generally change the characteristics and availability of

microsites for establishment and they may also affect the opportunity for dispersal,

for example where feral animals or floods transport seeds into new areas (Hobbs

1991). Military exercises will cause considerable disturbance to the landscape in

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designated areas and will thereby provide favourable conditions for weed

establishment should they be introduced.

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The major principles for management of disturbance are (Hobbs 1991):

. the natural disturbance regimeshould be maintained asfaras possible;

. prevention of weed invasion should be used to manage weeds, rather than

direct control;

,

29

. disturbance due to human activity should be minimised

causes rather than symptoms of problems should be treated;.

.

. synergism often operates between different types of disturbance for

example, the environmental impact of weed invasion in an area where

vegetation has been removed may be greater than the sum of the twodisturbance effects.

Feralanimalcontrol

Weed seeds and propagules may be spread by feral animals such as pigs and

donkeys. Grazing by donkeys and rooting by pigs removes native vegetation anddisturbs the soil surface. Pigs tend to prefer habitats that are particularly susceptible

to weed invasion, such as monsoon and riparian forests. Feral animal control,

therefore, is crucial to the success of any weed management program.

.

Feral animal catchers should also be made aware of the potential for their activities

to introduce and spread weeds. Their vehicles should adhere to the same wash

down requirements as military vehicles.

Rotating utilised areas within HEIA's

Whilst removing cattle will lead to an increase in the cover of understorey species,

particularly grasses, mobilisation of heavy machinery is likely to reduce vegetationcover and thus increase susceptibility to erosion and weed invasion. Resting areas

within training areas on a rotational basis may be necessary to prevent serious land

degradation. Once use of a particular area ceases, revegetation with suitable native

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understorey species will increase the rate of recovery and reduce the risk of erosionfrom wind and rain.

7.6.3 Learning more about weeds -research and monitoring

Efficient and effective weed management requires knowledge of the occurrences

and their direction of spread. A database that documents this information as well as

information on treatments that have been applied will be invaluable in assessing the

effectiveness of management strategies. Strategies can then be adjusted if

necessary.

30

Well designed research trials and monitoring will assist in assessing the importance

of an integrated approach to weed prevention and controlthrough the use of fire,

and physical and chemical methods. This may be particularly important during the

decommissioning of BFTA.

Increasing awareness and education

Users of BFTA need to be made aware of those weed species which occur or could

occur in the region, and the detrimental affects of these weeds on the environment

and quality of the land use. All personnel have a responsibility to minimise the

potential impact of introduced species, and will be required to observe certain

management directives, such as vehicle wash down, and avoidance of weed infested

areas and experimental areas. Specific weed awareness courses should be

conducted on weed identification and weed management. Army personnel can then

assist by reporting occurrences of weeds, and by avoiding further disturbance to or

spread of weeds.

Weed education and assistance can be provided by weed experts such as the

DPI&F weeds branch. Frank Maurer and Greg Hore, based at Timber Creek, are

responsible for weed management on the Daly River Reserve.

7.6.4

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8 MONITORING

G

While the primary objective of land management on the BFTA is to facilitate militarytraining, this can only be achieved in the medium and longer term by promoting and

maintaining sustainability and biodiversity of the landscape. Sustainability depends

on the ability of the landscape to recover from disturbance. Little research has been

done on the recovery of land from military activity in the tropics, but clearly it is

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important to increase knowledge in this area so that the optimum use of the land canbe achieved.

Managers often find it difficult to achieve land use sustainability because of lack of

data on which to base their management decisions (Ludwig at a1. 1997). Hence, it is

very important to provide baseline data so that impacts can be measured against abenchmark. Also, the condition of impacted areas should always be compared to the

condition of similar vegetation communities that have not been affected by military

activities or grazing. These relatively undisturbed areas may be used as control sites

that reflect natural changes to the environment. All sites, ie. impacted and control,

should be replicated to account for variation in recovery rate due to environmental

factors such as hydrology, species composition, and rainfall.

Monitoring should occur annually and at the same time of year to avoid seasonal

variation in the presence and abundance of species. This information should be

gathered with other important indicators of land condition, especially soilsinformation.

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8.1 Recovery of degraded areas after destocking

Parts of the BFTA are currently degraded by overgrazing and consequently, are

severely eroded. Excluding further disturbance from these areas, and monitoring the

natural recovery of selected sites in terms of vegetation cover and soil structure, will

provide valuable insights into the resilience or, conversely, fragility of these

ecosystems to disturbance. Other similarly disturbed areas could be actively

rehabilitated by stabilisation through earthworks then re-seeding at the start of the

wet season. Comparison of the recovery rate between areas that have been left to

recover naturally and those that have been actively rehabilitated will be extremely

useful for developing land management plans for both the operating and

decommissioning phases of BFTA. The condition of the natural and manipulated

rehabilitating areas should be compared to that of relatively undisturbed areas so

that a judgement can be made on the rate and extent of recovery.

Impact of military activities

To assess the sustainability of various vegetation units under a range of military

activities, and the recovery of areas once activity ceases, permanent sites should be

established and monitored for changes to species composition, abundance, and

cover. Monitoring of landscape function and processes can be achieved by

8.2

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measuring key indicators. These indicators may include soil surface condition

(vegetation cover, soil crust, topography), erosion features, and the capacity of the

land to capture and cycle water and nutrients.

Regular monitoring will eventually allow predictions to be made on the cumulative

impact of specific activities in different vegetation communities and associated soil

types. Variation in impacts will occur with season, the condition of the land prior to

military activity, and fire regime. It should be noted, however, that only low impact

activities, such as dismounted exercises in rocky areas, should be conducted during

the wet season because soils will be saturated and thus their structure will be easily

destroyed.

Rotating exercise areas at the optimum time will be a key strategy in balancing

ecological sustainability and maximum land use. The recovery rate of areas that are

rested from activity will give an indication of the frequency at which the use of impact

areas should be rotated. Re-establishment of vegetation after disturbance is criticalIy

important for ecosystem sustainability. Therefore, it is important that areas be rested

prior to the occurrence of significant damage to perennial plants, and to depletion of

the seed bank either through loss of seed-producing plants or by destruction of seed.

32

Overuse of exercise areas may mean that active rehabilitation is required to

minimise further damage and to accelerate the process of recovery toward a

sustainable system. Revegetation over extensive areas, however, is expensive and

labour intensive. Therefore, degradation of the land to a point where active

revegetation is necessary should be avoided at all costs.

Remote sensing can be useful to monitor changes to land condition on a broad

scale. Sources of remoteIy-sensed data include satellites, airborne scanners and

airborne video systems. The most common sources of satellite data for land

condition monitoring are Landsat, Spot and NOAA-AVHRR (Advanced Very High

Resolution Radiometer) systems (Campbe11 1996). It is important to collect quality

ground-truth measurements to relate satellite and airborne responses to actual landsurface features.

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Photographs taken from permanent photopoints using a standard lens, and at the

same time every year, are an effective means of monitoring changes in land

condition. They provide a visual historic record. Photographic monitoring is easily

repeatable and requires no special expertise.

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8.3 Education of military personnel

Personnel that actually use impact areas are in the best position to detect

detrimental environmental impacts. Education of key personnel on environmental

management and their communication with environmental management staff will

significantly enhance achievement of the objective to maintain sustainability of

training areas. The ability of environmental staff to evaluate and reinediate

environmental problems will be greatly enhanced if they are trained in ecological

principles, have local knowledge of ecosystems, and keep up to date with the latest

environmental practices. Liaison with appropriate people in other organisations for

advice and assistance is to be encouraged.

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9

9.1

CONCLUSIONS AND ACTIONS

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Sensitive habitats

Most of BFTA is suitable for the range of military exercises that are planned, and

irreversible impacts are unlikely provided that impacted areas are rested before

damage occurs. The 1997 vegetation survey identified three habitats that are

environmentally sensitive to the disturbances associated with military landuse:

Sandstone areas in the Western Hills, Yarnbarran, Koolendong, Wombungi,

and Mt Thymanan training sectors are suitable for dismounted exercises andwheeled vehicle manoeuvre but should not be used for live firing or other

activities that pose a significant fire risk. Sandstone areas require a fire-free

interval of at least five years so that obligate seeding species are able to

mature, produce seed and sustain the population between fire events.

Further, species that are listed as rare were recorded from the Western Hills,

Yarnbarran and Mt Thymanan sandstone areas. Sandstone areas cover a

significant proportion of BFTA. Therefore, the use of these areas for activitiesother than dismounted exercises needs to be rotated so that substantial

areas of this habitat on BFTA remain undisturbed for several years at a time.

.

.

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. Monsoon forest areas are highly sensitive habitats and require protection

from fire, weeds, feral animals, and all human impacts. Therefore, they must

be considered unsuitable for any form of military exercise. Careful fire

management in the vicinity of monsoon forests is crucial to their continued

integrity on BFTA.

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. Riparian habitats are also sensitive to disturbance because soils are

generally sandy and seasonalIy inundated. Flood waters significantly

increase the risk of erosion. These habitats are also susceptible to weed

invasion. Appropriate buffer zones (suggested I kin wide) from the banks of

major water courses such as the Victoria, Angalarri, Ikymbon, and

Fitzmaurice Rivers, within which vehicle or human disturbance should be

greatly minimised or restricted altogether, would protectthese fragile habitatsfrom further erosion.

9.2

34

Habitats of conservation significance

MeIaieuca minutifolia low woodland and Xerochloa grassland are of conservation

significance because they are restricted to the Victoria-Bonaparte bioregion. Whilst

these habitats may be relatively resilient to most military exercises, activities in these

areas should be restricted to low intensity dismounted exercises so that their

preservation is assured.

9.3 Weeds

Weed management strategies for infested areas along river banks and other areas

should be put in place as soon as possible to prevent further spread. The weed

management plan should have an integrated approach using chemical, physical and

fire treatments where appropriate forthe weed species and infestation.

Monitoring

The importance of monitoring the impacts of military activity on vegetation cannot be

overstated. The sustainabilty of the exercise areas, and hence the achievement of

optimum land use, will depend heavily on the effectiveness of monitoring techniques.

Every effort should be made to develop a set of key indicators that prescribe when

training areas should be rested from disturbance until recovery is sufficient to

tolerate further exercise impact. Monitoring should also provide an invaluable

opportunity to demonstrate and document rangeland improvement under Defence

management, which will contribute significantly to the reputation of Defence as a

successful land manager in the region.

9.4

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10 ACKNOWLEDGEMENTS

^

Nick Smith of the NT Herbarium for identifying numerous specimens; Department of

Lands, Planning and Environment for providing data from earlier surveys; Chris

Devonport and Kale Sanford-Readhead of NTU for providing the site map, assistingwith the vegetation map, setting up the GIS and manipulating the databases; Laurie

Corbett for assistance with the final report.

11 REFERENCES

35

,

Braithwaite, R W, Lonsdale, W M, and Estbergs, J A, 1989. Alien vegetation and

native biota in tropical Australia: the impact of Mimosa pigra. Bidogica/Conservation 48,189-210.

.

:

,

Briggs, J D, and Leigh, J H, 1995. Rare or Threatened Australian Plants, CSIRO

Publishing, Melbourne, page 243.

Bowman, D M J S, and Panton, R, 1993. Decline of Camris intratropica in the

Northern Territory:implications for pre- and post-colonisation fire regimes.

Journal of Blogeography20, 373-381.

Brock, J, 1988. Top End Native Plants, John Brock, Darwin, NT, page 8.

Bunn, S, E, 1996. Management and protection of riparian zones in tropical

savannas. In: Proceeding of a workshop on Land Management Resrach forthe

Army's Townsville Field Training Area (TFTA), pages 32-35.

Campbell, N, 1996. Land condition assessment and monitoring using

remoteIy-sensed data. In: Proceeding of a workshop on Land Management

Resrach forthe Army^ Townsvi'/Ie Field Training Area (TFTA), pages 25-27.

Chaloupka, M Y, and Domin, S B, 1986. Role of arithropochory in the invasion of

coral cays by alien flora. Ecology67, 1536-1547.

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Orothers, M, and Newbould, S, 1993. Rubber bush, Agriote No. 551, Department of

Primary Industry and Fisheries, Weeds Branch, Katherine.

Connors, G, Oliver, B, and Woinarski, J, 1996. Bioregions of the Northern Territory. '

conservation values, reservatibn status and information gaps. Final report to

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ANCA National Reserves System Cooperative Program (Project N607), Parks

and Wildlife Commission of the Northern Territory, NT, pages 4/7-433.

Cowie, I D, and Wemer, P A, 1987. Weeds in Kakadu National Park - A survey of

alien plants. Report to Australian National Paraks and Wildlife Service from

CSIRO, May 1987.

DPI&F, 1996. The Northern Territory Weeds Management Strategy 1996-2005.

Government Printer of the Northern Territory.

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Dunlop, C R, Leach, G J, A1brecht, D E, Barritt, M J, Cowie, I D, and Latz P K, 1996.Checklist of the Vascular Plants of the Northern Territory, Australia. Parks and

Wildlife Commission of the Northern Territory.

Dyer, R, Cobiac, M, Cafe, L, and Stockwell, T, 1997. Developing sustainable pasture

management practices for the semi-and tropics of the Northern Territory, MRC

Project NTA022, Final report, Department of Primary Industries and Fisheries,Katherine Research Station.

F1annagan, G J, 1993. Biological control of noogoora burr, Agriote No. 589,

Department of Primary Industry and Fisheries, Weeds Branch, Darwin.

Hobbs, R, 1991, Disturbance a precursor to weed invasion in native vegetation, Plant

Protection Quarterly V01 6(3), 99.04.

Hobbs, R, and Humphries, S E, 1995, An Intergrated Approach to the Ecology and

Management of Plant Invasions, Conservation Biology, V01 9(4), 761-770.

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Lonsdale W. M. (1993) Rates of spread of invading species - Mimosa pigra innorthern Australia, Journal of Ecology81:513-521.

Ludwig, J, Tongway, D, Freudenberger, D, Noble, J, and Hodgkinson, K, 1997. A

landscape perspective on rangeland management, in: Landscape Ecology,Function and Management, Principle from Australia^ Rangelands, page 79-92.

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Miller, I L, 1995, The Northern Ternt^^ry Noxious Weeds Act, Agriote No. 566,

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Parsons, W T, and Cutherbertson, E G, 1992. Noxious Plants of Australia, Inkata

Press, Melbourne, Victoria, page 313-314.

Pitt, J, 1991. Noogoora Burr. Agriote N0 490, Department of Primary Industry and

Fisheries, Darwin, NT.

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Agdex 643.

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ANU, Darwin, pages 217-237.

Russell-Smith, J, Ryan, P G, Klessa, D, Wright, G, and Harwood, R, (in press). Fire

regimes and fire-senstivie vegetation of the sandstone Amhem Plateau,

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weeds of the Northern Territory, Australia, The Environment Centre NT, page 4,

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van Rangelrooy, D S, and Miller, I L, 1993. Parkinsonia, Agriote No. 569,

Department of Primary Industry and Fisheries, Weeds Branch, Darwin.

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Wheeler, J R, Rye, B L, Koch, B L, and Wilson, A J G, 1992. Flora of the Kimberley

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APPENDieES

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Appendix I

Species recorded on Bradshaw Station in June1997

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Appendix I Species recorded on Bradshaw Station in June 1997.

SpeciesAbelmoschus ticulneus

Acacia auriculiformis

Acacia coriacea

Acacia difficilis

Acacia dimidiata

Acacia dunnii

Acacia froggattiiAcacia gallodesAcacia hammondii

Acacia hemignostaAcacia holosercia

Acacia kelleri(3r)Acacia Iatifolia

Acacia IysiphloiaAcacia neurocarpaAcacia nuperimmaAcacia pachyphloiaAcacia pellitaAcacia platycarpaAcacia spAcacia spAcacia spAcacia spAcacia spAcacia spAcacia spAcacia translucens

Acacia turnida

Acacia umbellata

Acacia valida

AChyranthes asperaAdansonia gregoriiAdenostemma Iavenia

Adjantum hispidulum (3rC)Aeschynomene IndicaAlloteropsis semialataA1phitonia excelsaAIStonia actinophyllaAlternanihera nodiflora

Alternanihera pungens*Am inarinia baccifera

Am inarinia multiflora

Ampelocissus acetosaAmyema benthamiiAmyema sanguineumAmyema spAmyemaspAn isQineles malabarica

Antidesma ghesoembillaAristida jailfolia

Aristida dominii

Aristida holathera

Artstida hygrometricaAnstida InaequiglumisAristida Ierichoenis subspinuliferaArtstida Iatifolia

Artstida spAristida spAristida sp

.

:

Bradshaw Station - Veg 97

FamilyMalvaceae

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Mimosoides

Amaranthaceae

Bixaceae

Asteraceae

Adjantaceae

Poaceae

Poaceae

Rhamnaceae

ApocynaceaeAmaranthaceae

Amaranthaceae

LyrthraceaeLyrthraceaeVitaceae

Loranthaceae

Loranthaceae

Loranthaceae

Loranthaceae

Lamiaceae

EuphorbiaceaePoaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

SpeciesAristida spArundinella nepalensisAt alaya hemiglaucaAt alaya variifoliaBacopa floribundaBarring toriia acutangulaBergia pedicellarisBidens pilosa'Blechnum orientale

Blechnum spBlechnum spBlumea diffusa

Blumea tenella

Bonamia pannosaBorreria exserta

80rreria spBOSiaea spBothriochloa ewartiana

Bothriochloa pertusaBrachyachne convergensBrachychiton diversifoliusBrachychiton spBrachychiton viscidulusBreynia cemuaBridelia tomentosa

Brunoniella australis

Buchanania obovata

Buchnera linearis

Buchnera rainosissma

Bulbostylis bamataBulbostylis bulbiferaGalandrinia unitlorum

Callitris intratropicaCalotropis procera*Calytrix achaetaCalytrix browniiCalytrix exstipulataCalytrix verticillataCan arium australianum

Canthium attenuatum

Capparis IasianthaCapparis umbonataCarallia brachiala

Carpentaria acuminataCartonema parviflorumCartonema trigonospermumGassytha aureaGassytha spGassytha spCathormion umbellatum

Gayratia maritimaGayratia infoliaCenchrus ciliarjs*

Centrolepis exsertaCheilanthes seiberi

Chionachne cyanthopodaChionachne spChloris lobata

Chrysopogon fallax

.

FamilyPoaceae

Fabaceae

SapindaceaeSapindaceaeScrophulariaceaeLechythidaceaeElatinaceae

Asteraceae

Blechnaceae

Blechnaceae

Blechnaceae

Asteraceae

Asteraceae

Convolvulaceae

Rubiaceae

Rubiaceae

Fabaceae

Poaceae

Poaceae

Poaceae

Sterculiaceae

Sterculiaceae

SIerculiaceae

EuphorbiaceaeEuphorbiaceaeACanthaceae

Anacardiaceae

ScrophulariaceaeScrophulariaceaeCyperaceaeCyperaceaePortulacaceae

Verbenaceae

AsclepiadaceaeMynaceaeMynaceaeMynaceaeMynaceaeBurseraceae

Rubiaceae

CapparaceaeCapparaceaeRhizophoraceaeArecaceae

Coinmelinaceae

Coinmelinaceae

Lauraceae

Lauraceae

Lauraceae

Mimosaceae

Vitaceae

Vitaceae

Poaceae

CentrolepidaceaeSinopteridaceaePoaceae

Poaceae

Poaceae

Poaceae

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Clerodendrum floribundum

Clerodendrum latei

Cochlospermum fraseriGoleus scutellarioides

Coinmelina SIdoides

Convolvulaceae spConvolvulaceae spCorehorus SIdoides

Gorymbia bleeseriGorymbia confertill oraGorymbia dichromophloiaGorymbia IerrugineaGorymbia joelscheanaGorymbia foelscheanaGorymbia grandifoliaGorymbia IatifoliaGorymbia polycarpaGorymbia ptychocarpaGorymbia terminalisGrinium spCrinum spCrinum spCrinum uniflorum

Crotalaria alata

Crotalaria am hemicus

Crotalaria brevis

Crotalaria crispataCrotalaria medicagineeCrotalaria novae-hollandiae

Crotolaria retusa

Croton am hemicus

Gymbogon bombycinusGymbopogon procerusCynodon dactylonCyperaceae spCyperaceae spCyperaceae spCyperaceae spCyperus holoschoenusCyperus spCyperus spCyperus spDicanthium sericum

Dichanthium Iecundum

Dichanthium spDicrostachys spicataDioscorea bulbifera

Distichostemon am hemicus

Distichostemon hispidulusDodoriaea oxypteraDollchandrone heterophyllaDrosera indica

Drosera lariata

Drosera petiolarisEchinochloa colona

ECtrosia IeporinaECtrosia schultzii

Ehretia salignaEleocharis sp

Verbenaceae

Verbenaceae

Bixaceae

Lamiaceae

Coinmelinaceae

Convolvulaceae

Convolvulaceae

Tiliaceae

MynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeLiliaceae

Liliaceae

Liliaceae

Liliaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

EuphorbiaceaePoaceae

Poaceae

Poaceae

CyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaePoaceae

Poaceae

Poaceae

Mimosaceae

Dioscoreaceae

SapindaceaeSapindaceaeSapindaceaeBignoniaceaeDroseraceae

Droseraceae

Droseraceae

Poaceae

Poaceae

Poaceae

Bombacaceae

Cyperaceae

Bradshaw Station - Veg 97

Eleccharis spEleocharis spElytrophorus spicatusEnneapogon polyphyllusEnneapogon purpurascensEnteropogon spEragrostis cumingiiEragrostis seijioliaEragrostis spEragrostis spEragrostis spEragrostis tenaxEragrostis tenellulaEragtostis cumingiiEriachne armfulI

Eriachne avenacea

Eriachne based owli

Eriachne burkettii

Eriachne ciliata

Enachne fastigiataEriachne glaucaEriachne obtusa

Eriachne pulchellaEriachne spEnachne spEriachne spEriachne spEriachne spEriachne spEriachne SUIcata

Eriachne triseta

Eriocaulon spErythrina vespertilioErythrophleum chlorostachysEucalyptus bigaleritaEucalyptus brevifoliaEucalyptus carnaldulensisEucalyptus microthecaEucalyptus miniataEucalyptus papuanaEucalyptus phoeniceaEucalyptus pruinosaEucalyptus tectificaEucalyptus telrodontaEucalyptus tintinnansEUlalia aurea

EUlalia fulva

Euphorbia tannensisEuphorbiaceae spExcoecaria parivifoliaFabaceae spFabaceae spFabaceae spFicus coronulata

Ficus OPPositaFicus racemosa

Fimbristylis acuminataF1mbristylis clavataFimbristylis densa

CyperaceaeCyperaceaePoaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Eriocaulaceae

Fabaceae

CaeselpiniaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaePoaceae

Poaceae

EuphorbiaceaeEuphorbiaceaeEuphorbiaceaeFabaceae

Fabaceae

Fabaceae

Moraceae

Moraceae

Moraceae

CyperaceaeCyperaceaeCyperaceae

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F1mbristylis macranthaFimbristylis microcaryaFimbristylis pachypteraFimbristylis pallidaF1mbristylis phaeoleucaF1mbristylis pierygospermaF1mbristylis schultziiF1mbristylis schultzii BoeckelerFimbristy!is solidifoliaF1mbristylis spF1mbristylis spF1mbristylis spFimbristylis spFimbristylis spF1mbristylis spF1mbristylis spF1mbristylis spF1mbristylis spF1mbristylis spF1mbristylis spF1mbristylis spF1mbristylis spF1mbristylis spFuirena ciliaris

Fuirena umbellata

Gardenia fucata

Gardenia megaspermaGeodorum neocaledonicum

Germainia grandifloraGermainia IruncatiglumisGlochidion perakenseGlochidion spGlochidion xerocarpumGinelina schlechteri

Gomphrena canescensGomphrena spGomphrena spGonocarpus IeptothecusGoodenia bicolor

Goodenia hePPIeanaGoodenia holtziana

Goodenia lamprospermaGoodenia spGoodenia spGossypium australeGrevillea agrifoliaGrevillea angulataGrevillea decurrens

Grevillea dimidiata

Grevillea dryandriGrevillea erythrocladaGrevillea he IiospermaGrevillea my OSodes(3KC-)Grevillea pteridifoliaGrevillea pyrimidalisGrevillea refracta

Grevillea striata

Grewia retusifolia

Gymnanthera sp

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CyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeRubiaceae

Rubiaceae

Orchidaceae

Poaceae

Poaceae

EuphorbiaceaeEuphorbiaceaeEuphorbiaceaeVerbenaceae

Amaranthaceae

Amaranthaceae

Amaranthaceae

HaloragaceaeGoodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Malvaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Tiliaceae

Bradshaw Station - Veg 97

L

Gyrocarpus americanusHaemodorum coccineum

Hakea arborescens

Hakea suberea

Halosarcia halocnemoides

Hellcteres sp. 32He Iiotropium spHellotropium spHellotropium tenuifoliumHeteropogan contortusHeteropogon triticeusHibbertia spHibiscus panduriformisHibiscus spHybanthus enneaspermusHygrophila an gustifoliaHypoestes floribundaHyptis suaveo1ens'Indigoiera GoluteaIndigofera jinifoliaIndigofera 11nnaeiIndigofera saxicolaIPOmoea copticaIPOmoea costataIPOmoea spIPOmoea spIschaemum australe

Iseilema vaginiflorumJacksonia dilatata

Jacksonia forrestii

Jasmimum didyinumJasminum moile

Leea Indica

Leptochloa neesiiLeuchenaultia fillformis

Limnophila fragransLindernia clausa

Lindsaea ensiiolia

LIPocarpa microcephalaLitsea glutinosaLoinandra tropicaLophostemon grandiflorusLudwigia octovalvisLudwigia perennisLuffa graveo1ensLysiana subflacataLysiphyllum cunning hammiiMacaranga involucrataMalvastrum americanum

Marsilea drummondii

May tenus cunning hamiiMe Ialeuca argenteaMeIaleuca citrolens

Me Iaieuca Ieucadendra

Me Ialeuca minutifolia

MeIaleuca nervosa

Me Iaieuca sericea

MeIaleuca spMe Ialeuca sp

I^

.

AsclepiadaceaeHemandiaceae

Haemodoraceae

Proteaceae

Proteaceae

Sterculiaceae

80raginaceaeBoraginaceae80raginaceaePoaceae

Poaceae

Dilleniaceae

Malvaceae

Maivaceae

Violaceae

ACanthaceae

ACanthaceae

Lamiaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Convolvulaceae

Convolvulaceae

Convolvulaceae

Convolvulaceae

Poaceae

Poaceae

Fabaceae

Fabaceae

Oleaceae

Oleaceae

Leeaceae

Poaceae

Goodeniaceae

Lauraceae

ScrophulariaceaeScrophulariaceaeLindsaeceae

CyperaceaeXanthorrhoeaceae

MynaceaeOn agraceaeOn agraceaeCucurbitaceae

Loranthaceae

CaesalpiniaceaeEuphorbiaceaeMalvaceae

Marsiliaceae

Celastraceae

MynaceaeMyrtaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMyrtaceae

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Me Ialeuca viridiflora

Melastoma spMe Ihania incana

Melia azedarach

Me 11cope elleryanaMerremia spMistletoe

Mistletoe

Mistletoe (on EUCa Iati)Mitrasacme connata

Mitrasacme spMnesithea rotlboelioides

Mucuna giganteaNauclea orientalis

Nelsonia campestrisNeptunia dimorphanthaNeptunia gracilisNYmpaea violaceaOldenlandia initrasacmoides

Operculine aequisepalaOphiuros axaltatusOryza australiensisOwenia vernicosa

Pachynema sphenandrumPandanus aquaticusPandanus spiralisPanicum decompositumPanicum mindanaense

Panicum seminudum

Panicum spPanicum trachyrhachisParkinsonia aculeata'

Paspalum SCObiculatumPassiflora foetida*

Pennisetum pedicellatum*Persoonia talcata

Petal OSIigma banksiiPetal OStigma pubescensPetalOStigma quadrilocularePhragmites karkaPhyllanthus grandisepalusPhyllanthus maderaspatensisPhyllanthus spPhyllanthus spPhyllanthus spPhyllanthus spPityrodia jamesiiPlanchonia careyaPIectrachne bynoeiPiectrachne pungensPoaceae

Poaceae spPoaceae spPoaceae spPoaceae sp.Poaceae spPoaceae spPoaceae spPoaceae spPoaceae spPoaceae spPoaceae sp

MynaceaeMelastomataceae

Sterculiaceae

Meliaceae

Rutaceae

Convolvulaceae

Loranthaceae

Loranthaceae

Loranthaceae

Loranthaceae

LoganiaceaePoaceae

Fabaceae

Rubiaceae

ACanthaceae

Mimosaceae

Mimosaceae

NymphaeaceaeRubiaceae

Convolvulaceae

Poaceae

Poaceae

Meliaceae

Poaceae

Pandanaceae

Pandanaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

CaesalpiniaceaePoaceae

Passifloraceae

Poaceae

Proteaceae

EuphorbiaceaeEuphorbiaceaeEuphorbiaceaePoaceae

EuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeVerbenaceae

LecythidaceaePoaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Bradshaw Station - Veg 97

Polycarpaea brevifloraPolycarpaea corymbosaPolycarpaea corymbosaPolycarpaea in VCIucrataPolycarpaea longiiloraPolycarpaea spPolycarpaea spPolycarpaea spPolygala eriocephalaPolygala 11narifoliaPolygala longifoliaPolymerIa ambiguaPouteria sericea

Premna acuminata

Pseudopoganotherum contortumPseudoraphis spinescensPterocaulon serrulatum

Ptilotus conicus

PIilotus spicatusRhynchosia minimaRhynchospora browniiRhynchospora exsertaRhynchospora spSalsola kali

Sauropis spSauropis spSauropis spScaevola revoluta

Schizachrium fragileSchizachyrium spSchoenoplectus praelongatusScleria pygmaeaScleria spScleria spScleria sphacelataSebastiana chainaelea

Sedge spSedge spSedge spSedge spSedge spSedge spSedge spSedge spSedge spSedge spSehima nervosum

Senna occidentalis*

TerminalIa volucris

Thecanthes puniceaThecanthes sanguineaThemeda triandra

Thysanotus chinensisTimonius timon

Trianthema rhynchocalypteraTrichodesma zeylanicumTriumfetta spUraria 015707 Litchfield (3KC)

Uraria lagopodioidesVentilago viminalisVer!ICOrdia verticillata

Vetiveria pauciflora

CaryophyllaceaeCaryophyllaceaeCaryophyllaceaeCaryophyllaceaeCaryophyllaceaeCaryophyllaceaeCaryophyllaceaeCaryophyllaceaePolygalaceaePolygalaceaePolygalaceaeConvolvulaceae

SapotaceaeVerbenaceae

Poaceae

Poaceae

Asteraceae

Amaranthaceae

Amaranthaceae

Fabaceae

CyperaceaeCyperaceaeCyperaceaeChenopodiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaePoaceae

Poaceae

Poaceae

CyperaceaeCyperaceaeCyperaceaeCyperaceaeEuphorbiaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaePoaceae

CaesalpiniaceaeCombretaceae

ThymelaeaceaeThymelaeaceaePoaceae

Liliaceae

Rubiaceae

A1zoaceae

BoraginaceaeTiliaceae

Fabaceae

Fabaceae

Rhamnaceae

MynaceaeFabaceae

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Vigna lanceolataVigna vexillataVilex glabrataWaitheria indica

Whiteochloa capillipesWrightia salignaXanthium strumarium*

Xanthostemon paradoxusXerchloa jinberbis

Xerochloa Ianiflora

Xyris coinplanataXyris IndicaYakirra majuscalaZanthoxylum parviflorumZornia areolata

Zornia prostrata

I

.

II

Fabaceae

Fabaceae

Verbenaceae

Sterculiaceae

Poaceae

ApocynaceaeAsteraceae

MynaceaePoaceae

Poaceae

XyridaceaeXyridaceaePoaceae

Rutaceae

Fabaceae

Fabaceae

Bradshaw Station - Veg 97

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L

Appendix 2

Species and the joeations from which theywere recorded. Most records are from June

1997.

,

I

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COMMERCIAL-IN-CONFIDENCE

Prepared for: Connell WagnerPrepared by: ERA Environmental Services Pty Ltd

SepU97Job NO XI32

Page 62: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

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Page 63: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Species recorded on Bradshaw Station during surveys in June 1997 and the locationswhere each was recorded. * indicates an introduced species.Conservation status code of species of conservation significance follows the speciesname.

'5,616ib:S' ~~' ~ ~~;Family isiteAbelmoschus ficulneus

Acacia auricu!iformisAcacia coriacea

Acacia difficilisAcacia difficilis

Acacia difficilis

Acacia difficilis

Acacia difficilis

Acacia dimcilis

Acacia difficilis

Acacia difficilis

Acacia difficilis

Acacia difficilis

Acacia difficilis

Acacia difficilis

Acacia difficilis

Acacia difficilis

Acacia difficilis

Acacia dimidiata

Acacia dimidiata

Acacia dimidiataAcacia dunnii

Acacia dunnii

Acacia froggattiiAcacia hammondii

Acacia hammondiiAcacia hammondii

Acacia hemignostaAcacia hemignostaAcacia hemignostaAcacia hemignostaAcacia hemignostaAcacia hemignostaAcacia hemignostaAcacia holoserciaAcacia holosericea

Acacia holosericea

Acacia holosericea

Acacia holosericea

.

Maivaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

L

,

34

142174

4

152

127

107

89

89

73

72

71

21

18

22

69

23

62

4

69

86165

3

I03

3

4197

187

132203

II 3

11 9

83

I 91

152

152

153

137

Easting643720

640000649386

6530005206/8

619700

711530602410

602410

616030

601780

601640

664942

686580

659430

586980

659630

621550

653000

586980

609860655810

654820

706680

654820

653000655780

674960

646620667550

614620

617830

620290

656900672500

5206/8

5206/8

.

Northing I8297970

83535908282648

82806108304631

8345300

83397908354680

8354680

8312470

8321/20

8320980

8296605

8305400

8290940

8342020

8290940

8312/30

8280610

8342020

83397008274414

8340/20

8322000

8340/20

82806iO8292760

8324550

83053208316970

8316/40

8323200

8324640

82727508306500

8304631

830463i

.

.

659640 8337280

Page 64: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Acacia holosericea

Acacia holosericeaAcacia holosericea

Acacia holosericeaAcacia holosericea

Acacia holosericea

Acacia holosericea

Acacia holosericea

Acacia holosericea

Acacia holosericea

Acacia holosericea

Acacia holosericea

Acacia holosericea

Acacia holosericea

Acacia holosericea

Acacia kelleri(3R?)Acacia IysiphloiaAcacia IysophloiaAcacia neurocarpaAcacia neurocarpaAcacia nuperimmaAcacia nuperrimaAcacia nuperrimaAcacia nuperrimaAcacia nuperrimaAcacia nuperrimaAcacia nuperrimaAcacia nuperrimaAcacia nuperrimaAcacia nuperrimaAcacia nuperrimaAcacia nuperrimaAcacia nuperrimaAcacia nuperrimaAcacia pachyphloiaAcacia pachyphloiaAcacia pachyphloiaAcacia pachyphloiaAcacia pachyphloiaAcacia pachyphloiaAcacia pachyphloiaAcacia pellitaAcacia platycarpaAcacia platycarpaAcacia platycarpa

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

158

168

169

150156

99

95

94

55

54

52

24

16

15

13

70165

164

103

105

79

11 7

184

157

136

I 31190

11 5

107

78

73

70

4

90

43

45

44

25

29

28

27

87200

154

92

662193

647526

647853

648656681950

68/060

677490

605680

654380

655510

655700

655500

676700

674120

661390

588330655810

653358

706680

707640

641370

615050654270

672900

659320

622840693500

615230

711530

641750

616030

588330

653000

605890

692090

689540

69/020

653050

656320

656290

656430

609560651400

618432

610550

8303/74

8277378

8277781

83006328305600

8305350

8299950

8326260

8299590

8298810

8300850

8301400

8303900

8304550

8302470

8339/208274414

8272845

8322000

8332860

8317080

83218iO8325580

8304000

8336970

83242908304000

8322020

8339790

831703

8312470

8339/20

82806t O

8354080

8347970

8345950

8347480

8302440

830747C

8306860

8306710

83397008282/60

8304390

8335330

I

:

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Page 65: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

Species 1997

.

Acacia sp.Acacia sp.Acacia spAcacia sp.Acacia sp. 160Acacia sp. 162Acacia sp. 163Acacia sp. 163Acacia sp. I 63Acacia sp. 166Acacia translucens

Acacia turnida

Acacia turnidaAcacia turnida

Acacia turnida

Acacia umbellata

Acacia umbellata

Acacia umbellata

Acacia umbellata

Acacia valida

Acacia valida

Acacia valida

Acacia valida

Acacia valida

Acacia valida

Acacia valida

Acacia valida

Acacia valida

Acacia valida

AChyranthes asperaAdansonia gregoriiAdansonia gregoriiAdansonia gregoriiAdansonia gregoriiAdansonia gregoriiAdansonia gregoriiAdansonia gregoriiAdansonia gregoriiAdansonia gregoriiAdansonia gregoriiAdenostemma laveria

Adjantum hispidulum (3rC)Adjantum hispidulum (3rC)Adonsonia gregorii

I

.

I

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Amaranthaceae

Bombacaceae

Bombacaceae

Bombacaceae

Bombacaceae

Bombacaceae

Bombacaceae

Bombacaceae

Bombacaceae

Bombacaceae

Bombacaceae

Asteraceae

Adjantaceae

Adjantaceae

Bombacaceae

I

83

84

I 31162

160

162

I65

164

163

166

67

100

103189

71

I 01

90

90

70

39

151

108

46

40

34

7

25

25

26

2

87I 91

11 8

97

28

52

32

29

16

66

32

126154

r

:

620290

620000

622840651520

675660

65/520

655810

653358

652393

65484t

621740

703040

706680686700

601640

703010

605890

605890

588330

683300

688590

700940

684750

684490

643720

652420

653050

653050

655770

656440

609560672500

615460

8324640

8324300

8324290828082

8303520

8282082

8274414

8272845

8280/50

8278410

83/1040

8318590

83220008304600

8320980

8318/80

8354080

8354080

8339/20

8338940

8346450

8346780

8341670

8341220

8297970

8288310

8302440

8302440

8305/40

8272820

83397008306500

8321630

^

656290

655700

635340

656320

676700

656900

621460

635340

620120618432

8306860

8300850

8301290

8307470

8303900

8272750

83/0830

8301290

83450608304390

Page 66: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Aeschynomene indicaA1phitonia excelsaA1phitonia excelsaA1phitonia excelsaAIStonia actinophyllaAIStonia actinophyllaAlter nanthera nodiflora

Alter nanthera pungens*Alternanthera pungens*Am inarinia bacciferaAm inarinia baccifera

Am inarinia bacciferaAm inarinia bacciferaAm inarinia baccifera

Am inarinia multifloraAmpellocissus acetosaAmpellocissus acetosaAmpellocissus acetosaAmpellocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosa

Fabaceae

Rhamnaceae

Rhamnaceae

Rhamnaceae

ApocynaceaeApocynaceaeAmaranthaceae

Amaranthaceae

Amaranthaceae

LythraceaeLythraceaeLythraceaeLyihraceaeLythraceaeLythraceaeVitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

37

69

89

130

142

126

35

2

32

43

I47

40

39

34

35203

187

I 91

184

99

95

I 01

78

88

83

81

105

103

129

109

I I 3

I I 4

I I 8

11 9

I 21

133

I 51

79

30

74

41

4

71

22

665760

586980

602410

619350

640000

620120

645880

656440

635340

692090

683990

684490

683300

643720

645880667550

674960

672500

654270

68/060

677490

703010

641750

602280

620290

635790707640

706680

619350

7011 80

614620

614340

615460

617830

612880

646100

688590

641370

654370

616210

685920

653000

601640

659430

8308880

8342020

8354680

8352260

8353590

8345060

8294600

8272820

8301290

8347970

8338/30

8341220

8338940

8297970

82946008316970

8324550

8306500

8325580

8305350

8299950

8318/80

831703

8354670

8324640

83172108332860

8322000

8352410

8347/60

831 6140

8316100

8321630

8323200

8327760

8305820

8346450

8317080

8307/80

8312690

8343550

8280610

8320980

8290940

I

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.

,

Species 1997

Ampelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmpelocissus acetosaAmyema benthamiiAmyema benthamiiAmyema sanguineumAn isomeles malabarica

An ISOmeles malabarica

An isomeles malabarica

Antidesma ghaesembillaAntidesma ghaesembillaAntidesma ghesaembillaAntidesma ghesaembillaAntidesma ghesaembillaAntidesma ghesaembillaAristida Iatifolia

Aristida Iatifolia

Aristida dominii

Aristida dominiiAristida holathera

Aristida holathera

Aristida holathera

Aristida holathera

Aristida hygrometricaAristida hygrometricaAristida hygrometricaAristida hygrometricaAristida hygrometricaAristida hygrometricaAristida hygrometricaAristida hygrometricaAristida hygrometricaAristida hygrometricaAristida hygrometrica

.

I

^

.

:

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Loranthaceae

Loranthaceae

Loranthaceae

Lamiaceae

Lamiaceae

Lamiaceae

EuphorbiaceaeEuphorbiaceaePoaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

e

.

26

31

33

40

17

43

45

61

65

55

53

51

47

46

11

13

16

143

127

140157

158

130

11 8

11 3

95

12

92

27

53178

78

135

54

33168

60170

169

174

165

162

136

81

72

.

655770

643480

641750

684490

680250

692090

689540

621440

623060

654380

654970

677600

681500

684750

654620

661390

676700

664170

619700

647400672900

662193

619350

615460

614620

677490

655230

610550

656430

65497065/650

641750

646280

655510

641750647526

641220649567

647853

649386

655810

65/520

659320

635790

601780

.

8305/40

8305350

8302740

8341220

8305/20

8347970

8345950

8312480

8315830

8299590

8299950

8326750

8335290

8341670

8297060

8302470

8303900

8349880

8345300

83429708304000

8303/74

8352260

8321630

8316/40

8299950

8300250

8335330

8306710

82999508285057

831703

8328010

8298810

83027408277378

83047708280819

8277781

8282648

8274414

8282082

8336970

8317210

8321/20

,

I

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Page 68: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Aristida in aequiglumis Poaceae

PoaceaeAristida InaequiglumisAristida Ierichoenis subspinulifera Poaceae

PoaceaeAristida Iatifolia

PoaceaeATistida Iatitolia

PoaceaeAristida Iatifolia

PoaceaeAristida Iatifolia

PoaceaeAristida Iatifolia

PoaceaeAristida Iatifolia

PoaceaeAristida IatifoliaPoaceaeAristida Iatifolia

PoaceaeAristida IatifoliaPoaceaeAristida Iatifolia

PoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeAristida Iatifolia

Aristida Iatifolia Poaceae

PoaceaeAristida Iatifolia

PoaceaeAristida Iatifolia

PoaceaeAristida Iatifolia

PoaceaeAristida tatifoliaPoaceaeAristida Iatifolia

PoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeATistida Iatifolia

PoaceaeAristida Iatifolia

PoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeAristida IatifoliaPoaceaeAristida IatifoiiaPoaceaeAristida mediumPoaceaeAristida spPoaceaeAristida sp.PoaceaeAristida sp.

169

174

160

62

I I 9

63

74

75

100

I I 6180

125

129

I 31

147

172

177

179

60

61

I 51

59

53

23

8

11

19

21

22

14

25

27

43

31

44

46

40

39

33

134

123154

143

647853

649386

675660

621550

617830

622230

616210

645530

703040

615200652721

614350

619350

622840

683990649173

647339

652310

641220

621440

688590

647400

654970

659630

652890

654620

683550

656900

664942

659430

668040

653050

656430

692090

643480

69/020

684750

684490

683300

641750

646080

6/2/30618432

664170

8277781

8282648

8303520

8312/30

8323200

8315860

8312690

8303930

8318590

83216508290760

8332060

8352410

8324290

8338/308284998

8289727

8288341

8304770

8312480

8346450

8302530

8299950

8290940

8291390

8297060

8305700

8272750

8296605

8290940

8303400

8302440

8306710

8347970

8305350

8347480

8341670

8341220

8338940

8302740

8328010

83313iO8304390

8349880

o

I.

. I, ,F ,

\

^

Page 69: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

Species 1997

Aristida sp.Aristida sp.Aristida spAristida spAristidia Iatifolia

Aristidia Iatifo!ia

Arundinella nepalensisArundinella nepalensisArundinella nepalensisArundinella nepalensisArundinella nepalensisArundinella nepalensisArundinella nepalensisArundinella nepalensisAtalaya hemiglaucaAt alaya hemiglaucaAtalaya hemiglaucaAtalaya hemiglaucaAtalaya hemiglaucaAt alaya hemiglaucaAtalaya hemiglaucaAtalaya hemiglaucaAt alaya hemiglaucaAtalaya hemiglaucaAtalaya hemiglaucaAtalaya hemiglaucaAtalaya hemiglaucaAtalaya hemiglaucaAtalaya hemiglaucaAtaiaya hemig!aucaAt alaya variifoliaBacopa floribundaBacopa floribundaBacopa floribundaBacopa floribundaBacopa floribundaBacopa floribundaBacopa floribundaBacopa floribundaBacopa floribundaBacopa floribundaBacopa floribundaBacopa floribundaBacopa floribundaBacopa floribunda

a

.

.

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

SapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeLecythidaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceae

I

4

129

I I O

4

34

105156

152

144

130

138

137

37

84175

59I 91

179

54

I 91

58168

53

34

25

16

13

12

11

7

207

153

133

11 8

I I 5

I I I

77

103

I 01

95

109

76

24

74

20

653000

619350

695190

653000

643720

707640

681950

5206/8

667400

619350

658680

659640

665760

620000648206

647400672500

652310

655510672500

647500647526

654970

643720

653050

676700

661390

655230

654620

652420687740

8280610

8352410

8346850

8280610

8297970

8332860

8305600

8304631

8347820

8352260

8334790

8337280

8308880

83243008283574

83025308306500

8288341

82988108306500

82953308277378

8299950

8297970

8302440

8303900

8302470

8300250

8297060

82883108316030

^

646100

615460

615230

683000

645780

706680

703010

677490

7011 80

645940

655500

616210

671200

8305820

8321630

8322020

8347100

8303800

8322000

8318/80

8299950

8347/60

8303850

8301400

8312690

8304/40

Page 70: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Bacopa floribundaBacopa floribundaBacopa floribundaBacopa floribundaBacopa floribundaBacopa floribundaBarringtoriia acutangulaBarringtoriia acutangulaBarringtoriia acutangulaBarringtoriia acutangulaBarringtoriia acutangulaBarringtoriia acutangulaBarringtoriia acutangulaBidens pilosa*Blechnum orientale

Blechnum sp.Blumea diffusa

Blumea diffusa

Blumea diffusa

Blumea diffusa

Blumea diffusa

Blumea diffusa

Blumea diffusa

Blumea diffusa

Blumea diffusa

Blumea diffusa

Blumea diffusa

Blumea diffusa

Blumea diffusa

Blumea diffusa

Blumea tenella

Blumea tenelia

Blumea tenella

Bonamia pannosaBorreria exserta

Borreria exserta

Borreria sp.BOSiaea sp.Boss boss

Bothriochloa ewartiana

Bothriochloa pertusaBrachyachne convergensBrachyachne convergensBrachyachne convergens

ScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeAsteraceae

Blechnaceae

Blechnaceae

Asteraceae

Fabaceae

Asteraceae

Asteraceae

Asteraceae

Asteraceae

Asteraceae

Asteraceae

Asteraceae

Asteraceae

Asteraceae

Asteraceae

Asteraceae

Asteraceae

Asteraceae

Asteraceae

Asteraceae

Convolvulaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

21

25

34

47

51

55

153

160

158

94

130

16

84

34

66

126

76

136

11 8

109

89

79

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4

59

57

22

21

61

34

22

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128192

200

I 61

78

78

37

94

53

57

58

664942

653050

643720

681500

677600

654380

8296605

8302440

8297970

8335290

8326750

8299590

675660

662193

605680

619350

676700

620000

643720

621460

620120

645940

659320

615460

701180602410

641370

635790

616030

653000

647400

648550

659430

664942

621440

643720

659430

655500

625720649590

651400

683190

641750

641750

665760

605680

654970

648550

647500

8303520

8303/74

8326260

8352260

8303900

8324300

8297970

83/0830

8345060

8303850

8336970

8321 630

8347/608354680

8317080

8317210

8312470

8280610

8302530

8295260

8290940

8296605

8312480

8297970

8290940

8301400

83600408312060

8282/60

8305770

831703

831703

8308880

8326260

8299950

8295260

8295330

I

.

^

I

I

,

^

.

Page 71: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

.

:

Brachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachyachne convergensBrachychiton diversifoiiaBrachychiton diversifo!iaBrachychiton diversifoliaBrachychiton diversifoliaBrachychiton diversifoliaBrachychiton diversifoliusBrachychiton diversifoliusBrachychiton diversifoliusBrachychiton diversifoliusBrachychiton diversifoliusBrachychiton diversifoliusBrachychiton diversifoliusBrachychiton sp.Brachychiton viscidulusBrachychiton viscidulusBrachychiton viscidulusBrachychiton viscidulus

I

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

,

.

I

75

11 O

I I 6

147

I37182

172

175

177

179

180

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46

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7

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656900

652420

654620

668040

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656430

658060

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692090

69/020

641750

635340

6/2/30

625720

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602280

656320

68/060653358

675660

602410

677490

659430

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8346850

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83372808299846

8284998

8283574

8289727

8288341

8290760

8299590

8306860

8341670

8302440

8272750

8288310

8297060

8303400

8305700

8300250

83067iO

8305720

8307/80

8347970

8347480

8302740

8301290

83313t O

8360040

8321630

8354670

8307470

83053508272845

8303520

8354680

8299950

8290940

8305/40

I

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6/2/30

615460

622840

620120

8331310

8321630

8324290

8345060

Page 72: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Brachychiton viscidulusBrachychiton viscidulusBrachychiton viscidulusBrachychiton viscidulusBrachychiton viscidulusBrachychiton viscidulusBrachychiton viscidulusBrachychiton viscidulusBrachychiton viscidulusBrachychiton viscidulusBrachychiton viscidulusBrachychiton viscidulusBrachychiton visciduiusBreynia cernuaBreynia cernuaBreynia cernuaBridelia tomentosa

Bridelia tometosa

Brunoniella australisBuchanania obovata

Buchanania obovataBuchanania obovata

BUGhanania obovata

Buchanania obovata

Buchanania obovataBuchanania obovata

Buchanania obovataBuchanania obovata

Buchanania obovata

Buchanania obovata

BUGhanania obovata

Buchanania obovata

Buchanania obovata

Buchanania obovata

Buchanania obovata

Buchanania obovata

Buchanania obovata

Buchnera linearis

BUGhnera linearis

Buchnera linearis

Buchnera linearis

BUGhnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

EuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeAnacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

Anacardiaceae

ScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceae

128

81

136

I 01

66

74

67

65

63

61

51

45

15

153

128

126

88

142

95152

148152

162

154

134189

143163

127

86

70

69

92

124

94

95

95

120

11 9

108

I I 7

11 3

11 O

124

136

625720

635790

659320

703010

621460

616210

621740

623060

622230

621440

677600

689540

674120

8360040

8317210

8336970

8318/80

83/0830

8312690

83/1040

8315830

8315860

8312480

8326750

8345950

8304550

625720

620120

602280

640000

6774905206/8

6702605206/8

65/520

618432

646080686700

664170652393

619700

609860

588330

586980

610550

6/4/50

605680

677490

677490

8360040

8345060

8354670

8353590

82999508304631

83235308304631

8282082

8304390

83280108304600

83498808280/50

8345300

8339700

8339/20

8342020

8335330

8332000

8326260

8299950

8299950

I

r

617830

700940

615050

614620

695190

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8323200

8346780

8321810

8316/40

8346850

8332000

8336970

,

,

.

Page 73: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

.

Species 1997

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

Buchnera linearis

BUGhnera linearis

Buchnera linearis

Buchnera linearis

Buchnera rainosissma

Bulbostylis barbataBulbostylis bulbiferaGalandrinia uniflorum

Galandrinia uniflorum

Galandrinia uniflorum

Callitris intratropicaCallitris intratropicaCalotropis procera*Calytrix achaetaCalylrix achaetaCalytrix achaetaCalylrix achaetaCalylrix brownii

I

ScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophuiariaceaeScrophuiariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeScrophulariaceaeCyperaceaeCyperaceaePortulacaceae

Portulacaceae

Portulacaceae

CupressaceaeCupressaceaeAsclepiadaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceae

I

.

125

I29

133

I34

140

145

147

102

105

128

100

99

43

45

44

20

22

61

17

97

50

127

96

72

73

78

86

89

92

65

88154

I 61

19

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103184

142

124

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104

123

18

.

.

614350

619350

6461 00

646080

647400

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683990

706390707640

625720

703040

68/060

692090

689540

69/020

671200

659430

621440

680250

I

8332060

8352410

8305820

8328010

8342970

8348200

8338/30

83217208332860

8360040

8318590

8305350

8347970

8345950

8347480

8304/40

8290940

8312480

8305/20

680380

619700

677020

60/780

616030

641750

609860602410

610550

623060

602280618432

683190

683550

664942

69/020

706680654270

640000

6/4/50

622840

707400

6/2/30

686580

8332950

8345300

8299900

8321/20

8312470

831703

83397008354680

8335330

8315830

83546708304390

8305770

8305700

8296605

8347480

83220008325580

8353590

8332000

8324290

8333000

8331310

8305400

Page 74: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Calytrix browniiCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCaly!rix exstipulataCalylrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalytrix exstipulataCalylrix exstipulataCalytrix exstipulataCalylrix exstipulataCalytrix exstipulataCalytrix exstipulataCan arium australianum

Can arium australianumCan arium australianum

Capparis IasianthaCapparis IasianthaCapparis IasianthaCapparis IasianthaCapparis IasianthaCapparis umbonataCapparis umbonataCapparis umbonataCapparis umbonataCarallia brachiata

Carallia brachiata

Carallia brachiata

Carallia brachiata

Carallia brachiata

Carissa lanceolata

MynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeBurseraceae

Burseraceae

Burseraceae

CapparaceaeCapparaceaeCapparaceaeCapparaceaeCapparaceaeCapparaceaeCapparaceaeCapparaceaeCapparaceaeRhizophoraceaeRhizophoraceaeRhizophoraceaeRhizophoraceaeRhizophoraceaeApocynaceae

4163

154

157

157

I 61

165

I64

164

166

124167

183

I 31

19

107

50

3

3

20

22

70

67

105

90

I 01

102

104152

87152

31

I I O

14

7

71

11 4

129175

126

142

87

87

66

132

653000652393

618432

672900

672900

683190

655810

653358

653358

654841

6/4/50653778

82806108280/50

8304390

8304000

8304000

8305770

8274414

8272845

8272845

8278410

83320008278890

.

.

622840

683550

711530

680380

654820

654820

67/200

659430

588330

621740707640

605890

703010

706390

7074005206/8

6095605206/8

643480

695190

668040

652420

656900

601640

614340

619350648206

620120

640000

609560

609560

621460

646620

8324290

8305700

8339790

8332950

8340/20

8340/20

8304/40

8290940

8339/20

83/10408332860

8354080

8318/80

8321720

83330008304631

83397008304631

8305350

8346850

8303400

8288310

8272750

8320980

8316100

83524108283574

8345060

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8339700

8339700

83/0830

8305320

,

.

.

I

.

Page 75: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

,

Species 1997

,

;

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceoiataCarissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolataCarissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolataCarissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

Carissa lanceolata

I

I

I

I

ApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceae

,

.

123

I 21

109

11 4

108

I 01

99168

193

173

175

96207

199

194

191

176

I88

187

179

97172

76

75

8

16

12

11

7

25

6

59

24

13

28

30

53

58

32

54

55

46

44

36

38

61 2130

612880

701180

614340

700940

703010

68/060647526

651620

649752

648206

677020687740

648640

654900

672500

648494

673870

674960

652310

.

8331310

8327760

8347t 60

8316100

8346780

8318/80

83053508277378

8303400

8284308

8283574

82999008316030

8286440

8299000

8306500

8285417

8322360

8324550

8288341

649173

645940

645530

652890

676700

655230

654620

652420

653050

649830

656900

647400

655500

66/390

656290

654370

654970

647500

635340

655510

654380

684750

69/020

658060

682560

8284998

8303850

8303930

8291390

8303900

8300250

8297060

8288310

8302440

8284430

8272750

8302530

8301400

8302470

8306860

8307/80

8299950

829533C

8301290

8298810

8299590

8341670

8347480

8305720

8337630

Page 76: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Carpentaria acuminataCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCartonema trigonospermumCaryratia maritimaGassytha aureaGassytha aureaGassytha sp.Gassytha sp.Gassytha sp.Oathormion umbellatum

Cathormion umbellatum

Cathormion umbellatum

Cathormion umbellatumOathormium umbellatum

Cathormium umbellatum

Cathormium umbellatum

Cathormium umbellatum

Gayratia maritimaGayratia maritimaGayratia maritimaGayratia trifoliaGenchrus ciliarjs*

Genchrus ciliarjs*

Genchrus ciliarjs*

Centrolepis exsertaCheilanthes tenuifolia

Chionachne cyanthopoda

Arecaceae

Coinmelinaceae

Coinmelinaceae

Coinmelinaceae

Coinmelinaceae

Coinmelinaceae

Coinmelinaceae

Coinmelinaceae

Coinmelinaceae

Coinmelinaceae

Coinmelinaceae

Coinmelinaceae

Coinme!in aceae

Coinmeiinaceae

Coinmelinaceae

Coinmelinaceae

Coinmelinaceae

Coinmelinaceae

Coinmelinaceae

Coinmelinaceae

Vitaceae

Lauraceae

Lauraceae

Lauraceae

Lauraceae

Lauraceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Vitaceae

Vitaceae

Vitaceae

Vitaceae

Poaceae

Poaceae

Poaceae

CentrolepidaceaeSinopteridaceaePoaceae

126

129

I I I

124

136

I 31

140

149

80

86

73

79

78

21

22

61

63

71

72

74

2

7

25

120

99

70

12

16

52

57

205

158

202

158

2

139

32

144155

32

107

73

106

34

620120

619350

683000

6/4/50

659320

622840

647400

670230

640590

609860

616030

641370

641750

664942

659430

621440

622230

601640

601780

616210

656440

652420

653050

8345060

8352410

8347100

8332000

8336970

8324290

8342970

8332420

8314600

8339700

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Page 77: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

; Species 1997

Chionachne spChioris lobata

Chrysopogan fallaxChrysopogan fallaxChrysopogan fallaxChrysopogan fallaxChrysopogan fallaxChrysopogan fallaxChrysopogan fallaxChrysopogan fallaxChrysopogan fallaxChrysopogan fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon iaiiaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallaxChrysopogon fallax

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

I-Oaeeae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

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Poaceae

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Poaceae

Poaceae

Poaceae

Poaceae

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Poaceae

Poaceae

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Poaceae

Poaceae

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Poaceae

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Poaceae

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197

207

202

199

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Page 78: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

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Page 79: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

*

Species 1997

Clerodendrum floribundum

Clerodendrum talei

C!erodendrum talei

Cochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCOGhlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCochlospermum fraseriCOGhlospermum fraseriCochlospermum fraseriCochlospermum fraseriCOGhlospermum fraseriCochlospermum fraseriCochlospermum fraseriGoleus scutellarioides

Coinmelina sidiodes

Convolvulaceae

Convolvulaceae

,

,

Verbenaceae

Verbenaceae

Verbenaceae

Bixaceae

Bixaceae

Bixaceae

Bixaceae

Bixaceae

Bixaceae

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Bixaceae

Bixaceae

Bixaceae

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Bixaceae

Lamiaceae

Coinmelinaceae

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Convolvulaceae

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Page 80: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Convolvu!aceae sp.Gorymbia bleeseriGorymbia bleeseriGorymbia bleeseriGorymbia bleeseriGorymbia bleeseriGorymbia bleeseriGorymbia bleeseriGorymbia bleeseriGorymbia bleeseriGorymbia bleeseriGorymbia bleeseriGorymbia contentfloraGorymbia confertitloraGorymbia confertifloraGorymbia conferIifloraGorymbia confertifloraGorymbia confer11floraGorymbia conferIifloraGorymbia contentfloraGorymbia confer11floraGorymbia conferIifloraGorymbia conferIifloraGorymbia conferIifloraGorymbia confer11floraGorymbia confer11floraGorymbia conferIifloraGorymbia confer11floraGorymbia dichromophloiaGorymbia dichromophloiaGorymbia dichromophloiaGorymbia dichromophloiaGorymbia dichromophloiaGorymbia dichromophloiaGorymbia dichromophloiaGorymbia dichromophloiaGorymbia dichromophloiaGorymbia dichromophloiaGorymbia dichromophloiaGorymbia dichromophloiaGorymbia dichromophloiaGorymbia ferrugineaGorymbia ferrugineaGorymbia ferrugineaGorymbia ferruginea

Convolvuiaceae

MynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceae

20

134

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143

80

135

135

107

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92

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189

184

183

167

185

164

163

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664170

640590

646280

646280

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610550

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692090

677490

677490

680250

692090

680250

655770

656320

684490655810

686700

654270

8304/40

8328010

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8349880

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.

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Page 81: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

I

Species 1997

Gorymbia ferrugineaGorymbia ferrugineaGorymbia ferrugineaGorymbia ferrugineaGorymbia ferrugineaGorymbia foelscheanaGorymbia foelscheanaGorymbia foelscheanaGorymbia foelscheanaGorymbia foelscheanaGorymbia foelscheanaGorymbia foelsheanaGorymbia grandifloraGorymbia grandifloraGorymbia grandifloraGorymbia grandifloraGorymbia grandifloraGorymbia grandifloraGorymbia grandifloraGorymbia grandifloraGorymbia grandifloraGorymbia grandifloraGorymbia grandifloraGorymbia grandifloraCorymbia grandifloraGorymbia grandifloraGorymbia grandifloraGorymbia grandifloraGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IanfoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia Iatifolia

.

I

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I

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Page 82: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Corymbia IanfoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia tatifoliaCorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia IatifoliaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaCorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia polycarpaGorymbia ptychocarpaGorymbia ptychocarpaGorymbia ptychocarpaGorymbia ptychocarpa

MynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceae

I I I

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21

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37

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Page 83: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

:

Species 1997

Gorymbia ptychocarpaGorymbia ptychocarpaGorymbia terminalisGorymbia terminalisGorymbia terminalisGorymbia terminalisGorymbia terminalisCrinum sp.Crinum sp.Crinum sp.Crinum uniflorum

Crotalaria alata

Crotalaria arnhemicus

Crotalaria am hemicus

Crotalaria arnhemicus

Crotalaria arnhemicus

Crotalaria crispataCrotalaria crispataCrotalaria crispataCrotalaria crispataCrotalaria crispataCrotalaria crispataCrotalaria crispataCrotalaria medicagineaOrotalaria medicagineaCrotalaria medicagineaCrotalaria medicagineaCrotalaria medicagineaCrotalaria medicagineaCrotalaria medicagineaCrotalaria medicagineaCrotalaria medicagineaCrotalaria medicagineaCrotalaria medicagineaCrotalaria medicagineaOrotalaria medicagineaCrotalaria medicagineaCrotalaria medicagineeCrotalaria novae-hollandiae

Orotalaria novae-hollandiae

Crotalaria novae-hollandiaeCrotalaria novae-hollandiae

Crotalaria retusaCroton am hemicus

Croton arnhemicus

MynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeLiliaceae

Liliaceae

Liliaceae

Liliaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

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Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

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Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

EuphorbiaceaeEuphorbiaceae

.

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87

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8290940

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8307/80

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:

Page 84: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Oroton am hemicusCroton arnhemicus

Croton am hemicus

Croton am hemicus

Croton arnhemicus

Croton am hemicus

Gymbopogon bombycinusGymbopogon bombycinusGymbopogon bombycinusGymbopogon procerusGymbopogon procerusGymbopogon procerusGymbopogon procerusCynodon dactylonCynodon dactylonCynodon dactylonCynodon dactylonCyperaceae sp.Cyperaceae spCyperus holoschoenusCyperus holoschoenusCyperus sp 192Cyperus sp.Cyperus sp.Dicanthium sericumDichanthium fecundumDichanthium fecundumDichanthium fecundumDichanthium fecundumDichanthium fecundum

Dichanthium sp.Dicrostachys spicataDicrostachys spicataDicrostachys spicataDioscorea bulbifera

Dioscorea bulbiferaDioscorea bulbiferaDistichostemon am hemicus

Distichostemon arnhemicus

Distichostemon hispidulusDistichostemon hispidulusDistichostemon hispidulusDistichostemon hispidulusDo doriaea oxypteraDodoriaea oxyptera

EuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaePoaceae

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Poaceae

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Poaceae

Mimosaceae

Mimosaceae

Mimosaceae

Dioscoreaceae

Dioscoreaceae

Dioscoreaceae

SapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceaeSapindaceae

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*

:

^

Page 85: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

I

^ Species 1997

Dollchandrone fillformisDo Iichandrone fillformis

Do Iichandrone fillformis

Dollchandrone filiformis

Dollchandrone fillformis

Dollchandrone fillformis

Do Iichandrone filiformis

Do Iichandrone filiformis

Do Iichandrone fillformis

Do Iichandrone fillformisDo Iichandrone fillformisDollchandrone fillformisDo!ichandrone fillformisDo Iichandrone filiformisDo Iichandrone filiformisDo Iichandrone heterophyllaDo Iichandrone heterophyllaDollchandrone heterophyllaDo Iichandrone heterophyllaDo Iichandrone heterophyllaDrosera indica

Drosera lariata

Drosera petiolarisDrosera petiolarisDrosera petiolarisDrosera petiolarisDrosera petiolarisEchinochloa colonaEchinochloa colona

ECtrosia IeporinaECtrosia IeporinaECtrosia schu!tzii

ECtrosia schultziiECtrosia schultziiEhretia salignaEhretia salignaEhretia salignaEhretia salignaEhretia salignaEhretia salignaEhretia salignaEhretia salignaEhretia salignaEhretia salignaEhretia saligna

.

^

BignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeBignoniaceaeDroseraceae

Droseraceae

Droseraceae

Droseraceae

Droseraceae

Droseraceae

Droseraceae

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207

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8347820

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8318/808303/27

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8302530

8312690

8346780

8295330

8299590

8302440

Page 86: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Ehretia salignaEhretia salignaEhretia salignaEhretia salignaEhretia salignaEhretia salignaEhretia salignaEhretia salignaEleocharis spEleocharis sp.Eleocharis sp.Elytrophorus spicatusElytrophorus spicatusElytrophorus spicatusElytrophorus spicatusElytrophorus spicatusElytrophorus spicatusElylrophorus spicatusEnneapogon polyphyllusEnneapogon polyphyllusEnneapogon purpurascensEnteropogon sp.Eragrostis cumingiiEragrostis cumingiiEragrostis cumingiiEragrostis cumingiiEragrostis cumingiiEragrostis cumingiiEragrostis cumingiiEragrostis cumingiiEragrostis cumingiiEragrostis cumingiiEragrostis cumingiiEragrostis setifoliaEragrostis setifoliaEragrostis setifoliaEragrostis setifoliaEragrostis setifoliaEragrostis setifoliaEragrostis setifoliaEragrostis setifoliaEragrostis setifoliaEragrostis setifoliaEragrostis setifoliaEragrostis sp.

BoraginaceaeBoraginaceaeBoraginaceaeBoraginaceaeBoraginaceaeBoraginaceaeBoraginaceaeBoraginaceaeCyperaceaeCyperaceaeCyperaceaePoaceae

Poaceae

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7

53

13

8

38

43

52

6

91

138

68

7

35

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106152

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34

3

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17

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144

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37

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28

24199

205

204

200

198

197

194

193

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195

196

17

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654970

661390

652890

682560

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613058

658680

591780

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7085305206/8

8288310

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8337630

8347970

8300850

8284430

8341404

8334790

8321040

8288310

8294600

8295260

8340/208304631

643720

654820

635340

656900

655700

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8297970

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8301290

8272750

8300850

8305/20

.

5206/8

667400

645780

621440

655700

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641750

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655500648640

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8304631

8347820

8303800

8312480

8300850

8308880

8302740

8306860

83014008286440

8314200

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8282/60

8289030

8292760

8299000

8303400

8299000

8295680

8295680

8305/20

^

,

.

^

I

.

Page 87: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

Species 1997

,Eragrostis sp.Eragrostis sp. IEragrostis sp. IEragrostis sp. IEragrostis sp. IEragrostis sp. IEragrostis sp. IEragrostis tenaxEragrostis tenaxEragrostis tenaxEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tene!IulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenel!ulaEragrostis teneilulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellula

I

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*

95

132

60

75

61

54

12160

156

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I I I

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652310

649386

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,

8299950

8305320

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8305700

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.

I

.

I

Page 88: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Eragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellu!aEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragrostis tenellulaEragtostis cumingiieraichne pulchellaEriachne armittii

Eriachne armittii

Eriachne armittii

Eriachne armittii

Eriachne armittiiEriachne avenacea

Eriachne avenacea

Eriachne basdowii

Eriachne based owli

Eriachne basedowiiEriachne basedowii

Eriachne basedowii

Eriachne basedowli

Eriachne basedowii

Eriachne basedowli

Eriachne basedowiiEriachne burkettii

Eriachne burkittiiEriachne ciliata

Eriachne ciliata

Eriachne ciliata

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15

30

13

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7

28

31

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54

52

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683550

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651890

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588330

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641370

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641750

622840655780

649590

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:

I

.

,

,

^

,

.

I

I

Page 89: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

^

.

Species 1997

:

^

Eriachne ciliata

Eriachne ciliata

Eriachne ciliataEriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne ciliata

Eriachne fastigiataEriachne fastigiataEriachne fastigiataEriachne glaucaEriachne glaucaEriachne glaucaEriachne glaucaEriachne glaucaEriachne glaucaEriachne glaucaEriachne glaucaEriachne glaucaEriachne glaucaEriachne glaucaEriachne glaucaEriachne glauca

Poaceae

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.

134

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143207

I 61

167

174

189

190

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129

123

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I I 5

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668040

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:

641750675660

614520

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641220

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8317038303520

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8303800

8299900

8299590

8303400

8299950

8282030

8294860

Page 90: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Eriachne glaucaEriachne glaucaEriachne glaucaEriachne glaucaEriachne glaucaEriachne Iatifolia

Eriachne medium

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusaEriachne obtusa

Eriachne obtusa

Eriachne obtusaEriachne obtusaEriachne obtusaEriachne obtusaEriachne obtusa

Eriachne obtusa

Eriachne obtusaEriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusaEriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusaEriachne obtusa

Eriachne obtusa

Eriachne obtusa

Poaceae

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6

22

37

36

33

127

12

11 9

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99

108

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5

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649830

659430

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6951 90

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674120

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65/890

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;

8352410

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8305320

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8292760

8285417

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8305770

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8290940

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8317210

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8337630

82806iO

,

Page 91: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

.

Species 1997

7Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusa

Eriachne obtusaEriachne obtusifolia

Eriachne obtusifolia

Eriachne obutsa

Eriachne pulchellaEriachne spEriachne sp.Eriachne sp.Eriachne sp.Eriachne sp.Eriachne sp.Eriachne SUIcataEriachne triseta

Eriachne triseta

Erythrina vespertilioErythrina vespertilioErythrina vespertilioErythropheum chiorostachysErythrophleum chlorostachysErythrophleum chlorostachysErythrophleum chlorostachysErythrophleum chlorostachysErythrophleum chlorostachysErythrophleum chlorostachysErylhrophleum chlorostachysErythrophleum chlorostachysErylhrophleum chlorostachysErythrophleum chlorostachysErythrophleum chiorostachysErythrophleum chlorostachysEryihrophleum chlorostachysErythrophleum chiorostachysErylhrophleum chlorostachysErythrophleum chiorostachysErythrophleum chlorostachys

,

*

.

.

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

CaesalpiniaceaeFabaceae

Fabaceae

CaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceae

.

,

45

50

73

51

77

74

76

63

61

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193

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127

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;

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645780

616210

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687740

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659630651400

651620

651620

672900

653330673870

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692090

647340

646620654270

619700

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619700

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647570

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670260653358

655810

8345950

8332950

8312470

8326750

8303800

8312690

8303850

8315860

8312480

8304770

8298810

82999508303/27

8316030

8312060

82806iO8305600

82909408282/60

8303400

8303400

8304000

82945308322360

8312060

8347970

8343070

83053208325580

8345300

8342920

8352260

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,

,

.

619700 8345300

Page 92: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Erythrophleum chiorostachysErythrophleum chlorostachysErythrophleum chlorostachysErythrophleum chlorostachysErythrophleum chiorostachysErythrophleum chlorostachysErythrophleum chlorostachysErythrophleum chlorostachysErythrophleum chlorostachysErythrophleum chiorostachysErythrophleum chlorostachysErythrophleum chlorostachysErythrophleum chiorostachysErythrophleum chlorostachysErythrophleum chlorostachysErythrophleum chiorostachysErythrophleum chlorostachysErythrophleum chiorostachysErythrophleum chlorostachysErythrophleum chiorostachysErythrophleum chlorostachysErythrophluem chiorostachysEryihrophluem chlorostachysErythrophluem chiorostachysErylhrophluem chlorostachysErythrophluem chiorostachysErvihrophluem chlorostachysErythrophluem chlorostachysErythrophluem chlorostachysErythrophluem chlorostachysEryihrophluem chlorostachysErythrophluem chlorostachysErythrophluem chiorostachysErythrophluem chlorostachysEry!hrophluem chiorostachysErythropleum chiorostachysEry!hropleum chlorostachysErythropleum chlorostachysErythropleum chiorostachysErythropleum chiorostachysErythropleum chlorostachysEucalyptus bigaleritaEucalyptus bigaleritaEucalyptus bigalerita

CaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeMynaceaeMynaceaeMynaceae

11 3

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22

29

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11 4

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8315830

8290940

8307470

8327460

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8304770

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8316100

:

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8342970

8354670

8343070

,

.

:

I

,

.

:

Page 93: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

Species 1997

Eucalyptus bigaleritaEucalyptus bigaleritaEucalyptus bigaleritaEucalyptus brevifoliaEucalyptus carnaldulensisEucalyptus carnaldulensisEucalyptus carnaldulensisEucalyptus carnaldulensisEucalyptus camauldulensisEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus microthecaEucalyptus miniataEucalyptus miniataEucalyptus miniataEucalyptus miniataEucalyptus miniataEucalyptus miniataEucalyptus miniataEucalyptus miniata

I

MynaceaeMynaceaeMynaceaeMynaceaeMyrtaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceae

.

129

89

129208

24

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150

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8301400

8300850

8272820

83039008305600

8300632

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8295260

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.

.

.

.

Page 94: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Eucalyptus miniataEucalyptus miniataEucalyptus miniataEucalyptus miniataEucalyptus papuanaEucalyptus papuanaEucalyptus papuanaEucalyptus papuanaEucalyptus papuanaEucalyptus papuanaEucalyptus papuanaEucalyptus papuanaEucalyptus papuanaEucalyptus papuanaEucalyptus papuanaEucalyptus papuanaEucalyptus papuanaEucalyptus papuanaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus phoeniceaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosa

MynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceae

42

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620000

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601640618432

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I

:

,

,

.

^

,

.

Page 95: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

Species 1997

,

Eucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus pruinosaEucalyptus sp.Eucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus techficaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus techficaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus tectificaEucalyptus tetrodontaEucalyptus tetrodontaEucalyptus tetrodontaEucalyptus tetrodontaEucalyptus tetrodontaEucalyptus tetrodontaEucalyptus tetrodontaEucalyptus tetrodontaEucalyptus tetrodontaEucalyptus tetrodontaEucalyptus tetrodonta

,

,

,

MynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceae

15

19

20

60

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17

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96

99

105207

123192

192

I 91

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140

I 31

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81

83

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11 7

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184

146

92

140

135

103

102

80

79

674120

683550

671200

64/220

654370

680250

645530

677020

68/060707640

687740

6/2/30649590

649590

672500

672500

667400

667400

647570

647400

622840

612880

615460

623060

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8304550

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8314600

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I

:

Page 96: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Eucalyptus tetrodontaEucalyptus tintinnansEucalyptus tintinnansEucalyptus tintinnansEucalyptus tintinnansEucalyptus tintinnansEucalyptus tintinnansEucalyptus tintinnansEucalyptus tintinnansEucalyptus tintinnansEucalyptus tintinnansEUlalia aurea

EUlalia aurea

EUlalia aurea

EUlalia fulva

EUlalia fulva

Euphorbia tannensisEvolvulus alsinoides

Excocaria parvifoliaExcoecaria hemiglaucaExcoecaria hemiglaucaExcoecaria hemiglaucaExcoecaria hemiglaucaExcoecaria parivifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifoliaExcoecaria parvifolia

MynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaePoaceae

Poaceae

Poaceae

Poaceae

Poaceae

EuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceae

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16

32

33

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658680

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Page 97: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

Species 1997

Fabaceae sp

Fabaceae sp.Ficus coronulataFicus coronulataFicus coronulataFicus coronulata

Ficus OPPositaFicus OPPositaFicus racemosa

Ficus racemosa

Ficus racemosa

Ficus racemosa

F1mbristylis acuminataF1mbristylis clavataF1mbristylis clavataFimbristylis clavataFimbristylis clavataF1mbristylis clavataFimbristylis clavataF1mbristylis clavataFimbristylis clavataFimbristylis clavataFimbristylis clavataFimbristylis densaFimbristylis densaFimbristylis densaFimbristylis densaFimbristylis densaF1mbristylis densaFimbristylis densaFimbristylis macranthaF1mbristylis macranthaF1mbristylis macranthaFimbristylis macranthaF1mbristylis macranthaFimbristylis macranthaFimbristylis macranthaFimbristylis macranthaF1mbristylis macranthaFimbristylis macranthaF1mbristylis macranthaF1mbristylis macranthaFimbristylis microcaryaFimbristylis microcarya

*

Fabaceae

Fabaceae

Moraceae

Moraceae

Moraceae

Moraceae

Moraceae

Moraceae

Moraceae

Moraceae

Moraceae

Moraceae

CyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceae

*

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8299590

8304/40

8347820

8318/80

8339700

8317080

831703

8312470

8321/20

8352410

8316/40

8323200

8321810

8322020

8296605

8340/208332860

8347970

8294860

8296605

82909408304631

..

Page 98: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Fimbristylis pachypteraFimbristylis pallidaF1mbristylis pallidaFimbristylis phaeoleucaF1mbristylis phaeoleucaFimbristylis phaeoleucaF1mbristylis phaeoleucaFimbristylis phaeoleucaFimbristylis phaeoleucaFimbristylis phaeoleucaFimbristylis phaeoleucaFimbristylis phaeoleucaFimbristylis phaeoleucaFimbristylis phaeoleucaFimbristylis phaeoleucaFimbristylis phaeoleucaFimbristylis phaeoleucaFimbristylis phaeoleucaFimbristylis pterygospermaF1mbristylis schultziiFimbristylis schultziiFimbristylis schultziiFimbristylis schultziiFimbristylis schultziiF1mbristylis schultziiFimbristylis schultzii BoeckelerFimbristylis schultzii BoeckelerFimbristylis schultzii BoeckelerFimbristylis schultzii BoeckelerF1mbristylis schultzii BoeckelerFimbristylis schultzii Boecke!erFimbristylis schultzii BoeckelerFimbristylis schultzii BoeckelerFimbristylis schultzii BoeckelerFimbristylis schultzii 80eckelerFimbristylis schultzii BoeckelerF1mbristylis schultzii BoeckelerF1mbristylis schultzii BoeckelerF1mbristylis schultzii BoeckelerFimbristylis schultzii BoeckelerFimbristylis schultzii BoeckelerFimbristylis schultzii BoeckelerF1mbristylis schultzii BoeckelerFimbristylis schultzii Boeckeler

CyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceae

124153

152

149

95

75

58

49

46

48

43

40

9

39

6

11

28

37157

47

50

51

20

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19

I I O

102

103

106

108

120

11 O

123

132

143

147

92

100

74

90

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61 4150

5206/8

670230

677490

645530

647500

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692090

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649830

654620

656290

665760672900

681500

680380

677600

671200

674120

683550

695190

706390

706680

708530

700940

8332000

8304631

8332420

8299950

8303930

8295330

8333650

8341670

8333930

8347970

8341220

8294530

8338940

8284430

8297060

830686083088808304000

8335290

8332950

83267508304/40

8304550

8305700

8346850

8321720

8322000

8340/20

8346780

.

,

.

,

695190

6/2/30

646620

664170

683990

610550

703040

616210

605890

640590

643720

652420

652890

I

8346850

8331310

8305320

8349880

8338/30

8335330

8318590

8312690

8354080

8314600

8297970

8288310

8291390

*

.

Page 99: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

,

:Species 1997

,

F1mbristylisschultziiBoeckeler CyperaceaeFimbristylisschultziiBoeckeler CyperaceaeFimbristylisschultziiBoeckeler CyperaceaeF1mbristylisschultziiBoeckeler CyperaceaeFimbristylisschultziiBoeckeler CyperaceaeFimbristylisschultziiBoeckeler CyperaceaeFimbristylisschultziiBoeckeler CyperaceaeFimbristylisschultziiBoeckeler CyperaceaeFimbristylisschultziiBoeckeler Cyperaceae

CyperaceaeFimbristylis solidifoliaCyperaceaeF1mbristylis sp.CyperaceaeFimbristylis sp.CyperaceaeFimbristylis spCyperaceaeFimbristylis sp.CyperaceaeFimbristylis spCyperaceaeF1mbristylis spCyperaceaeF1mbristylis spCyperaceaeFimbristylis sp.CyperaceaeFimbristylis sp.CyperaceaeFimbristylis spCyperaceaeFimbristylis sp.CyperaceaeFimbristylis sp.CyperaceaeFimbristylis spCyperaceaeFimbristylis sp.CyperaceaeFimbristylis sp.CyperaceaeFimbristylis spCyperaceaeFimbristylis sp.

Fimbristylis sp. 25 (New species) CyperaceaeCyperaceaeF1mbristylis tetrangonaCyperaceaeF1mbristylis trachycaryaCyperaceaeFimbristylis trigastrocaryaFlagelliaraceaeFlagellaria indicaFlagelliaraceaeFlagellaria indicaFlagelliaraceaeFlagellaria sp.FabaceaeFlemingia lineataFabaceaeFlemingia paucifloraFabaceaeFlemingia paucifloraFabaceaeFlemingia paucifloraFabaceaeFlemingia paucifloraFabaceaeFlemingia paucifloraFabaceaeFlemingia paucifloraFabaceaeFlemingia paucifloraFabaceaeFlemingia paucifloraFabaceaeFlemingia pauciflora

:

,

.

.

I

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76

25

25

34

41

63

73

73

59155

133

90

132159

62

144155

67

14

55

10

5

5

53

22

45

48

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3

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3

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126

126

41

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59

58

106

46

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38

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,

.

645940

653050

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622230

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616030

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8297970

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8315860

8312470

8312470

8302530

.

646100

605890

646620665577

621550

667400

.

8305820

8354080

83053208303/27

8312/30

8347820

o

621740

668040

654380

655220

651890

651890

654970

659430

689540

680750

653050

654820

591780

654820

621460

620120

620120

685920

680750

647400

647500

708530

684750

684750

682560

680730

683300

83/1040

83034008299590

8294860

8282030

8282030

8299950

8290940

8345950

8333930

8302440

8340/20

8321 040

8276470

83/0830

8345060

8345060

8343550

8333930

8302530

8295330

8340/20

8341670

8341670

8337630

8333650

8338940

.

Page 100: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Fleming Ia paucifloraFlueggea virosaFlueggea virosaFlueggea virosaFlueggea virosaFlueggea virosaFlueggea virosaFlueggea virosaFlueggea virosaFlueggea virosaFlueggea virosaFlueggea virosaFlueggea virosaFlueggea virosaFlueggea virosaFlueggea virosaFlueggea virosaFuirena ciliarisFuirena ciliaris

Fuirena ciliarisGardenia fucata

Gardenia fucata

Gardenia fucata

Gardenia fucata

Gardenia fucata

Gardenia megaspermaGardenia megaspermaGardenia megaspermaGardenia megaspermaGardenia megaspermaGardenia megaspermaGardenia megaspermaGardenia megaspermaGardenia megaspermaGardenia megaspermaGardenia megaspermaGardenia megaspermaGeodorum neocaledonicumGermainia grandifloraGermainia truncatiglumisGermainia truncatiglumisGermainia truncatiglumisGermainia truncatiglumisGlochidion xerocarpum

Fabaceae

EuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeCyperaceaeCyperaceaeCyperaceaeRubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Orchidaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Euphorbiaceae

40

142

139

I14

I 13

109

95

84

54

16

44

2

46

25

32

38

144152

153

189

207

128

22

18

120

145

I 31

127

124

143

11 7

100

80

42

3

102

66153

144

16

137

24

16

684490

656900

640000

647340

614340

614620

701180

677490

620000

655510

676700

69/020

656440

684750

653050

635340

682560

6674005206/8

8341220

8272750

8353590

8343070

8316100

8316/40

8347/60

8299950

8324300

8298810

8303900

8347480

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.

.

,

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659430

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o

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:

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615050

703040

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654820

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621460

,

8348200

83242908345300

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8349880

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8350483

82764708321720

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:

. -

:

667400

676700

659640655500

676700

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8303900

83372808301400

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^

I

:

:

Page 101: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

;

,

Species 1997

, Glochidion xerocarpumGlochidion xerocarpumGlochidion xerocarpumGlochidion xerocarpumGlochidium sp.Gineiina schlechteriGineiina schlechteri

Gomphrena canescensGomphrena canescensGomphrena canescensGomphrena canesGensGomphrena canescensGomphrena canesGensGomphrena canescensGomphrena canescensGomphrena sp.Gomphrena sp.Gonocarpus IeptothecusGonocarpus IeptothecusGoodenia bicolor

Goodenia hePPIeanaGoodenia he PPIeanaGoodenia hePPIeanaGoodenia hePPIeanaGoodenia hePPIeanaGoodenia hePPIeanaGoodenia holtziana

Goodenia lamprospermaGoodenia lamprospermaGoodenia lamprospermaGoodenia lamprospermaGoodenia lamprospermaGoodenia lamprospermaGoodenia lamprospermaGoodenia lamprospermaGoodenia sp.Goodenia sp.Gossypium australeGossypium australeGossypium australeGrevillea agrifoliaGrevillea agrifoliaGrevillea agrifoliaGrevillea agrifoliaGrevillea agrifolia

.

EuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeVerbenaceae

Verbenaceae

Amaranthaceae

Amaranthaceae

Amaranthaceae

Amaranthaceae

Amaranthaceae

Amaranthaceae

Am arantnaceae

Amaranthaceae

Amaranthaceae

Amaranthaceae

HaloragaceaeHaloragaceaeGoodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Goodenia

Goodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Maivaceae

Malvaceae

Malvaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

I

24

52

84

94153

87

126174

157

I 41

100

I 01

50

20

15

30I54

152

153

73

61

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99

81

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34

58

57

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16

6

to

8

147

9

30

43

I 51

185

190

184

79

72

655500

655700

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605680

8301400

8300850

8324300

8326260

609560

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672900

647570

703040

7030iO

680380

671200

674120

654370618432

5206/8

I

8339700

83450608282648

8304000

8342920

8318590

8318/80

8332950

8304/40

8304550

8307/808304390

8304631

.

616030

621440

646100

619700

68/060

635790

623060662193

643720

647500

648550

647400

676700

649830

655220

652890

683990

653330

654370

692090

688590655920

693500

654270

641370

60/780

8312470

8312480

8305820

8345300

8305350

8317210

83158308303/74

8297970

8295330

8295260

8302530

8303900

8284430

8294860

8291390

8338/30

8294530

8307/80

8347970

834645083282708304000

83255808317080

8321/20

.

Page 102: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Grevillea angularaGrevillea angulataGrevillea angulataGrevillea angulataGrevillea angulataGrevillea angulataGrevillea angulataGrevillea decurrens

Grevillea decurrens

Grevillea decurrensGrevillea decurrensGrevillea decurrensGrevillea decurrens

Grevillea decurrensGrevillea decurrens

Grevillea decurrens

Grevillea decurrens

Grevillea decurrens

Grevillea decurrens

Grevillea decurrensGrevillea decurrens

Grevillea decurrensGrevillea dimidiata

Grevillea dimidiata

Grevillea dryandriGrevillea dryandriGrevillea dryandriGrevillea erythrocladaGrevillea he IiospermaGrevillea in jinosojdesGrevillea in jinosoides

Grevillea myOSodes (3KC-)G revillea pteridifoliaGrevillea pteridifoliaGrevillea pteridifoliaGrevillea pteridifoliaGrevillea pyrimidalisGrevillea refracta

Grevillea refracta

Grevillea refracta

Grevillea retusifoliaGrevillea retusifolia

Grevillea striataGrevillea striata

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

134154

135

107

80

78

70

143

I 31

148

145

124185

125

80

103

63

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71

92

78

86

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I 41

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128

92

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I 31

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70

138166

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67

67

6203

13

13

646080618432

646280

711530

640590

641750

588330

664170

622840

670260

667400

6/4/50655920

614350

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706680

622230

654820

601640

610550

641750

609860

655770

647570

664170

646280

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653000

588330

658680654841

647570

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621740

621740

649830667550

66,390

66,390

83280108304390

8328010

8339790

8314600

831703

8339/20

8349880

8324290

8323530

8348200

83320008328270

8332060

8314600

8322000

8315860

8340/20

8320980

8335330

831703

8339700

8305/40

8342920

8349880

83280t O

8318590

8360040

8335330

8304/40

8324290

8324290

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83347908278410

8342920

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83/1040

83/1040

82844308316970

8302470

8302470

.

.

.

.

II

.

.

.

I

.

^

I

Page 103: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

I

:

Species 1997

,Grevillea striataGrevillea striataGrevillea striata

Grewia TetusifoliaGrewia retusifolia

Grewia retusifoliaGrewia retusifoliaGrewia retusifolia

Grewia retusifoliaGrewia retusifoliaGrewia retusifolia

Grewia retusifolia

Grewia retusifolia

Grewia retusifoliaGrewia retusifolia

Grewia retusifoliaGrewia retusifoliaGrewia retusifoliaGrewia retusifolia

Grewia retusifoliaGrewia retusifoliaGrewia retusifolia

Grewia retusifoliaGrewia retusifoliaGrewia retusifolia

Gymnanthera sp.Gyrocarpus americanusGyrocarpus americanusGyrocarpus americanusGyrocarpus americanusGyrocarpus americanusGyrocarpus americanusGyrocarpus americanusGyrocarpus americanusGyrocarpus americanusHaemodorum coccineumHaemodorum coccineum

Haemodorum coccineum

Haemodorum coccineum

Haemodorum coccineumHaemodorum coccineum

Haemodorum coccineum

Hakea arborescensHakea arborescens

.

Proteaceae

Proteaceae

Proteaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

Tiliaceae

AsclepiadaceaeHernandiaceae

Hernandiaceae

Her nandiaceae

HemandiaceaeHernandiaceae

Hernandiaceae

Hernandiaceae

Hernandiaceae

Hernandiaceae

Haemodoraceae

Haemodoraceae

Haemodoraceae

Haemodoraceae

HaemodoraceaeHaemodoraceae

Haemodoraceae

Proteaceae

Proteaceae

.

54205

54

11 4

108

11 2

I I 3168

127

133158

94

99

132

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16

17

24

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150

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,

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655510

614340

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614620647526

619700

646100662193

605680

68/060

646620

605700

620000

676700

680250

655500

654370

684490

692090

623060

645940

620290

619350647526

648656

708530

620000

620290

621440

635340

635340

656900

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706680

703040

653000

659430

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8298810

8316100

8346780

8316370

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8345300

83058208303/74

8326260

8305350

8305320

8326080

8324350

8303900

8305/20

8301400

8307/80

8341220

8347970

8315830

8303850

8324640

83522608277378

8300632

8340/20

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8324640

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8301290

8301290

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8324290

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8321810

8322000

8318590

8280610

8290940

8342920

8354670

^

,

.

,.

Page 104: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Hakea arborescens

Hakea arborescensHakea arborescens

Hakea arborescens

Hakea arborescens

Hakea arborescens

Hakea arborescens

Hakea arborescens

Hakea arborescens

Hakea arborescens

Hakea arborescens

Hakea arborescens

Hakea arborescens

Hakea arborescens

Hakea aroborescens

Hakea aroborescensHakea aroborescens

Hakea suberea

Hakea suberea

Hakea suberea

Hakea suberea

Hakea suberea

Hakea suberea

Hakea suberea

Halosarcia halocnemoides

Hellcteres sp.HeIiotropium sp.Hellotropium sp.He Iiotropium tenuifoliumHellotropium tenuifoliumHerb sp.Herb sp.Heteropogan contortusHeteropogan contortusHeteropogan contortusHeteropogan contortusHeteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon contortus

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

ChenopodiaceaeSterculiaceae

BoraginaceaeBoraginaceaeBoraginaceaeBoraginaceae

203

169

170

78

80

43

72

46

31

10

26

33

40

41

10

54203

120

127

123

I 01

11 9

105

100

68

32

75

124

19

36

I32

32194

199

203

I 91

139

95

11 4160

152

153

83168

88

667550

647853

649567

641750

640590

692090

601780

684750

643480

655220

655770

641750

684490

685920

655220

655510667550

8316970

8277781

8280819

831703

8314600

8347970

8321/20

8341670

8305350

8294860

8305/40

8302740

8341220

8343550

8294860

82988108316970

;

619700

6/2/30

703010

617830707640

703040

591780

635340

645530

6/4/50

683550

658060

646620

635340654900

648640

667550

672500

647340

677490

614340675660

5206/8

Poaceae

Poaceae

Poaceae

Poaceae

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8345300

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8318/80

83232008332860

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.

^

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.

Page 105: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

^

Heteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon contortusHeteropogon triticeusHeteropogon triticeusHeteropogon triticeusHeteropogon triticeusHeteropogon triticeusHeteropogon triticeusHibbertia sp.Hibiscus panduriformisHibiscus panduriformisHibiscus sp.Hygrophila an gustifoliaHygrophila an gustifoliaHygrophila an gustifoliaHygrophila an gustifoliaHygrophila an gustifoliaHygrophila an gustifoliaHyptis suave o1ens*Indigofera coluteaIndigofera GoluteaIndigofera coluteaIndigofera coluteaIndigofera coluteaIndigofera 11nifoliaIndigofera IinifoliaIndigofera 11nifoliaIndigofera IinifoliaIndigofera IinifoliaIndigophera jinifoliaIPOmoea copticaIPOmoea costataIPOmoea sp.Ischaemum australe

Iseilema vaginiflorumIseilema vaginiflorumIseilema vaginiflorum

Poaceae

Poaceae

Poaceae

Poaceae

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Maivaceae

Malvaceae

Malvaceae

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ACanthaceae

ACanthaceae

ACanthaceae

ACanthaceae

ACanthaceae

Lamiaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

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Fabaceae

Fabaceae

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Convolvulaceae

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,

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8289727

Page 106: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Iseilema vaginiflorumIseilema vaginiflorumIseilema vaginiflorumIseilema vaginiflorumJacksonia dilatataJacksonia forrestiiJasmimum didyinumJasminum moile

Jasminum in o11eJasminum moile

Jasminum in o11eLeea rubra

Leea rubra

Leptochloa neesiiLimnophila fragransLimnophila fragransLindernia clausa

Lindsaea ensifoliaLipocarpa microcephalaLitsea glutinosaLoinandra tropicaLoinandra tropicaLoinandra tropica

Lophostemon grandiflorusLophostemon grandiflorusLudwigia octovalvisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennis

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Oleaceae

Oleaceae

Oleaceae

Oleaceae

Oleaceae

Leeaceae

Leeaceae

Poaceae

ScrophulariaceaeScrophulariaceaeScrophulariaceaeLindsaeaceae

CyperaceaeLauraceae

Xanthorrhoeaceae

Xanthorrhoeaceae

Xanthorrhoeaceae

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.

I

,

Page 107: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Ludwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLudwigia perennisLuffa grave o1ensLysiana subflacataLysiphylla cunning hammiiLysiphylla cunning hammiiLysiphylla cunning hammiiLysiphylla cunning hammiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunninghamiiLysiphyllum cunning hamii

,

.

On agraceaeOn agraceaeOn agraceaeOn agraceaeOn agraceaeOn agraceaeOn agraceaeOn agraceaeOn agraceaeCucurbitaceae

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,

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Page 108: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Lysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hamiiLysiphyllum cunning hammiLysiphyllum cunning hammiLysiphyllum cunning hammiLysiphyllum cunning hammiLysiphyllum cunning hammiLysiphyl!urn cunning hammiLysiphyllum cunning hammiLysiphyllum cunning hammiLysiphyllum cunning hammiLysiphyllum cunning hammiLysiphyllum cunning hammiLysiphyllum cunning hammiLysiphyllum cunning hammiLysiphyllum cunning hammiMacaranga involucrataMarsilea drummondii

Maytenus cunning hamiiMe Ialeuca argenteaMeIaleuca argenteaMe Iaieuca argenteaMe Ialeuca citrolens

Me Ialeuca IeucadendraMe Iaieuca IeucadendraMe Iaieuca Ieucadendra

Me Iaieuca Ieucadendra

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Me Ialeuca IeucadendraMe Iaieuca IeucadendraMe Ialeuca IeucadendraMeIaieuca IeucadendraMe Ialeuca IeucodendraMe Ialeuca minutifoli

Me Ialeuca minutifoliaMe Ialeuca minutifolia

Me Iaieuca minutifoliaMe Ialeuca minutifolia

Me Ialeuca minutifolia

CaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeCaesalpiniaceaeEuphorbiaceaeMarsileaceae

Celastraceae

MynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMyrtaceae

25

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^

^

.

:

.

Page 109: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

;

Species 1997

Me Iaieuca minutifolia

Me Ialeuca minutifolia

Me Ialeuca minutifolia

Me Ialeuca minutifoliaMe Ialeuca minutifoliaMe Iaieuca minutifolia

Me Ialeuca minutifoliaMe Ialeuca minutifoliaMe Iaieuca minutifoliaMe Iaieuca minutifoiiaMe Ialeuca minutifoliaMe Ialeuca minutifoliaMe Iaieuca minutifoliaMe Iaieuca minutifolia

Me Iaieuca minutifoliaMe Iaieuca minutifolia

Me Iaieuca minutifo!IaMe Ialeuca minutifoliaMe Ialeuca minutifolia

Me Ialeuca minutifoliaMe Iaieuca minutifolia

Me Iaieuca minutifoliaMe Iaieuca minutifolia

Me Iaieuca minutifoliaMe Iaieuca minutifoliaMe Iaieuca minutifoliaMe Ialeuca minutifoliaMe Iaieuca minutifoliaMe Ialeuca minutifolia

Me Ialeuca minutifoliaMe Ialeuca minutifoliaMe Iaieuca minutifoliaMe Ialeuca minutifoliaMe Ialeuca minutifoliaMe Iaieuca minutifoliaMe Ialeuca minutifoliaMe Iaieuca minutifoliaMe Ialeuca minutifoliaMe Ialeuca minutifoliaMe Ialeuca minutifoliaMe Ialeuca minutifolia

Me Ialeuca nervosa

Me Ialeuca nervosa

Me Iaieuca nervosa

Me Iaieuca nervosa

.

MynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceae

,

.

^

11 4

11 3

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133

132174

I 51192

206

202

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187

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108I 61

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8316370

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83464508312060

8316960

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8303/27

8326590

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8290940

8326080

Page 110: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Me Ialeuca nervosa

Me Ialeuca sericea

Me Ialeuca sericea

Me Ialeuca sericeaMe Iaieuca sericeaMe Ialeuca sericeaMe Iaieuca sericea

Me Iaieuca sericea

Me Ialeuca sericeaMe Ialeuca sericeaMe Iaieuca sericea

Me Ialeuca sericea

Me Ia!euca sericeaMe Iaieuca sericeaMe Ialeuca sericeaMe Ialeuca sericea

Me Ialeuca ser!cea

Me Ialeuca sericea

Me Ialeuca sp.Me Ialeuca sp. 181Me Ialeuca virdiflora

Me Ialeuca viridifloraMe Iaieuca viridiflora

Me Iaieuca viridifloraMe Ialeuca viridifloraMe Ialeuca viridifloraMe Iaieuca viridiflora

Me Ialeuca viridifloraMe Ialeuca viridifloraMe Ialeuca viridifloraMe Ialeuca viridifloraMe Ialeuca viridifloraMe Iaieuca viridifloraMe Ialeuca viridifloraMe Ialeuca viridifloraMe Iaieuca viridiflora

Me Ialeuca viridifloraMe Ialeuca viridifloraMe Iaieuca viridifloraMe Ialeuca viridifloraMe Ialeuca viridifloraMe Ialeuca viridifloraMe Iaieuca viridifloraMe Ialeuca viridifloraMe Ialeuca viridiflora

Me Iaieuca viridiflora

MynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMyrtaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceae

22

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8326590

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8288341

8321810

^

Page 111: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

Species 1997

Me Ialeuca viridiflora

Me Iaieuca viridiflora

Me Ialeuca viridifloraMe Ialeuca viridifloraMe Ialeuca viridiflora

Me Iaieuca viridif!oraMe Ialeuca viridifloraMe Iaieuca viridif!ora

Me Ialeuca viridifloraMe Iaieuca viridiflora

Me Ialeuca viridifloraMe Ialeuca viridifloraMe Iaieuca viridifloraMe Iaieuca viridifloraMe Ialeuca viridifloraMe Ialeuca viridifloraMe Iaieuca viridifloraMe Ialeuca viridifloraMe Ialeuca viridifloraMe Iaieuca viridifloraMe Iaieuca viridifloraMe Iaieuca viridifloraMe Ialeuca viridifloraMe Ialeuca viridifloraMe Iaieuca viridifloraMe Ialeuca viridiflora

Melastoma sp.Me Ihania incana

Me Ihania incana

Me 11cope elleryanaMe!ICOpe elleryanaMe 11cope elleryanaMe Iicope eileryanaMe Iicope elleryanaMerremia sp.Mistletoe

Mistletoe

Mistletoe

Mistletoe (on E. Iatifolia)Mistletoe (on E. pruinosa)Mitrasacme connata

Mitrasacme connata

Mitrasacme connata

Mitrasacme connata

Mitrasacme connata

a

,

MynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMyF1aceaeMynaceaeMynaceaeMynaceaeMynaceaeMynaceaeMelastomataceae

Sterculiaceae

Sterculiaceae

Rutaceae

Rutaceae

Rutaceae

Rutaceae

Rutaceae

Convolvulaceae

Loranthaceae

Loranthaceae

Loranthaceae

Loranthaceae

Loranthaceae

LoganiaceaeLoganiaceaeLoganiaceaeLoganiaceaeLoganiaceae

.

105

11 2

22

37

24

23

9

21

51

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60/780

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620450

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616210

616030

609560

671200

643480

620120

667400

621460

609560

621460

614340

647500

667400

688590

617830

645530

622840

612880

617830

640590

703010

8332860

8316370

8290940

8308880

8301400

8290940

8294530

8296605

8326750

8294530

8282030

8347100

8335290

8294860

8300850

83420208354680

8321/20

8318/80

8341404

8280610

8324670

8303800

8303850

8312690

8312470

8339700

8304/40

8305350

8345060

8347820

83/0830

8339700

83/0830

8316iOO

8295330

8347820

8346450

8323200

8303930

8324290

8327760

8323200

8314600

8318/80

,

Page 112: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Mitrasacme connata

Mitrasacme connata

Mitrasacme connata

Mitrasacme connata

Mitrasacme connata

Mitrasacme connata

Mitrasacme connata

Mitrasacme connata

Mitrasacme sp.Mnesithea rottboelioidesMnesithea rottboellioidesMnesithea rotlboellioidesMnesithea rottboellioidesMnesithea rottboellioides

Mnesithea rottboellioidesMnesithea rottboellioidesMnesithea rottboellioidesMnesithea rottboellioidesMnesithea rottboellioidesMnesithea rottboellioidesMnesithea rottboellioides

Mucuna giganteaMucuna giganteaNauclea orientalisNauclea orientalis

Nauclea orientalisNelsonia campestrisNelsonia campestrisNelsonia campestrisNelsonia campestrisNelsonia campestrisNelsonia campestrisNeptunia dimorphanthaNeptunia dimorphanthaNeptunia dimorphanthaNeptunia dimorphanthaNeptunia dimorphanthaNeptunia dimorphanthaNeptunia dimorphanthaNeptunia gracilisNeptunia gracilisNeptunia gracilisNeptunia gracilisNeptunia gracilisNeptunia yellow

LoganiaceaeLoganiaceaeLoganiaceaeLoganiaceaeLoganiaceaeLoganiaceaeLoganiaceaeLoganiaceaeLoganiaceaePoaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Fabaceae

Fabaceae

Nauclea

Nauclea

Nauclea

ACanthaceae

ACanthaceae

ACanthaceae

ACanthaceae

ACanthaceae

ACanthaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

Mimosaceae

102

69

61

20

12

60

54

55154

158

193

153

152

140

139

130

95

94

87

16

7

66

126

84

130

142153

153

35152

95

6

59

58

55

33

19

8

7199

196

188

I I O

36

43

706390

586980

621440

67/200

655230

641220

655510

654380618432

662193

651620

8321720

8342020

8312480

8304/40

8300250

8304770

8298810

82995908304390

8303/74

8303400

5206/8

647400

647340

619350

677490

605680

609560

676700

652420

621460

620120

620000

619350

640000

8304631

8342970

8343070

8352260

8299950

8326260

8339700

8303900

8288310

83/0830

8345060

8324300

8352260

8353590

I

.

^

6458805206/8

677490

649830

647400

647500

654380

641750

683550

652890

65242064864065/550

673870

695190

658060

692090

82946008304631

8299950

8284430

8302530

8295330

8299590

8302740

8305700

8291390

82883108286440

8295680

8322360

8346850

8305720

8347970

.

.

:

.

Page 113: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

.

Species 1997

NYmpaea violaceaOldenlandia initrasacmoides

Oldenlandia initrasacmoidesOldenlandia initrasacmoidesOldenlandia initrasacmoidesOldenlandia initrasacmoidesOldenlandia initrasacmoides

Oldenlandia initrasacmoidesOldenlandia initrasacmoides

Oldenlandia initrasacmoides

Oldenlandia initrasacmoides

Oldenlandia initrasacmoidesOldenlandia initrasacmoidesOldenlandia initrasacmoidesOldenlandia initrasacmoides

Oldenlandia initrasacmoidesOldenlandia initrasacmoidesOldenlandia initrasacmoides

Oldenlandia initrasacmoides

Operculina aequisepalaOperculine aequisepalaOphiuros axaltatusOphiuros axaltatusOphiuros axaltatusOphiuros axaltatusOphiuros exaltatusOphiurus exaltatusOphiurus exaltatusOphiurus exaltatusOryza australiensisOryza australiensisOwenia vernicosa

Owenia vernicosa

Owenia vernicosaOwenia vernicosa

Owenia vernicosa

Owenia vernicosaOwenia vernicosa

Owenia vernicosaOwenia vernicosaOwenia vernicosa

Pachynema sphenandrumPachynema sp.Pandanus aquaticus

,

NymphaeaceaeRubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Convolvulaceae

Convolvulaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Meliaceae

Meliaceae

Meliaceae

Meliaceae

Meliaceae

Meliaceae

Meliaceae

Meliaceae

Meliaceae

Meliaceae

Dilleniaceae

Dilleniaceae

Pandanaceae

^

I

I

138

I I 2

81

11 O

133

129

I 31

76

79

99

75

59

15

54

61

72

63

4

71

34

57

58

40

57

34

46172

I77

179

35

91190

189

183

154

107

127

69

42

18

67

134

71

142

658680

614520

635790

695190

646100

619350

622840

645940

641370

68/060

645530

647400

674120

655510

621440

601780

622230

653000

601640

643720648550

647500

684490

648550

643720

684750649173

647339

652310

645880

613058693500

686700

8334790

8316370

8317210

8346850

8305820

8352410

8324290

8303850

8317080

8305350

83039308302530

8304550

8298810

8312480

8321/20

8315860

82806108320980

8297970

8295260

8295330

8341220

8295260

8297970

83416708284998

8289727

828834t

8294600

83414048304000

8304600

.

,

^

618432

711530

619700

586980

692391

686580621740

646080

601640640000

8304390

8339790

8345300

8342020

8350483

8305400

83/1040

83280iO

8320980

8353590

Page 114: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Pandanus aquaticusPandanus aquaticusPandanus aquaticusPandanus aquaticusPandanus spiralisPandanus spiralisPandanus spiralisPandanus spiralisPandanus spiralisPandanus spiralisPandanus spiralisPanicum decompositumPanicum decompositumPanicum decompositumPanicum decompositumPanicum decompositumPanicum decompositumPanicum decompositumPanicum decompositumPanicum decompositumPanicum decompositumPanicum decompositumPanicum decompositumPanicum decompositumPanicum decompositumPanicum mindanaense

Panicum mindanaense

Panicum mindanaense

Panicum seminudumPanicum seminudum

Panicum seminudumPanicum seminudum

Panicum trachyrachisPanicum trachyrachisParkinsonia aculeata*

Paspalum SCObiculatumPaspalum scrobiculatumPassiflora foetida*Passiflora foetida*

Pennisetum pedicellatum*Persoonia falcata

Persoonia falcata

Persoonia falcataPersoonia falcataPersoonia falcata

Pandanaceae

Pandanaceae

Pandanaceae

Pandanaceae

Pandanaceae

Pandanaceae

Pandanaceae

Pandanaceae

Pandanaceae

Pandanaceae

Pandanaceae

Pandanaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

CaesalpiniaceaePoaceae

Poaceae

Passifloraceae

Passifloraceae

Poaceae

Proteaceae

Proteaceae

Proteaceae

Poaceae

Poaceae

144

130

142

137

95

138

128

21

87

86

84205

182

I 81

177

174

172

130

147

95

52

37

36

24

94

13

11

12

16

53

54

55

11 8

98

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95153

89

139

103

134

148200

154

667400

619350

640000

659640

677490

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625720

664942

609560

609860

620000673800

654940

653260

647339

649386

649173

619350

683990

677490

655700

665760

658060

655500

605680

661390

654620

655230

676700

654970

655510

654380

615460

678480

656440

677490

8347820

8352260

8353590

8337280

8299950

8334790

8360040

8296605

8339700

8339700

83243008314200

8299846

8294327

8289727

8282648

8284998

8352260

8338/30

8299950

8300850

8308880

83057208301400

8326260

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.

.

.

.

602410

647340

656900

706680

646080

67026065/400

618432

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8272750

8322000

83280iO

83235308282/60

8304390

o

.

.

I

Page 115: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

I

Species 1997

Persoonia falcataPersoonia falcata

Persoonia falcata

Persoonia falcataPersoonia falcataPersoonia falcata

Persoonia falcataPersoonia falcata

Persoonia falcataPersoonia falcataPersoonia falcataPersoonia falcataPersoonia falcata

PetalOStigma banksiiPetalOStigma banksiiPetalOStigma banksiiPetal OStigma banksiiPetalOStigma banksiiPetalOStigma banksiiPetalOStigma pubescensPetalOStigma pubescensPetalOStigma pubescensPetalOStigma pubescensPetalOStigma pubescensPetalOStigma pubescensPetalOStigma pubescensPetalOStigma pubescensPetalOStigma pubescensPetalOStigma pubescensPetalOStigma pubescensPetalOStigma pubescensPetalOStigma pubescensPetalOStigma pubescensPetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadriloculare

Poaceae

Poaceae

Proteaceae

Proteaceae

Proteaceae

Proteaceae

Poaceae

Proteaceae

Proteaceae

Poaceae

Proteaceae

Proteaceae

Proteaceae

EuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceae

.

,

167

185

107

71

102

81

69

65

67

70

72

73

80

97208

20

96

50

10197

170

149

136

129

128

104

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69

86

22

72

83

143

124

I 31

134

135167

146164

165

122184

123

,

653778

655920

711530

601640

706390

635790

586980

623060

621740

588330

60/780

616030640590

,

82788908328270

8339790

8320980

8321720

8317210

8342020

8315830

83/1040

8339/20

8321/2083124708314600

.

,

680000

671200

677020

677020

655220655780

649567

670230

659320

619350

625720

707400

707640

703010

586980

609860

659430

601780

620290

664170

6/4/50

622840

646080

646280653778

667400653358

655810

612880654270

6/2/30

8307400

8304/408299900

8299900829486082927608280819

8332420

833697083524108360040

83330008332860

8318/80

8342020

8339700

8290940

8321/20

8324640

83498808332000

8324290

832801083280iO8278890

83482008272845

8274414

83274608325580

8331310

,

Page 116: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

PetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadriiocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePetalOStigma quadrilocularePhragmites karkaPhyl!arithus grandisepalusPhyllanthus sp.Phyllanthus sp.Phyllanthus spPhyllanthus sp.Pityrodia lainesiiPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careya

Planchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careya

EuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaePoaceae

EuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeVerbenaceae

LecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecyihidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecylhidaceaeLecy!hidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecylhidaceae

163

11 7

11 5

3

31

67

71

79

80

92

100

102

103

I04

107

142

70

57

58

48

34

90

11 8

122

129

125

127

103

128

124

145

143

148158

160

163

I 71

200

203

11 7

86

102

80

95

652393

615050

615230

654820

643480

621740

601640

64/370

640590

610550

703040

706390

706680

707400

711530

640000

588330

648550

647500

680750

643720

605890

615460

612880

619350

614350

619700

706680

625720

6/4/50

667400

664170

670260662193

675660

652393

647906

651400

667550

615050

609860

706390

640590

677490

8280/50

8321810

8322020

8340/20

8305350

8311 040

8320980

8317080

8314600

8335330

8318590

8321720

8322000

8333000

8339790

8353590

8339/20

8295260

8295330

8333930

8297970

8354080

8321630

8327460

8352410

8332060

8345300

8322000

8360040

8332000

8348200

8349880

83235308303/74

8303520

8280/50

8284769

8282/60

8316970

8321810

8339700

8321720

8314600

8299950

.

^

,

.

,

Page 117: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

t

.

,

., Species 1997

Planchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careya

Planchonia careyaPlanchonia careya

Planchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPlanchonia careyaPiechtrachne pungensPIectrachne bynoeiPIectrachne bynoeiPiectrachne pungensPIectrachne pungensPIectrachne pungensPIectrachne pungensPiectrachne pungensPIectrachne pungensPleatrachne pungensPiectrachne pungensPiectrachne pungensPIectrachne pungensPIectrachne pungensPIectrachne pungensPledrachne pungensPiectrachne pungensPIectrachne pungensPIectrachne pungensPleatrachne pungensPIectrachne pungensPIectrachne pungensPiectrachne pungensPIectrachne pungensPleatrachne pungensPIectrachne pungensPiectrachne pungensPleatrachne pungensPledrachne pungensPiectrachne pungens

.

LecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecyihidaceaeLecythidaceaeLecythidaceaeLecythidaceaeLecythidaceaePoaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

,

.

16

22

26

40

40

73

23

83

83

85

88

89

95

93

94

63

90

18

143I 61

154

146

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135

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164

165

189

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190

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166

184

183

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618432

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646280

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622840651520

651400

653358

655810

686700

651400

693500

614350655920

654841

654270

8303900

8290940

8305/408341220

8341220

8312470

8290940

8324640

8324640

8324350

83546708354680

82999508326080

8326260

8315860

8354080

8305400

83498808305770

8304390

8348200

83369708280/50

83280tO

83280iO

83242908282082

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8272845

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8304600

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8304000

83320608328270

8278410

8325580

,

*

,

653778

625720

659430

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621440

8278890

8360040

8290940

8332000

8321810

8312480

Page 118: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Pledrachne pungensPIectrachne pungensPIectrachne pungensPIectrachne pungensPIectrachne pungens

Piectrachne pungensPIectrachne pungensPiectrachne pungensPiectrachne pungensPIectrachne pungensPiectrachne pungensPIectrachne pungensPiectrachne pungensPiectrachne pungensPIectrachne pungensPiectrachne pungensPiectrachne pungensPiectrachne pungensPiectrachne pungensPiectrachne pungensPiectrachne pungensPiectrachne pungens.PIlycarpeae corymbosaPoaceae sp.Poaceae sp

Poaceae spPoaceae sp.Poaceae sp.Poaceae sp.Poaceae sp.Poaceae sp.

Poaceae sp.Poaceae sp.

Poaceae sp.Polycarpaea brevifloraPolycarpaea corymbosaPolycarpaea corymbosaPolycarpaea sp.Polycarpaea sp.Polycarpea longifloraPolycarpeae brevifloraPolycarpeae brevifloraPolycarpeae brevifloraPolycarpeae corymbosaPolycarpeae sp.

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Caryophyl!aceaeCaryophyllaceaeCaryophyllaceaeCaryophyllaceaeCaryophyllaceaeCaryophyllaceaeCaryophyllaceaeCaryophyllaceaeCaryophyllaceaeCaryophyllaceaeCaryophyllaceae

69

67

62

31

71

23

19

18

70

72

11 5

92

107

102

100

86

73

80

79

78

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67

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98

98

129152

153

35

11 7

11 9

108

83

54

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145184

23

69

27

62

67

103

135

586980

621740

62/550

643480

601640

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686580

588330

601780

615230

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703040

609860

616030

640590

641370

641750

653000

654820

621740

680730

678480

678480

6193505206/8

83420208311 040

8312/30

8305350

8320980

829094083057008305400

8339/20

8321/2083220208335330

8339790

8321720

8318590

8339700831247083146008317080

831703

8280610

8340/20

83/1040

8333650

8301930

8301930

83524108304631

^

.

,

.

645880

615050

617830

700940

620290

655510

622840

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586980

656430

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621740

706680

646280

8294600

8321810

8323200

8346780

8324640

8298810

8324290

83482008325580

82909408342020

8306710

8312/3083/1040

8322000

8328010

,

.

I

Page 119: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

t

Species 1997

,

Polygala eriocephalaPolygala jinarifoliaPolymeria ambiguaPolymeria ambiguaPolymeria ambiguaPolymerIa ambiguaPolymeria ambiguaPolymeria ambiguaPolymeria ambiguaPolymeria ambiguaPouteria sericeaPremna acuminata

Premna acuminata

Pseudopoganotherum contortumPseudopoganotherum contortumPseudopoganotherum contortumPseudopoganotherum contortumPseudopoganotherum contortumPseudopoganotherum contortumPseudopoganotherum contortumPseudopoganotherum contortumPseudopoganotherum contortumPseudopoganotherum contortumPseudopoganotherum contortumPseudopoganotherum contortumPseudopoganotherum contortumPseudoraphis spinescensPterocaulon serrulatumPtilotus conicus

Ptilotus spicatusPtilotus spicatusPtilotus spicatusPtilotus spicatusPtilotus spicatusPtilotus spicatusPtilotus spicatusPtilotus spicatusRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exserta

,

PolygalaceaePolygalaceaeConvolvulaceae

Convolvulaceae

Convolvulaceae

Convolvulaceae

Convolvulaceae

Convolvulaceae

Convolvulaceae

Convolvulaceae

SapotaceaeVerbenaceae

Verbenaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Asteraceae

Amaranthaceae

Amaranthaceae

Amaranthaceae

Amaranthaceae

Amaranthaceae

Amaranthaceae

Amaranthaceae

Amaranthaceae

Amaranthaceae

CyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceae

I

73

74

8

30

17

58

59

28

26

25

90

140

40

55

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133

129

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703010

670230

677600

681500

682560

665760

684490

685920

684750675660

676700

671200

684750

695190

708530

647500

69/020

684490

654820

692090

612880

614520

615230

615050

8312470

8312690

8291390

8307/80

8305/20

8295330

8302530

8306860

8305/40

8302440

8354080

8342970

8341220

8299590

8327760

8323200

8347100

831 8180

8332420

8326750

8335290

8337630

8308880

8341220

8343550

83416708303520

8303900

8304/40

8341670

8346850

8340/20

8295330

8347480

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8340/20

8347970

8327760

8316370

8322020

8321810

I

I

,

,

.

,

646100

619350

8305820

8352410

Page 120: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Rhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora exsertaRhynchospora sp.Salsola kali

Sauropis sp.Sauropsis sp.Sauropsis spSauropsis sp.Scaevola revoluta

Schizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragile

CyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeChenopodiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeEuphorbiaceaeGoodeniaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

132

136

149

I 51

I I O

I I I

11 9

109

108

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I 01

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96

6157

32

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43

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102

103

105

109

11 5

11 9

125

124

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I 31

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I 41

146

I 01

646620

659320

670230

688590

695190

683000

617830

701180

700940

677600

668040

692090

689540

681500

647400

616030

703010

616210707640

708530

677020

649830672900

635340

664170

692090

683300

685920

588330

706390

706680707640

701180

615230

617830

614350

6/4/50

703040

622840

646100

659320

647570

667400

703010

8305320

8336970

8332420

8346450

8346850

8347100

8323200

8347/60

8346780

8326750

8303400

8347970

8345950

83352908302530

8312470

8318/80

83126908332860

8340/20

8299900

82844308304000

8301290

8349880

8347970

8338940

8343550

8339/20

8321720

83220008332860

8347/60

8322020

8323200

8332060

8332000

8318590

8324290

8305820

8336970

8342920

8348200

8318/80

^

^

,

,

.

,

:

:

Page 121: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

r

* Species I 997

^

Schizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium fragileSchizachyrium sp.Schleria pygmaeaSchleria pygmaeaScleria sp.SGIeria sp.Scleria tricuspidataScleria tricuspidataScleria tricuspidataScleria tricuspidataScleria tricuspidataSGIeria tricuspidataScleria tricuspidataScleria tricuspidataScleria tricuspidataSebastiana chainaeleaSebastiana chainaelea

Sedge spp.Sedge sp.Sedge sp.Sedge sp.Sedge sp.Sedge sp.SedgesSehima nervosa

Sehima nervosa

Sehima nervosa

Sehima nervosa

Sehima nervosa

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

CyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeEuphorbiaceaeEuphorbiaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaeCyperaceaePoaceae

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Poaceae

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Poaceae

,

33

96

79

50

4

16

20

21

31

54

53

78

60

61

62

69

72154

35

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138154

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11 7

87

47

51

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10

8

144

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78173

178

181

79

57

34180

207

203

202

199

193

,

641750

677020

641370

680380

653000

676700

67/200

664942

643480

655510654970

64/750

641220

621440

621550

586980

601780618432

645880

645880

658680618432

617830

615050

609560

681500

677600

682560

655220

652890

667400

602280

641750649752

651650

653260

641370

648550

643720652721

687740

667550

648000

648640651620

8302740

8299900

8317080

8332950

8280610

83039008304/40

8296605

83053508298810

8299950

831703

8304770

8312480

8312/30

8342020

8321/208304390

8294600

8294600

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8323200

832181083397008335290

8326750

8337630

8294860

8291390

8347820

8354670

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8285057

8294327

8317080

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83160308316970

830080082864408303400

.

I

.

I

Page 122: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Sehima nervosa

Sehima nervosa

Sehima nervosa

Sehima nervosa

Sehima nervosa

Sehima nervosa

Sehima nervosa

Sehima nervosa

Sehima nervosa

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosumSehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

I 91

177

188

77

29

17

15

13

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106

109

108

94

100

99

I I 3

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145

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42

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672500

647339

673870

645780

656320

680250

674120

661390

654370

708530

701180

700940

605680

703040

68/060

614620

605700

695190

647400

6/2/30

688590

645940647853

667400

683990

625720

647570

646620

602280

681500

645530

647400

684490

683550

653050

655770

658060

665760

682560

683300

692391

685920

654380

692090

8306500

8289727

8322360

8303800

8307470

8305/20

8304550

8302470

8307/80

8340/20

8347/60

8346780

8326260

8318590

8305350

8316/40

8326080

8346850

8342970

8331310

8346450

83038508277781

8348200

8338/30

8360040

8342920

8305320

8354670

8335290

8303930

8302530

8341220

8305700

8302440

8305/40

8305720

8308880

8337630

8338940

8350483

8343550

8299590

8347970

I

I

^

Page 123: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Sehima nervosum

Senna Occidentalis*

Senna o1igocladaSesbania carinabina

Setaria apiculataSetaria apiculataSetaria apiculataSetaria apiculataSetaria apiculataSetaria apiculataSetaria apiculataSetaria apiculataSetaria apiculataSIda acuta*

Sida cordifolja*Sida cordifolja*

SIda cordifolja*Sida rhombifoija*Solanum IucaniSolanum Iucani

Sorghum australienseSorghum australienseSorghum australienseSorghum australienseSorghum australienseSorghum australienseSorghum intransSorghum intransSorghum intransSorghum intransSorghum intransSorghum intransSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosum

I

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

CaesalpiniaceaeCaesalpiniaceaeFabaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Malvaceae

Malvaceae

Malvaceae

Malvaceae

Maivaceae

Solanaceae

Solanaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

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Poaceae

Poaceae

Poaceae

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.

;

44

46

9

48

49

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95153

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148

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187

186

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684750

653330

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677600

676700

656440

659630

591780

677490

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:

.

;

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676680

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615050

610550

647400

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683990

667400

647570

,

8345300

8336970

8354670

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8312/30

8312480

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8301290

8272820

8272750

8272750

8272820

8301290

8342020

8323530

8290940

8333930

8338940

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8326590

8326590

8303/74

8321810

8335330

8342970

8346450

8338/30

8348200

8342920.

^

.

Page 124: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Sorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosum

Poaceae

Poaceae

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Poaceae

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Poaceae

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Poaceae

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Poaceae

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Poaceae

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Poaceae

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I32

129

128

127I64

11 9

I I 3163

I69

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186

196

195

194

193

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183

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166

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655810

676680

651550

651550

654900

651620

649590

8305320

8352410

8360040

83453008272845

8323200

8316/408280/50

8277781

8274414

8326590

8295680

8295680829900083034008312060

655920

654841

653260

651650

649567

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700940651520

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677490

656320

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659630

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655220

653330

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605700

680750

653000677600

83282708278410

8294327

8285057

8280819

83220008278890

83467808282082

8318/80

8299950

8307470

8347970

8341 220

8338940

8337630

8305350

8290940

8305/40

83336508290940

8294860

8294530

8284430

8326080

8333930

82806108326750

.

Page 125: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

I

Species 1997

.

Sorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum plumosumSorghum sp.Sorghum sp.sorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideum

.

.

.

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

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Poaceae

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Poaceae

Poaceae

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Poaceae

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Poaceae

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Poaceae

Poaceae

Poaceae

Poaceae

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Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

.

77

88

85

83

81

79

76

61

75

74

72

65

64

89

57159

154

125

135

134

I 31

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143

11 5

I I 6

124

123

122

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145200

I I O207

207

204

201

189

146I 61

154

I 51

149

148

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645780

602280

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620290

635790

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645940

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601780

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623100602410

648550665577

618432

614350

646280

646080

622840

619350

664170

615230

615200

6/4/50

6/2/30

612880

612880

659320693500

667400651400

695190687740

687740

667350

651400

686700

667400683190

618432

688590

670230

670260

614520

8303800

8354670

8324350

8324640

8317210

8317080

8303850

8312480

8303930

8312690

8321/20

8315830

83158708354680

82952608303/27

8304390

8332060

8328010

8328010

8324290

8352410

8349880

8322020

8321650

8332000

8331310

8327460

8327760

83369708304000

83482008282/60

83468508316030

8316030

8316970

8282/60

8304600

83482008305770

8304390

8346450

8332420

8323530

8316370

.

^

I

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Species 1997

Sorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSorghum stipoideumSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculata

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

86

107

20

42

31

29

22

106

19

50

15

14

5

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17

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60

94

62

104

100

97

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677600

641220

605680

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83397008339790

8304/408350483

8305350

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83057008332950

8304550

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8345950

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8321810

8320980

8332000

8342920

8346450

8348200

,

,

,

:

I

,

. -

Page 127: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

:

.

I

:

Species 1997

7 Spermacoce auriculataSpermacoce auriculataSpermacoce auricu!ataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auricu!ataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce auriculataSpermacoce brevifloraSpermacoce exsertaSpermacoce exsertaSpermacoce sp.Spermacoce sp.Sporobolus australasicaSporobolus australasicaSporobolus australasicusSporobolus australasicusSporobolus australasicusSporobolus australasicusSporobolus australasicusSporobolus australasicusSporobolus pulchellusSporobolus pulchellusStackhousia intermedia

I

I

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

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Poaceae

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Poaceae

Stackhousiaceae

.

I 31

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129

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8347100

Page 128: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Stackhousia intermedia

Stackhousia intermedia

Stackhousia intermediaStackhousia intermedia

Stackhousia intermedia

Stackhousia intermedia

Stackhousia intermedia

Stackhousia intermedia

Stackhousia intermedia

Stackhousia intermedia

Stackhousia intermedia

Stackhousia intermediaStackhousia intermedia

Stackhousia intermediaStackhousia intermedia

Sternodia IythrifoliaStemodia IyihrifoliaSternodia tephropelinaSternodia tephropelinaSternodia tephropelinaStenocarpus cunning hamiiStenocarpus cunning hamiiStenocarpus cunning hamiiSterculia quadrifidaStreptoglossa odoraStreptoglossa odoraStrychnos lucidaStrychnos lucidaStrychnos lucidaStrychnos lucidaStrychnos lucidaStylidium multiscapumStylidium mumscapumStylidium multiscapumStylidium multiscapumStylidium multiscapumStylidium multiscapumStylidium schizanthumStylidium schizanthumStylidium schizanthumStylidium sp.Stylidium sp.Stylidium sp.Sysygium nervosum

Stackhousiaceae

Stackhousiaceae

Stackhousiaceae

Stackhousiaceae

Stackhousiaceae

Stackhousiaceae

Stackhousiaceae

Stackhousiaceae

Stackhousiaceae

Stackhousiaceae

Stackhousiaceae

Stackhousiaceae

Stackhousiaceae

Stackhousiaceae

Stackhousiaceae

Goodeniaceae

Asteraceae

Goodeniaceae

Goodeniaceae

Goodeniaceae

Proteaceae

Proteaceae

Proteaceae

Sterculiaceae

Asteraceae

Asteraceae

LoganiaceaeLoganiaceaeLoganiaceaeLoganiaceaeLoganiaceaeStylidiaceaeStylidiaceaeStylidiaceaeStylidiaceaeStylidiaceaeStylidiaceaeStylidiaceaeStylidiaceaeStylidiaceaeStylidiaceaeStylidiaceaeMynaceaeMynaceae

96

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I 31

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120

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609860

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,

.

.

I

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^

I

I

Page 129: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

I

Species 1997

,

,

Syzygium forteSyzygium sp.Syzyigium nervosumTacca IeontopetaioidesTephrosia coriaceaTephrosia coriaceaTephrosia coriaceaTephrosia filipesTephrosia filipesTephrosia filipesTephrosia flammeaTephrosia IeptocladaTephrosia reinotifloraTephrosia sp.Terminalia arostrataTerminalia arostrata

TerminalIa arostrata

TerminalIa arostrata

TerminalIa arostrata

Terminalia arostrata

TerminalIa arostrata

Terminalia arostrata

Terminalia arostrata

TerminalIa arostrata

Terminalia arostrata

Terminalia bursarina

TerminalIa bursarina

Terminalia canes Gens

TerminalIa canescens

Terminalia canescens

TerminalIa canescens

TerminalIa canescensTerminalia canescens

Terminalia canescens

Terminalia canescensTerminalia canescens

Terminalia canescens

Terminalia canescensTerminalia canescens

Terminalia canescens

Terminalia canescens

Terminalia canescens

Terminalia canescens

Terminalia canescens

Terminalia canescens

.

.

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.

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Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

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Combretaceae

Combretaceae

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Combretaceae

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Combretaceae

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Combretaceae

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Combretaceae

Combretaceae

Combretaceae

e

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8350483

8345950

8307470

Page 130: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Terminalia canescens

Terminalia canescens

Terminalia canescens

TerminalIa canescens

Terminalia canescens

Terminalia canescens

Terminalia canescens

Terminalia canescens

Terminalia canescens

Terminalia canescens

TerminalIa carpentariaeTerminalia carpentariaeTerminalia grandifloraTerminalia grandifloraTerminalIa grandifloraTerminalia grandifloraTerminalIa grandifloraTerminalIa grandifloraTerminalia grandifloraTerminalia grandifloraTerminalia grandifloraTerminalIa grandifloraTerminalia latipesTerminalIa latipesTerminalia latipesTerminalia latipesTerminalia latipesTerminalia latipesTerminalia latipesTerminalIa latipesTerminalia latipesTerminalia latipesTerminalia latipesTerminalia platyphyllaTerminalia platyphyllaTerminalia platyphyllaTerminalia platyphyllaTerminalIa platyphyllaTerminalia platyphyllaTerminalia platyphyllaTerminalia platyphyllaTerminalia platyphyllaTerminalIa platyphyllaTerminalia platyphyllaTerminalia platyphylla

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

31

31

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60

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I 01

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140

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:

Page 131: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

,

Species 1997

TerminalIa platyphyllaTerminalia platyphyllaTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalIa platypteraTerminalIa platypteraTerminalIa platypteraTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalIa platypteraTerminalia platypteraTerminalia platypteraTerminalIa platypteraTerminalia platypteraTerminalIa platypteraTerminalia platypteraTerminalia platypteraTerminalIa platypteraTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalia platypteraTerminalIa platypteraTerminalia platypteraTerminalIa platypteraTerminalia platypteraTerminalia platypteraTerminalIa platypteraTerminalIa playtphyllaTerminalIa play!pteraTerminalia sericeum

Terminalia sericocarpaTerminalia sericocarpaTerminalia sp.

I,

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,

,

I

Page 132: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Terminalia sp.TerminalIa sp.Terminalia volucris

Terminalia volucris

Terminalia volucrisTerminalia volucris

Terminalia volucrisTerminalia volucris

TerminalIa volucris

TerminalIa volucris

Terminalia volucrisTerminalia volucris

Terminalia volucris

Terminalia volucris

Terminalia volucris

Terminalia volucris

TerminalIa volucris

TerminalIa volucris

Terminalia volucris

Terminalia volucris

Terminalia volucris

Terminalia volucris

Thecanthes sanguineaThecanthes sanguineaThecanthes sanguineaThecanthes sanguineaThecanthes sanguineaThecanthes sanguineaThecanthes sanguineaThemeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandraThemeda triandra

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

Combretaceae

ThymelaeaceaeThymelaeaceaeThymelaeaceaeThymelaeaceaeThymelaeaceaeThymelaeaceaeThymelaeaceaePoaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

166

167

59

57

58199

109188

208

50

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186

46

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32

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I I I

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643720

645880

641750

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700940

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685920

658060

649830

683000

619350

6/2/30

612880

8278410

8278890

8302530

8295260

82953308286440

8347/608322360

8307400

8332950

82988108326590

8341670

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8272820

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8341220

8301290

8297970

8294600

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.

I

:

:

Page 133: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

I

Species 1997

Themeda triandra

Themeda triandraThemeda triandra

Themeda triandraThemeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandraThemeda triandra

Themeda triandra

Themeda triandra

Themeda triandraThemeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandraThemeda triandra

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Themeda triandra

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Themeda triandra

Themeda triandra

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,

Poaceae

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136

139174

108206

203

I 91

187

160

169

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148

147

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,

Page 134: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Species 1997

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandra

Themeda triandraTimonius timon

Timonius timon

Timonius timonTimonus timon

Trianthema rhynchocalypteraTrichodesma zeylanicumTrichodesma zeylanicumTriumfetta sp.Uraria 015707 Litchfield (3RC-)Uraria lagopodioidesVentilago viminalisVentilago viminalisVeincordia verticillataVetiveria paucifloraVetiveria paucifloraVetiveria paucifloraVetiveria paucifloraVigna lanceolataVigna lanceolataVigna vexillataVigna vexillataVitex glabrataWaitheria indicaWaltheria indicaWaitheria indica

Waltheria indicaWaltheria indica

Waitheria indicaWaltheria indicaWaltheria indicaWaitheria indica

Waltheria indica

Whiteochloa capillipesWhiteochloa capillipesWhiteochloa capillipesWhiteochloa capillipesWhiteochloa capillipes

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

Rubiaceae

Rubiaceae

Rubiaceae

Rubiaceae

PolygalaceaeBoraginaceaeBoraginaceaeTiliaceae

Fabaceae

Fabaceae

Rhamnaceae

Rhamnaceae

MynaceaePoaceae

Poaceae

Poaceae

Poaceae

Fabaceae

Fabaceae

Fabaceae

Fabaceae

Verbenaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Sterculiaceae

Poaceae

Poaceae

Poaceae

Poaceae

Poaceae

96

75

74

65

64

60

55

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8318590

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.

I

Page 135: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

I,

,

Species 1997

I

Whiteochloa capillipesWhiteochloa capi!lipesWrightia salignaWrightia salignaWrightia salignaWrightia salignaWrightia salignaWrightia sailgnaWrightia sailgnaWrightia salignaXanthium spinosum*Xanthium spinosum*Xanthostemon paradoxusXerochloa jinberbisXerochloa jinberbis

Xerochloa Ianiflora

Xyris coinplanataXyris indicaXyris indicaXyris indicaXyris indicaYakirra majuscalaYakirra majuscalaZanthoxylum parviflorumZornia areolata

Zornia prostrata

*

^

,

.

Poaceae

Poaceae

ApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeApocynaceaeAsteraceae

Asteraceae

MynaceaePoaceae

Poaceae

Poaceae

XyridaceaeXyridaceaeXyridaceaeXyridaceaeXyridaceaePoaceae

Poaceae

Rutaceae

Fabaceae

Fabaceae

,

23

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100

129

103

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89

69

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.

Page 136: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare
Page 137: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

,

.

,

.

Appendix 8

Impact Ranking on Vegetation Units

.

I

.

^

,

;

.

:

COMMERCIAL-IN-CONFIDENCE

Prepared for: Connell WagnerPrepared by: ERA Environmental Services Pty Ltd

SepV97Job NO XI32

Page 138: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Appendix 8 Ranking of impact of military activities on mapping units.

Habitat and mapping unit

Monsoon forest

I mixed S ecies I

Ri arian Forest, O en-Forest2 Ri arian - Me Ialeuca Ieucadendra I

3 Riparian - Eucalyptus microtheca, TerminaliaIat tera'

4 Riparian - Eucalyptus camauldulensis, E.microtheca I

Co inbialEucal to en-Forest, Woodland5 Eucalyptus miniata, E. tetrodonta over annual anderennia! rasses 1.2

6 Eucalyptus miniata (E. tetrodonta, C. bleeseri, Cdichromo hloia over hummock rasses 1-27 EUCal tustetrodontaover erennial rasses '8 Cor inbia bleeseri over hummock rasses 1-2

9 Gorymbia bleeseri(E. tetrodonta, E. miniata) overannual and hummock rasses 1.2

10 Eucalyptus tectifica over annual and perennialrasses

11 EUCal tus techfica over hummock rasses '

HEl

12 Eucalyptus phoenicea over hummock grassannual rasses 1.2

13 Eucalyptus phoenicea, C. dichromophloia overhummock rasses I

Hi h

Field

finn

14 Gorymbia Iatifoiia over annual and perennialrasses and sed es

Hi h

High

15 Cor inbia Iatifolia over hummock rasses I

Hi h

16Eucal tus ruinosaover erennial rasses

High

17 EUCal

Dismounted

Hi h

18Co inbia o1 car a+'

High

I 9 Eucalyptus alba, C. grandifolia over perennial

High

rasses

High

20 Eucalyptus microtheca (Excoecaria parvifolia) overerennial rasses

Hi h

tus tintinnans over hummock rasses 1-2

High

21 EUCal

Hi h

Medium

Marieouvre

22 EUCal

High

High

Hi h

High

High

High

.

LowoPEN FOREST, WOODLAND

Hi h

tus microtheca over

23 Me Iaieuca viridiflora over Eleocharis I

Medium

Medium

tus microtheca over bare round

24 Me!aleuca viridiflora over erennial

Hi h

Hi h

Medium

25 Me Ialecua minutifolia, M. sericeum over annualand erennial rasses3

Hi h

High

High

High

Medium

26 Excoecaria parvifolia (Terminalia volucris) overerennial rasses

Low

High

High

Low

27L si h

Hi h

Medium

28 TerminalIa canescens, Erythrophleumchiorostach s over annual rasses

Medium

High

High

Medium

erennial rasses

Medium

High

High

Low

CORYMBIAIEUCALYPTOPEN-WOODLAND

Medium

Ium cunnin hamiiover erennial rasses

.

Medium

29 Cor inbia Iatifolia over hummock rasses

Low

Medium

Medium

Hi h

30 Cor inbia Iatifolia over

Hi h

Medium

Medium

31 Eucalyptus papuana, C. polycarpa, E. bigaleritaover erennial rasses

Low

High

Low

Medium

Medium

32Eucal tusmicrothecaover erennial rasses

Low

Medium

rasses

33 Eucalyptus tentifica over annual and perennial

Hi h

Low

Medium

Low

Hi h

rasses

Medium

High

Low

Low

Low

High

Low

Hi h

Low

Medium

Prepared for: Connell WagnerPrepared by: ERA Environmental Services Pty Ltd.

Medium

Low

Medium

Low

erennial

High

Medium

Low

Medium

Medium

Hi h

rasses

Medium

Low

Medium

Medium

Hi h

Low

High

Medium

Medium

Medium

Medium

Hi h

Medium

Low

Medium

Medium

Medium

Low

Hi h

Low

Low

Low

COMMERCIAL-IN-CONFIDENCE

Medium

Hi h

Low

Low

Low

Hi h

Low

Low

High

Low

High

MediumLow

Low

Hi h

Low

High

Low

Low

Low

Medium

Low

Low

Medium

Low

Sept197Job NO XI32

Page 139: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

*

:

I

OTHER OPEN-WOODLAND

34 L si h 11um Gunnin hamiiover erennial rasses35 Terminalis bursarina over annual rasses36 Acacia validaover erennial rasses

37 MeIaleuca minutifolia, M. sericea over bare round38 Terminalia arostrata, T. volucris over perennial

rasses

39 Terminalia arsotrata, Eucalyptus species, overerennial rasses

40 Mixed over hummock rasses

.

SHRUBLAND

41 Acacia over hummock rasses 1-2

GRASSLAND

42 Chrysopogon fallax, Sehima nervosa, SorghumIumosum, Themeda triandra

43 Xeroch!oa jinberbis, Eleocharjs3

.

44 Sorghum stipiodeum, Eriachne species, Aristidas ecies

45 PIectrachne b noeji. 2

,

I

46 Sed eland

Low

Low

Low

*

Medium

Low

Low

The ranking takes into account the conservation status of the vegetation and the resilience ofvegetation to disturbance from military exercises and associated activities. Important assumptions ofthe ranking are that:

areas are monitored and rested when appropriate so that vegetation can recover beforefurther disturbance;

exercises are conducted during the dry season. None of these areas are suitable for activityduring the wet season, except for bare sandstone areas. However, the problem of accesswould need to be addressed;

Low

Low

Low

Medium

Low

Low

Low

.

Low

Low

Hi h

Low

Low

Low

.

Low

Low

^

Low

Low

Hi h

Hi h

Low

Low

Low

Low

.

Hi h

Low

Hi h

Low

Low

Hi h

Low

fire control strategies have been effective Iy implemented

Low

Low

Low

Hi h

Low

Low

Low

Hi

Low

h

Medium

Low

Low

I

Hi h

Low

Hi h

Low

^

COMMERCIAL-IN-CONFIDENCE

Prepared for: ConnellWagnerPrepared by: ERA Environmental Services Pty Ltd

15/09/97Job NO XI32

Page 140: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

.

Page 141: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

LygodiumLygodiumLygodiumLygodiumLygodiumLygodiumLysianaLysianaLysianaLysianaMallotus

Malvastrum

Marsdenia

Marsdenia

Marsdenia

Marsdenia

Marsdenia

Marsdenia

Marsilea

MaytenusMaytenusMaytenusMe Ialeuca

Me Ialeuca

Me Ialeuca

Me Ialeuca

Me Ialeuca

Me Iaieuca

Me Ialeuca

Me Iaieuca

Me Ialeuca

Me Ialeuca

Me Ialeuca

Me Ialeuca

Me Ialeuca

Me Ialeuca

Me Ialeuca

Me Iaieuca

Me Iaieuca

Me Ialeuca

Melastoma

Melastoma

Me Ihania

Me Ihania

Me IicopeMe IicopeMelochia

Melochia

MemecylonMemecylonMemecylonMemecylonMemecylonMemecylonMemecylonMemecylonMerremia

Merremia

Merremia

.

microphyllummicrophyllummicrophyllummicrophyllummicrophyl!urnmicrophyllumspathulataspathulataspathulatasubfalcata

nesophilusamericanum

glandulifera (3r)hemipterahemipterahemipteraviridiflora

viridiflora

inutica

ferdinandi

ferdinandi

SCHIZAEACEAE

SCHIZAEACEAE

SCHIZAEACEAESCHIZAEACEAE

SCHIZAEACEAE

SCHIZAEACEAE

LORANTHACEAE

LORANTHACEAE

LORANTHACEAE

LORANTHACEAE

EUPHORBIACEAE

MALVACEAE

AsCLEPiADACEAEAscLEPiADACEAE

AsCLEPiADACEAE

AscLEPiADACEAE

AscLEPiADACEAE

AscLEPiADACEAE

MARSILEACEAE

CELASTRACEAE

CELASTRACEAE

CELASTRACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MELASTOMATACEAE

MELASTOMATACEAE

STERCULIACEAE

STERCULIACEAE

1205/994

1205/994

3031989

1205/994

1303/989

1505/994

1405/994

1305/994

1805/952

2408/987

9031989

1603/989

2031989

4031989

3031989

1303/989

2702/986

1103/989

1005/959

1101855

1505/994

1103/989

4031989

2002/994

9051995

2602/986

5101982

1605/994

1005/994

1205/994

1407/977

1407/977

1405/994

1205/994

1205/994

1605/994

2511/987

1605/994

1205/994

2511/987

2806/986

2408/987

1403/989

1305/994

1405/994

1603/989

1305/994

1407/977

1205/994

1405/994

9031989

1405/994

1605/994

2031989

2302/994

2031989

1205/994

1405/994

9051989

acacioides

acacioides

acacioides

argenteadealbata

Ieucadendra

Ieucadendra

Ieucadendra

Ieucadendra

Ieucadendra

minutifolia

minutifolia

nervosa

sericea

stenostachyaviridiflora

viridiflora

viridiflora

affine

affine

oblongifoliaoblongifoliaelleryanaelleryanaA55270

pyramidatapauciflorumpauciflorumpauciflorumpauciflorumpauciflorumpauciflorumpauciflorumpauciflorumquinataquinata

,

1445/2

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14352i

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15/400

153000

144100

1505/5

15/400

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143100

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14/900

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152800

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15/300

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144000

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150345

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1304759

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1302830

1300/05

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1300100

13/0100

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1302000

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13/0800

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1300600

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1301000

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1300000

STERCULIACEAE

STERCULIACEAE

MELASTOMATACEAE

MELASTOMATACEAE

MELASTOMATACEAE

MELASTOMATACEAE

MELASTOMATACEAE

MELASTOMATACEAE

MELASTOMATACEAE

MELASTOMATACEAE

CONGOLVULACEAE

CONGOLVULACEAE

CONGOLVULACEAE

Page 142: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

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Page 143: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

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campestriscampestriscampestriscampestriscampestriscampestrisarida (3RC)arida (3RC)arida (3RC)auriculataauriculataauriculataauriculatahirsutula

monospermaaragoanaaragoanaholochila

Page 144: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Nervilia

Nesaea

Nesaea

Nesaea

Nitella

Notelaea

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Oldenlandia

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holochila

am hemica

am hemica

inuelleri

microcarpahastifolia

macrosperma

macrospermaviolacea

violacea

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aurantiaca

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crenata

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LYRTHRACEAE

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OLEACEAE

NYMPHAEACEAE

NYMPHAEACEAE

NYMPHAEACEAE

NYMPHAEACEAE

NYMPHAEACEAE

NYMPHAEACEAE

NYMPHAEACEAE

NYMPHAEACEAE

MENYANTHACEAE

MENYANTHACEAE

MENYANTHACEAE

MENYANTHACEAE

MENYANTHACEAE

MENYANTHACEAE

MENYANTHACEAE

MENYANTHACEAE

MENYANTHACEAE

MENYANTHACEAE

OLACACEAE

OLACACEAE

OLACACEAE

OLACACEAE

RUBIACEAE

RUB!ACEAE

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RUBIACEAE

RUBIACEAE

RUBIACEAE

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RUBIACEAE

RUBIACEAE

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novo-guineensis

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exaltatus

exaltatus

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MELASTOMATACEAE

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Page 145: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

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POACEAE

ROACEAE

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POACEAE

POACEAE

ROACEAE

POACEAE

POACEAE

ROACEAE

POACEAE

POACEAE

POACEAE

HEMION!TIDACEAE

HEMIONITIDACEAE

HEMIONITIDACEAE

HEMIONITIDACEAE

HEMIONITIDACEAE

HEMIONITIDACEAE

HEMIONITIDACEAE

CAESALPINIACEAE

APOCYNACEAE

APOCYNACEAE

APOCYNACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

PASSIFLORACEAE

RUBIACEAE

POACEAE

POACEAE

POLYGONACEAE

PROTEACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

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2602/986

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reynoldsiireynoldsiireynoldsiireynoldsiireynoldsiireynoldsiireynoldsiiaculeata *

velutina

velutina

velutina

rarum

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longifoliumscrobiculatum

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scrobiculatum

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foetida *

brownii

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falcata

banksii

pubescenspubescensquadrilocularequadrilocularequadrilocularequadriloculare

Page 146: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Phaius

Pheidochloa

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minutiflorus

reticulatus

urinaria

ORCHIDACEAE

POACEAE

PHILYDRACEAE

PHILYDRACEAE

PHILYDRACEAE

PHILYDRACEAE

ROACEAE

EUPHORBIACEAE

EUPHORBIACEAEEUPHORBIACEAE

EUPHORBIACEAEEUPHORBIACEAE

EUPHORBIACEAE

EUPHORBIACEAEEUPHORBIACEAE

EUPHORBIACEAE

EUPHORBIACEAE

EUPHORBIACEAE

EUPHORBIACEAE

EUPHORBIACEAE

EUPHORBIACEAEEUPHORBIACEAE

SOLANACEAE

PIPERACEAE

PIPERACEAE

PIPERACEAE

PITTOSPORACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

SAPOTACEAESAPOTACEAEPOACEAE

ROACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAEPOACEAEPOACEAE

PLUMBAGINACEAEPLUMBAGINACEAELAMIACEAE

ANNONACEAE

ANNONACEAEANNONACEAEANNONACEAE

ANNONACEAECARYOPHYLLACEAE

1207/992

1405/994

1405/994

1405/994

1605/994

1605/994

1207/992

1005/994

1205/994

2202/994

1103/989

1303/989

2031989

2702/986

o

1405/994

1505/994

1605/994

1207/992

1405/994

2202/994

1505/994

1108/949

1207/992

4031989

1603/989

1205/994

2402/994

1405/994

1005/994

51897

2308/987

1405/994

1505/994

1205/994

1605/994

9051989

1005/994

1005/994

2308/987

1105/983

9031989

2308/987

1405/994

1202/99,

1102/991

1408/9491505/952

2704/995

2202/994

1603/9891303/989

1105/994

1108/983

203,989

2031989

1603/9892031989

8051994

minima

macropiper

I43100

1449/9

144728

144743

150124

150659

143200

142000

143522

144403

15/400

145500

144100

152800

145300

1449/9

150430

150659

143200

144100

144403

150440

152600

143200

142300

142200

1445/2

144901

144728

14/900

152500

15/600

144728

144703

142858

150500

15/600

142000

14/835

15/600

14/700

15/600

15/800

150400

14/900

14/700

153000

144800

14/800

144403

14/900

145300

142000

141700

144000

144300

142200

144100

142200

ferrugineumlaineSii

lanuginosalanuginosaternifolia

ternifolia

1303800

1295842

1300/04

1300/08

1305900

1302319

1303800

1301054

1295949

1294407

1302300

1300400

1294400

13/0800

1301700

1295842

1303218

1302319

1303800

1305400

1294407

1302830

1301900

1303800

1293500

1304800

1304759

1295840

1300/04

1300600

1300000

1294500

1300/04

1300031

1300607

I301000

1293500

1301 100

1304000

1294500

1301000

1293500

1294700

1303/30

1305600

1305700

1301600

13/0200

1305705

1294407

13/0100

1304100

1301100

130,000

1294500

1294500

1304500

1294400

1304800

axillaris

axillaris

axillaris

axillaris

axillaris

axillaris

am hemica

xerocarpa

bynoeibynoeipungenspungens

pungens

pungens

pungenspungenspungenszeylanica (3r)zeylanica (3r)stellatus

nitidissima

nitidissima

nitidissima

cylindrocarpacylindrocarpacorymbosa

,

I

Page 147: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

::

: PolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolycarpaeaPolygalaPolygalaPolygalaPolygalaPolygalaPolygalaPolygalaPolygalaPolygalaPolygalaPolygalaPolygalaPortulaca

Portulaca

Potamogetonam hemicaPouteria

RouterIa am hemica

Pouteria sericea

Pouteria sericea

Pouteria sericea

Pouteria sericea

Pouteria sericea

zeylanicaPouzolzia

Pouzolzia zeylanicaPouzolzia zeylanicaPouzolzia zeylanicaPouzolzia zeylanicaPremna acuminata

herbaceaPremna

Pseuderanthemum variabile

Pseudopogonatherum contortumPseudopogonatherum contortumPseudopogonatherum contortumPseudopogonatherum contortumPseudopogonatherum contortumPseudopogonatherum irritans

nudumPsilotum

nudumPsilotum

GorymbosacorymbosacorymbosaGorymbosainvolucrata

involucrata

involucrata

involucrata

longifloralongifloralongifloralongifloralongifloralongifloralongifloralongifloralongifloralongifloralongiflorastaininodina (3R)violacea

015087

027554

eriocepha!aexsquarrosa

exsquarrosaIinarifolia

longifolialongifoliapycnocephalapycnocephalarhinanthoides

stenoclada

bicolor

bicolor

;

CARYOPHYLLACEAECARYOPHYLLACEAE

CARYOPHYLLACEAE

CARYOPHYLLACEAE

CARYOPHYLLACEAE

CARYOPHYLLACEAE

CARYOPHYLLACEAE

CARYOPHYLLACEAE

CARYOPHYLLACEAECARYOPHYLLACEAE

CARYOPHYLLACEAE

CARYOPHYLLACEAE

CARYOPHYLLACEAECARYOPHYLLACEAE

CARYOPHYLLACEAE

CARYOPHYLLACEAE

CARYOPHYLLACEAE

CARYOPHYLLACEAECARYOPHYLLACEAE

CARYOPHYLLACEAE

CARYOPHYLLACEAE

POLYGALACEAE

POLYGALACEAE

POLYGALACEAE

POLYGALACEAE

POLYGALACEAE

POLYGALACEAE

POLYGALACEAE

POLYGALACEAE

POLYGALACEAE

POLYGALACEAE

POLYGALACEAE

POLYGALACEAE

PORTULACACEAE

PORTULACACEAE

POTAMOGETONACEAE

SAPOTACEAE

SAPOTACEAE

SAPOTACEAE

SAPOTACEAE

SAPOTACEAE

SAPOTACEAE

SAPOTACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

ACANTHACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

PSILOTACEAE

PSILOTACEAE

,

I

I

1305/994

1207/992

2704/995

2704/995

1305/994

1605/994

1305/994

2402/994

8051994

1305/994

1205/994

2303/958

1405/994

1403/963

1905/952

1905/952

1905/952

1905/952

2704/995

1305/994

1303/989

1405/994

8031989

1205/994

2002/994

1205/994

1305/994

2002/994

3031989

1305/994

1505/994

8031989

8031989

1405/994

1405/994

1405/994

1305/994

2202/994

1405/994

1405/994

1605/994

1205/994

2802/986

1603/989

8031989

1303/989

1103/989

2402/989

4031989

1305/994

1611/988

1405/994

1305/994

1205/994

1205/994

1505/994

1105/994

1205/994

1207/992

1441 43

143300

14/800

141800

144926

150500

143851

144901

142200

144406

144400

14/800

150406

144900

150000

145500

145500

150000

14/800

1441 00

145500

150406

150800

144400

144549

143521

144100

144549

143400

144100

150445

15/200

143800

150345

150406

144743

143851

144403

144728

144926

150500

144500

153000

14/900

150800

145400

150800

14/500

144900

144100

14/400

144728

144726

144406

143105

150410

142548

1445/2

143200

13/0836

1303800

1305705

1305705

1295923

1301 000

1301 055

1295840

1304800

13/0644

1304800

1305000

1302826

1305000

1305000

1304900

1304900

1304800

1305705

1305300

1300400

1302826

1303500

1304800

1295656

1301 848

1305300

1295656

1300200

1305300

1302825

1303400

1304400

1302823

1302826

1300/05

1301055

1294407

1300/04

1295923

1301000

1304800

13/0200

13/0100

1303500

1304100

1303400

1304100

1294600

1305300

1300600

1300/04

13/0205

13048i8

1300740

1302825

1302500

1304759

1303800

.

:

Page 148: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Psilotum

Psilotum

Psilotum

Psoralea

Psoralea

Psoralea

Pteridium

Pteridium

Pteris

Pterocaulon

Pterocaulon

Pterocaulon

Pterocaulon

Pterocaulon

Pterocaulon

Pterocaulon

Ptilotus

Ptilotus

Ptilotus

Ptilotus

PycnosporaPycnosporaPycnosporaRapaneaRapaneaRhynchosporaRhynchosporaRhynchosporaRhynchosporaRhynchosporaRhynchosporaRicinocarposRotala

Rotala

Rotala

Rotala

Rotala

Rotala

Rotala

Rotala

SacciolepisSacciolepisSacciolepisSacciolepisSacciolepisSacciolepisSalomonia

Salomonia

Santalum

Santalum

SantalumSarcostemma

Sarcostemma

Sarcostemma

SauropusSauropusSauropusSauropusSauropus

nudum

nudum

nudum

badocana

badocana

balsamica

revolutum

revolutum

PSILOTACEAE

PSILOTACEAE

PSILOTACEAE

FABACEAE

FABACEAE

FABACEAE

DENNSTAEDTIACEAE

DENNSTAEDTIACEAE

PTERIDACEAE

ASTERACEAE

ASTERACEAE

ASTERACEAE

ASTERACEAE

ASTERACEAE

ASTERACEAE

ASTERACEAE

AMARANTHACEAE

AMARANTHACEAE

AMARANTHACEAE

AMARANTHACEAE

FABACEAE

FABACEAE

FABACEAE

MYRSNACEAE

MYRSNACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

EUPHORBIACEAE

LYRTHRACEAE

LYRTHRACEAE

LYRTHRACEAE

LYRTHRACEAE

LYRTHRACEAE

LYRTHRACEAE

LYRTHRACEAE

LYRTHRACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POLYGALACEAE

POLYGALACEAE

SANTALACEAE

SANTALACEAE

SANTALACEAE

AsCLEPIDADACEAE

AsCLEPiDADACEAE

AscLEPiDADACEAEEUPHORBIACEAEEUPHORBIACEAE

EUPHORBIACEAE

EUPHORBIACEAE

EUPHORBIACEAE

globuliflorusglobuliflorusserrulatum

serrulatum

sphacelatumverbascifolium

calostachyuscorymbosuscorymbosusspicatuslutescens

lutescens

lutescens

benthamiana

benthamiana

exserta

exserta

heterochaeta

heterochaeta

heterochaeta

submarginata

1205/994

1303/989

1303/989

8051994

9051994

1303/989

9051994

2402/989

1205/994

2602/986

1405/994

1005/994

1002/99j

1407/977

9051994

1205/994

2506/970

8031989

1405/994

8031989

1305/994

1305/994

1005/994

1108/983

2031989

1205/994

1005/994

1405/994

1205/994

1205/994

1105/994

1005/994

1405/994

1405/994

8051994

1405/994

1603/989

4031989

1205/994

9051994

1305/994

1005/994

1405/994

1205/994

1105/994

1605/994

1605/994

3031989

1207/992

4031989

3031989

1405/994

1403/989

1303/989

1305/994

1605/994

2002/994

2402/989

9031989

144502

145800

144500

142200

1422/3

144700

14/833

14/500

1445/2

152600

150300

142130

143500

152500

1422/3

1445/2

144800

15/100

150406

144900

144100

1435/2

14/835

14/700

144100

142858

14/900

1449/9

144400

143105

142548

14/900

144743

144929

142200

150248

142200

142300

144502

1422/6

144100

142224

150406

143521

142000

150124

150124

143100

143300

144900

143400

144728

152800

145400144926

150500

144549

14/500

15/900

1304800

1300700

1305000

1304800

1304847

1304400

1304001

1304100

1304759

13/0600

1303100

1300838

1304000

1301800

1304847

1304759

13,0200

1305000

1302826

1305000

1305300

1301 850

1304000

1301000

1294400

1300607

1300600

1295842

1304800

1300744

1302500

1300600

1300/05

1295842

1304800

1303036

1304800

1293500

1304800

1304844

1305300

1302048

1302826

1295952

1301 100

1305900

1305900

1300500

1303900

1294600

1300900

1300/04

1304900

1304100

1295923

1301000

1295656

1304100

1295500

diandra

diandra

meXICana

meXICana

meXIcana

meXIcana

occultiflora

indica

indica

indica

indica

myOSuroidesmyOSuroideSciliata

ciliata

lanceolatum

lanceolatum

lanceolatum

viminale

viminale

viminale

elachophyllustrachyspermustrachyspermus

I

^

I

,

,

,

.

Page 149: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

SauropusSauropusScaevolaScaevolaScaevolaScaevola

SchizachyriumSchizachyriumSchizachyriumSchizachyriumSchizachyriumSchizachyriumSchoenoplectusSchoenoplectusSchoenoplectusSchoenoplectusScleria

Scleria

ScleriaScleria

Scleria

Scleria

Scleria

Scleria

Scleria

Scleria

Scleria

ScleriaScleriaScleriaScleria

ScleriaScleria

ScleriaScleria

SGIeria

ScleriaScleria

Scleria

ScleriaScleriaScleriaScleriaScleriaScleriaScleriaScleria

ScleriaScleria

Scleria

ScleriaScleriaScleriaScleriaScleriaScleria

SGIeriaScleria

Scleria

,

.

browniana

browniana

revoluta

taccada

fragilefragilefragilefragilefragilepachyarthronlateriflorusinucronatus

inucronatus

.

EUPHORBIACEAEEUPHORBIACEAEGOODENIACEAEGOODENIACEAEGOODENIACEAEGOODENIACEAEPOACEAEPOACEAEROACEAEPOACEAEPOACEAEPOACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAE

,

annularisannularis

brownii

brownii

brownii

brownii

brownii

caricina

ciliaris

ciliaris

ciliaris

ciliaris

laxa

Ievis

Ievis

lingulatalingulatalingulatalingulatalingulatalingulatalingulatalingulatalingulatanovae-hollandiaenovae-hollandiaenovae-hollandiae

poaeformispolycarpapygmaeapygmaeapygmaeapygmaeapygmaearugosa

rugosarugosasphacelatasphacelatasphacelatasphacelatasphacelata

90319892308/9871303/9892602/9861405/994

2405/9581505/994

2105/9521905/9522704/995

1305/9942105/9521105/994

1303/9891905/994

1405/9942402/989

40319891605/994

1205/9941603/9891403/989

1303/9891205/994

303198930319892502/98930319891205/994

1405/99430319892031989303198930319891205/994

1611/988303198930319892402/98930319891205/9941305/9941605/9941205/99440319891305/9941605/9941405/9941405/9941205/9941605/9941405/994

1105/994

1205/9941105/9942402/9891205/994

1005/9941405/994

152700

15/300

144700

152500

144724

152200

144707

145800

14520014/800

1435/2

145500

142548

145800

150345

144743

14/500

144900

145510

144500

141900

152800

144500

144500

143400

143100

14/500

143400

142858

150248

143400

144000142600

143400

143521

14/400

143400

142400

14/500

143400142858144100150659143105142300

144726

150124

15024815040614352i

150124150248142000

143522142000

14/50014352i

14/835

144728

13000001294000130440013/09001300/041305000

1300045

1295200

13059001305705

130185013/1000

130250013007001302823

1300/05

1304100

1294900

13/0223

130480013/0100

1304900

1305000

1304800

1302000

13005001301 800

13020001300607

1303036

13020001294500

130020013009001295952

1300600

13002001300300130410013020001300607130530013023191300744129350013/02051305900130303613028261295952130590013030361301100129594913011001304100129595213040001300/04

Page 150: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Scleria

Scleria

Scleria

Sebastiania

Sebastiania

Sebastiania

SeiaginellaSenna

Senna

Senna

Senna

Senna

Sesbania

SetariaSetaria

Setaria

Setaria

Setaria

Setaria

Setaria

Setaria

Sida

Sida

SinilaxSinilaxSolanum

Solanum

SolanumSolanum

SolanumSolanum

Solanum

Solenostemon

Solenostemon

Solenostemon

Solenostemon

Solenostemon

Solenostemon

Solenostemon

SorghumSorghumSorghumSorghumSowerbaea

SpermacoceSpermacoceSpermacoceSpermacoceSpermacoceSpermacoceSpermacoceSpermacoceSpermacoceSpermacoceSpermacoceSpermacoceSpermacoceSpermacoceSphenoclea

chainaeleachainaeleachainaeleaciliaris

cladophyllacladophyllao1igocladao1igoclada

CYPERACEAECYPERACEAECYPERACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAESELAGINELLACEAECAESALPINIACEAECAESALPINIACEAECAESALPINIACEAECAESALPINIACEAECAESALPINIACEAEFABACEAEPOACEAEPOACEAEPOACEAEPOACEAEROACEAEROACEAEPOACEAEPOACEAEMALVACEAEMALVACEAESMILACACEAESMILACACEAESOLANACEAESOLANACEAESOLANACEAESOLANACEAESOLANACEAESOLANACEAESOLANACEAELAMIACEAELAMIACEAELAMIACEAELAMIACEAELAMIACEAELAMIACEAELAMIACEAEPOACEAEPOACEAEPOACEAEROACEAELILIACEAERUBIACEAERUBIACEAERUBIACEAERUBIACEAERUBIACEAERUBIACEAERUBIACEAERUBIACEAERUBIACEAERUBIACEAERUBIACEAERUBIACEAERUBIACEAERUBIACEAESPHENOCLEACEAE

carinabina

apiculataapiculataapiculataapiculataoplismenoidesoplismenoidesoplismenoidesoplismenoidesacuta

fibulifera

australisaustralisechinatum

echinatum

echinatumIucani

Iucani

1305/9942402/9891005/994

1005/994

1405/994

9051994

1105/994

2031989

2202/994

1305/9941605/9941405/994

1908/9491205/9941905/9521505/9941305/9941303/9892402/9892031989303198990519941605/9941105/9941205/9941305/994

1405/994

1002/99j1407/977

1407/977

1405/994

1405/9941303/9892402/98930319891405/994

905199430319891303/9891108/9491207/9941305/9941305/9941105/99430319891103/989203198930319891305/9941205/9941305/9941205/9941205/994803198980319891202/99,80319892002/9941004/990

144726

14/500

14/835

14/900

150406

1422/3

142000

144300

143951

143851

150500

144728

152100

144406

144600

150400

1435/2

145800

14/500

1441 00

1424001422/3

150500142000144406

143851

1449/9

143500152300152300144728

144728

145800

14/500

143400

150406

14/833

143400

144500

152600143105

144100

143455

142000

143400

150800144100

1426001444061445/2144406143522

14440615270015270014/900144900144549142700

13/0205

1304100

1304000

1300600

1302826

1304847

1301054

1294500

1294838

1301055

1301000

1300/04

1301 700

1304818

13/0100

1310000

1301850

1300700

1304100

1294400

130030013048471301000130110013048i8

1301055

1295842

13040001301700

130,700

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scutellarioidesscutellarioidesscutellarioidesscutellarioidesscutellarioidesscutellarioidesscutellarioidesmatarankense

plumosumstipoideumstipoideumalliacea

auriculataauriculata

brachystemaexserta

,

.

.

,

zeylanica

,

I

Page 151: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

;

I SporobolusStackhousiaStackhousiaStackhousia

. Stackhousia

Stackhousia

I StackhousiaStackhousiaStackhousia

; StaurogyneI Staurogyne

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I SternodiaStenocarpusStenocarpusStenocarpusStenocarpusStenocarpus

I StenocarpusStenocarpusSterculia

StrychnosStrychnosStrychnosStrychnosStrychnosStrychnosStylidium

I StylidiumStylidiumStylidiumStylidiumStylidiumStylidiumStylidiumStylidiumStylidiumStylidium

; StylidiumStylidiumStylidiumStylidium

I StylidiumStylidiumStylidiumStylidiumStylidiumStylidiumStylidiumSyzygiumSyzygiumSyzygiumSyzygiumSyzygium

virginicusintermediaintermediaintermediaintermediaintermediaintermediaintermediaintermedia

IeptocaulisIeptocaulisIythrifoliaIythrifoliaIythrifoliaIythrifoliaIythrifoliaIythrifolia

POACEAESTACKHOUSIACEAESTACKHOUSIACEAESTACKHOUSIACEAESTACKHOUSIACEAESTACKHOUSIACEAESTACKHOUSIACEAESTACKHOUSIACEAESTACKHOUSIACEAEACANTHACEAEACANTHACEAESCROPHULARIACEAESCROPHULARIACEAESCROPHULARIACEAESCROPHULARIACEAESCROPHULARIACEAESCROPHULARIACEAESCROPHULARIACEAEPROTEACEAEPROTEACEAEPROTEACEAEPROTEACEAEPROTEACEAEPROTEACEAEPROTEACEAESTERCULIACEAELOGANIACEAELOGANIACEAELOGANIACEAELOGANIACEAELOGANIACEAELOGANIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLID!ACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAESTYLIDIACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAE

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acacioidescunning hamiicunning hamiicunning hamiicunning hamiicunning hamii

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14/500

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144510150300

145500143455

1505/5

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14/83314/835

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144400

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1445/2

144743

150248144000144901

1505/5

142224

144100143100

142858

142858144400143400144300152800

15/3001427001449/9142000

holtzei

lucidalucidalucida

lucidalucidalucida

ceratophorumceratophorumdunlopianumfissilobium

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pachyrhizumpachyrhizumpachyrhizumschizanthumschizanthumschizanthumschizanthum

12948041295923

13041001304800130050013035001302826130570513/080013048001305300130480013/0205

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angophoroidesangophoroideseucalyptoideseucalyptoideseucalyptoides

Page 152: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Tabernaemontana

Tabernaemontana

Tacca

Tacca

Tacca

Tacca

Taenitis

Taenitis

Tarenna

TephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTephrosiaTerminalia

Terminalia

Terminalia

Terminalia

Terminalia

Terminalia

Terminalia

Terminalia

Terminalia

Terminalia

orientalis

orientalis

IeontopetaloidesIeontopetaloidesmaculata (3kC)maculata (3kC)blechnoides

blechnoides

dallachiana

brachyodoncoriacea

coriacea

coriacea

eriocarpa

juncea

IeptocladaIeptocladaIeptocladamacrocarpa

macrocarpa

macrocarpa

nematophyllanematophyllaoblongataphaeospermaphaeospermaphaeospermaphaeospermapolyzygareinotiflora

reinotiflora

reinotiflora

reinotiflora

reinotiflora

reticulata

rosea

APOCYNACEAE

APOCYNACEAE

TAGCACEAE

TACCACEAE

TAGCACEAE

TACCACEAE

HEMIONITIDACEAE

HEMIONITIDACEAE

RUBIACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAEFABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

COMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAE

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canescens

canescens

canescens

canescens

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carpentariaeferdinandiana

ferdinandiana

ferdinandiana

ferdinandiana

Page 153: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

:

I

TerminaliaTerminalia

Terminalia

Terminalia

Terminalia

TerminalIa

Terminalia

Terminalia

TerminalIa

Terminalia

Terminalia

Terminala

Terminalia

TerminaliaTerminalia

TerminaliaTerminalia

TerminalIaTerminalia

Terminalia

TerminaliaTerminalia

TerminaliaThaumastochloaThaumastochloaThaumastochloaThecanthes

Thecanthes

Thecanthes

ThecanthesThecanthes

Themeda

Themeda

Themeda

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Timonius

Timonius

TinosporaTrachymeneTrachymeneTrema

Trema

Trema

Trianthema

Trianthema

TribulopisTrichodesma

TrichosanthesTrichosanthesTrichosanthesTrichosanthesTrichosanthesTrichosanthesTrichosanthesTrichosanthesTrichosanthes

ferdinandianaferdinandiana

ferdinandiana

ferdinandiana

ferdinandiana

grandifloragrandifloragrandifloralatipeslatipeslatipeslatipeslatipeslatipeslatipeslatipesmicrocarpa

platypterapterocaryapterocaryapterocaryavolucris

volucris

major

major

maiorconcreta

punicea

sanguinea

sanguinea

sanguinea

arguenstriandra

triandra

.

COMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAECOMBRETACEAEPOACEAEPOACEAE

ROACEAETHYMELAEACEAETHYMELAEACEAETHYMELAEACEAETHYMELAEACEAETHYMELAEACEAEPOACEAE

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I

:

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1505/994

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2202/994

1207/994

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1305/994

1605/994

2511/9871305/994

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1505/9941305/9941305/994

2102/994

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9051995

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1205/994

1505/994

1305/9941407/977

1205/994

1505/9941405/99430319892408/987

80319892704/9952002/9941205/9941603/98990319891103/98940319892031989

1103/9892402/98930319891303/989

,

143522

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150248

145300

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144400

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142222

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1302825

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populneoideschinensis

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timOn

sinilacina

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rhynchocalyptrarhynchocalyptraangustifoliazeylanicumcucumerina

cucumerina

cucumerina

cucumerina

cucumerina

cucumerina

cucumerina

cucumerina

holtzei

Page 154: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

TricostulariaTricostulariaTricostularia

TriglochinTriglochinTriglochinTriodia

Triodia

Triodia

Triodia

Triodia

Triodia

Triodia

Triumfetta

Triumfetta

Triumfetta

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Triumfetta

Triumfetta

Triumfetta

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Triumfetta

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Triumfetta

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Urena

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undulata

undulata

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dubium

dubium

microstachyamicrostachyamicrostachyamicrostachyamicrostachyamicrostachyastenostachyaalbida

denticulata

denticulata

parvifloraparvifloraparviflorapentandraplumigera

CYPERACEAECYPERACEAECYPERACEAEJUNCAGINACEAEJUNCAGINACEAEJUNCAGINACEAEPOACEAE

POACEAEPOACEAEPOACEAE

POACEAE

POACEAEPOACEAE

AscLEPiADACEAEAsCLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEMELIACEAE

MELIACEAEMELIACEAEMELIACEAEAsCLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEASOLEPIADACEAEAscLEPiADACEAEAscLEPiADACEAETYPHACEAEFABACEAEFABACEAEFABACEAEFABACEAELENTIBULARIACEAELENTIBULARIACEAELENTIBULARIACEAELENTIBULARIACEAELENTIBULARIACEAELENTIBULARIACEAELENTIBULARIACEAELENTIBULARIACEAELENTIBULARIACEAELENTIBULARIACEAELENTIBULARIACEAE

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2202/994

1405/994

2031989

2402/989

1105/994

1303/98980319892704/995

1505/994

1305/994

1205/994

1207/994

1505/994

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1605/9941305/99490519941305/9941405/9941305/9941303/989

1105/994

2031989

9031989

90319891505/9941103/989

90319891603/9891303/9891103/9899031989

1605/994

1405/994

1303/9891103/9891103/9891303/9891305/99490319891004/9901305/994

2002/994

1505/994

50419671205/9941405/994

1005/9941405/9941405/99490519941205/994

905199420319892402/9941205/994

143522

142224

143951

144926

144000

14/500

142000

144700

15080014/800

150420

143455

144400

14352i

1438511441 00

1449/9

150500

143851

1422/3

144100

150300144100

145800

142000

144100

15/500

15/900

150430

150800

15/500

14/900

145400

15/400

15/500150500

150300

144700

15080015/400144500

143455

15/900

142700144100

144549

150420

14/800

144400

15040614,833

144728

150406

14/833

143521

14/833

144300

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pubesGenspubescenspubescenspubescenscinerascens

cinerascens

cinerascens

cinerascens

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flexuosa

flexuosa

flexuosa

flexuosa

flexuosa

flexuosa

flexuosa

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13023001300100

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1301t 001294900130530012956561302824

13/07001304800130282613040011300/041302826130400112959521304001129450012954301300607

^

domingensislagopodioideslagopodioideslagopodioideslobata

caerulea

caerulea

caerulea

chrysanthachrysanthachrysanthacircumvolutacircumvoluta

dunlopiihamiltonii(3RC)Ieptoplectra

.

Page 155: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Utricularia

Utricularia

Utricularia

Utricularia

Utricularia

Utricularia

Utricularia

Utricularia

Utricularia

Utricularia

Utricularia

Utricularia

Vavaea

Ventcordia

Veincordia

Ventcordia

Verticordia

Vetiveria

Vetiveria

VignaVignaVignaVignaVignaVitex

Waitheria

Waltheria

Waltheria

Waltheria

Waltheria

Wedelia

Whiteochloa

Whiteochloa

Whiteochloa

WrightiaWrightiaXanthostemon

Xanthostemon

Xanthostemon

Xanthostemon

Xanthostemon

Xanthostemon

Xanthostemon

Xanthostemon

XenostegiaXenostegiaXenostegiaXenostegiaXerochloa

Xerochloa

XyrisXyrisXyrisXyrisXyrisXyrisXyrisXyrisXyris

I

I

IeptoplectraIimosa

inuelleri

odorata

odorata

odorata

uliginosauliginosauliginosa

LENTIBULARIACEAE

LENTIBULARIACEAE

LENTIBULARIACEAE

LENTIBULARIACEAE

LENTIBULARIACEAE

LENTIBULARIACEAE

LENTIBULARIACEAE

LENTIBULARIACEAE

LENTIBULARIACEAE

LENTIBULARIACEAE

LENTIBULARIACEAE

LENTIBULARIACEAE

MELIACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

POACEAE

POACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

STERCULIACEAE

STERCULIACEAE

STERCULIACEAE

STERCULIACEAE

STERCULIACEAE

ASTERACEAE

POACEAE

POACEAE

POACEAE

APOCYNACEAE

APOCYNACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

CONVOLVULACEAE

CONVOLVULACEAE

CONVOLVULACEAE

CONVOLVULACEAE

POACEAE

POACEAE

XYRIDACEAE

XYRIDACEAE

XYRIDACEAE

XYRIDACEAE

XYRIDACEAE

XYRIDACEAE

XYRIDACEAE

XYRIDACEAE

XYRIDACEAE

australiana

cunning hamiicunning hamiicunning hamiiverticillata

pauciflorapaucifloralanceolata

lanceolata

lanceolata

lanceolata

vexillata

acuminata

indica

indica

indica

indica

indica

1205/994

1405/994

1205/994

1605/994

3031989

3031989

1605/994

1105/994

2402/989

1205/994

1205/994

1303/989

1303/989

4101989

1202/99,

2702/986

1510/982

2602/986

1605/994

1205/994

1505/994

1205/994

1505/994

1405/994

4031989

1305/994

1905/952

1405/994

1905/952

1405/994

8031989

8031989

2602/986

1205/994

1202/99j

1505/994

1005/994

1305/994

1405/994

1205/994

1405/994

1005/994

2031989

1505/994

1305/994

1605/994

1205/994

1305/994

1805/952

2306/988

1405/994

1305/994

2202/994

1605/994

1405/994

9051994

1205/994

1405/994

9051994

143105

144926

143105

150124

143400

142600

1501 24

142000

14/500

1443/2

1443/2

145500

144500

14/800

14/900

153000

142800

152600

150659

142858

150445

14352i

150400

150248

144900

144100

150700

150406

150700

1435/2

144900

152700

152500

144406

14/900

150430

14/835

143455

144728

143851

150400

14/900

144300

150420

144358

150124

144406

1435/2

144800

143000

144728

144100

143951

150659

150345

14/833

143105

1449/9

14/833

^

1300740129592313007401305900

1300900

1300200

1305900

1301 100

1304100

1304759

1304759

1300400

1305000

1305700

1305600

13/0800

1310000

13/0600

1302319

1300607

1302825

1295952

1303/30

1303036

1294600

1305300

1304200

1302826

13/0800

1301850

1305000

1302600

13/0900

13048i8

1305500

1303218

1304000

1301835

1300/04

1301 055

1303/30

1300600

1294500

1302824

13/0615

1305900

13048i8

1301850

13/0200

1293700

1300/04

1305300

1294838

1302319

1302823

1304001

1300740

1295842

1304001

capillipescapillipessemitonsa

salignasalignaeucalyptoideseucalyptoidesparadoxusparadoxusparadoxusparadoxusparadoxusparadoxustridentata

tridentata

tridentata

tridentata

barbata

jinberbjs

coinplanatacoinplanatacoinplanatacoinplanatacoinplanatacoinplanatacoinplanataindica

indica

Page 156: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

XyrisXyrisXyrisXyrisYakirra

Yakirra

Yakirra

Yakirra

Yakirra

ZanthoxylumZiziphusZiziphusZornia

Zornia

pauciflora

majusculamajusculamajusculamajusculapaucifloraparviflorumquadrilocularisquadrilocularischaetophorain uriculata

XYRIDACEAEXYRIDACEAEXYRIDACEAEXYRIDACEAEPOACEAEROACEAEPOACEAEROACEAEROACEAERUTACEAERHAMNACEAERHAMNACEAEFABACEAEFABACEAE

,

1405/9941405/994

1105/9944051994

8031989I605199480319891405/994

8051994

1303/9891103/989

1103/989

2101988

1605/994

1449/9

144728

142500

142000

15/200150659150800150345

142200

144500

150800

15/400

142400

150500

1295842

1300/04

13025001301054

1303400

13023i9

1305500

1302823

1304800

1305000

1303400

1302300

1295000

1301000

o

.

I

.

.

.

Page 157: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

I

^

Appendix 4 Species listfrom locations bounded by the co-ordinates 14 14 ' 129 35 'to 15 30' 131 10'Conservation status is rioted. * indicates an introduced species.These species were recorded prior to the 1997 survey.

GENUS

,

Abelmoschus

Abutilon

Abutilon

Abutilon

Abutilon

Abutilon

Abutilon

Abutilon

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

.

SPECIES NAME

manihot

andrewsianum

andrewsianum

andrewsianum

andrewsianum

andrewsianum

cunning hamiiIndicum

alieniana

alieniana

aulacocarpaaulacocarpaaulacocarpaaulacocarpacalcigeracataractae

conjunctifoliaconjunctifoliadimcilis

difficilis

dimcilis

dimcilis

difficilis

dimidiata

dimidiata

froggattiifroggattiifroggattiifroggattiifroggattii90noclada90nOCladahammondii

hemignostahemignostahemignostahemsleyiholosericea

holosericea

holosericea

holosericea

humifusa

humifusa

kelleri(3r)kelleri (3r)latescens

latescens

Iatifolia

IeptophlebaIycopodiifolia

FAMILY

*CHARACEAE

*CONVOLVULACEAE*FABACEAE

MALVACEAE

MALVACEAE

MALVACEAE

MALVACEAE

MALVACEAE

MALVACEAE

MALVACEAE

MALVACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAEMIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAEMIMOSACEAE

MIMOSACEAE

MIMOSACEAEMIMOSACEAEMIMOSACEAEMIMOSACEAE

MIMOSACEAEMIMOSACEAEMIMOSACEAEMIMOSACEAEMIMOSACEAEMIMOSACEAEMIMOSACEAE

MIMOSACEAE

,

COLLECTION LATITUDE LONGITUDE

DATE

1505/994

9081983

2602/986

4031989

9031989

1405/994

9051994

1403/989

1103t 989

1305/994

1603/989

1005/994

2402/994

1105/994

1505/994

1005/994

1505/994

9051994

1605/994

1403/989

2402/994

1605/994

1205/994

1105/994

1305/994

1305/994

1505/994

1207/994

2602/986

9031989

2402/994

1403/989

2208/987

2108/949

2105/952

1605/994

1407/977

1407/977

1908/949

1205/994

4101989

1605/994

2105/952

1505/994

2031989

2704/995

2308/987

2308/987

4101989

1202/991

1405/994

1303/989

8031989

I

150400

14/700

152500

142300

15/900

150300

1422/3

152800

15/400

143455

14/900

14/900

14490t

142000

150430

14/835

1505/5

1422/3

150500

152600

14490i

1501 24

143522

142000

144100

143455

142858

143521

152600

15/800

144901

152800

152300

145500

145700

150124

152500

152500

152600

144500

142700

150500

145600

1505/5

144000

14/800

15/600

15/600

14/800

14/900

144926

144700

150800

1310000

1300300

13/0900

1293500

1301100

1300000

1304847

1304900

1302300

1301835

13/0100

1300600

1295840

1301100

1303218

1304000

1302845

1304847

1301000

13/0600

1295840

1305900

1295949

1301000

1305300

1301835

1300607

1295952

13/0600

1294000

1295840

1304900

1293700

1304900

1304900

1305900

1301800

1301800

1301800

1304800

1305500

1301000

1304800

1302845

1294500

1305705

1294500

1294500

1305700

1305500

1295923

1304400

1303500.

,

Page 158: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

Acacia

AChyranthesActinostachysActinostachysActinostachysAdansonia

Adansonia

IycopodiifoliaIycopodiifoliamegalanthamegalanthamegalanthain ultisiliquainultisiliquainultisiliquamultisiliquamultisiliquamultisiliquaneurocarpa

nuperrima

nuperrima

nuperrima

nuperrima

nuperrima

oncinocarpa

pachyphloiapellitapellitapellitapellitapellitapellitapellitapellitapellitaplatycarpaplatycarpaPIectocarpaPIectocarpapiectocarpapledocarpaPIectocarpaPIectocarpasetulifera (3K)subternata

translucens

translucens

translucens

turnida

turnida

turnida

turnida

turnida

turnida

turnida

turnida

turnida

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAE

MIMOSACEAEMIMOSACEAE

MIMOSACEAE

AMARANTHACEAESOHIZAEACEAE

SCHIZAEACEAE

SCHIZAEACEAE

BOMBACECEAEBOMBACECEAE

2

1403/989

1303/989

2202/994

1605/994

2308/987

1505/994

1105/994

2202/994

2402/994

1305/994

1505/994

4101989

2502/986

1105/994

8031989

1205/994

8031989

1505/994

1405/994

1108/983

1605/994

2402/989

1303/989

9051994

1205/994

2031989

1505/994

1305/994

1105/994

1505/994

1605/994

1405/994

1205/994

2031989

1305/994

1605/994

9031989

2702/986

1505/994

2202/994

1505/994

1605/994

1405/994

9091957

4101989

1305/994

1405/994

1207/992

1005/994

1/2/855

1405/994

1205/994

1405/994

1303/989

2031989

3031989

1303/989

8051994

1405/994

152800

145500

144403

150659

15/600

144703

142000

144403

144901

143455

1505/5

142700

152600

142000

150800

144400

143800

150430

150345

143200

150124

14/500

144700

14/833

143521

144100

150440

143455

142000

150430

150500

144926

144500

1441 00

143455

150659

15/600

153000

150400

144403

150420

150124

144743

150000

14/800

14385i

1449/9

143300

14/900

152600

144728

1445/2

144728

144500

144000

143400

145500

142200

150248

.

1304900

1300400

1294407

1302319

1294500

1300031

1301100

1294407

1295840

1301835

1302845

1305500

13/0600

1301100

1303500

1304800

1304400

1303218

1302823

1295400

1305900

1304100

1304400

1304001

1295952

1294400

1302830

1301835

1301100

1303218

1301000

1295923

1304800

1294400

1301835

1302319

1293500

13/0800

1303/30

1294407

1302824

1305900

1300/05

13/1000

1305700

1301055

1295842

1303900

1300600

1300600

1300/04

1304759

1300/04

1305000

1294500

1300200

1300400

1304800

1303036

.

.

.

.

.

.

I

;

aspera

digitatadigitatadigitatagregorii

gregorii

.:

.

.

.

,

.

.

I

Page 159: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

,

:

Adansonia

Adenia

Adenosma

Adenosma

Adenosma

Adenostemma

Adenostemma

Adenostemma

Adjantum

Adjantum

Adjantum

AegialitisAegicerasAidia

Aidia

Aidia

Aidia

Aidia

Aidia

Aidia

Aidia

Aidia

Aidia

A1bizia

A1phitoniaA1phitoniaA1phitoniaA1phitoniaAIStonia

AIStonia

AIStonia

AIStonia

AIStonia

AIStonia

AIStonia

AIStonia

AIStonia

Alternanthera

Alternanthera

Alter nanthera

Alternanthera

A1ysicarpusAm mannia

AmyemaAmyemaAmyemaAmyemaAmyemaAmyemaAmyemaAmyemaAmyemaAmyemaAmyemaAneilema

An isomeles

An isomeles

An isomeles

An isomeles

^.

gregoriiheterophyllainuelleri

inuelleri

inuelleri

Iavenia

Iavenia

Iavenia

hispidulum (3rC)philippensephilippenseannulara

comiculatum

racemosa

racemosa

racemosa

racemosa

racemosa

racemosa

racemosa

racemosa

racemosa

racemosa

canescens

excelsa

excelsa

excelsa

excelsa

actinophyllaspectabilisspectabilisspectabilisspectabilisspectabilisspectabilisspectabilisspectabilisdenticulata

nodiflora

nodiflora

^

.

.

.

BOMBACECEAEPASSIFLORACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

ASTERACEAE

ASTERACEAE

ASTERACEAE

ADIANTACEAE

ADIANTACEAE

ADIANTACEAE

PLUMBAGiNACEAEA

MYRSINACEAE

RUBIACEAE

RUBIACEAE

RUBIACEAE

RUBIACEAE

RUBIACEAE

RUBIACEAE

RUBIACEAE

RUBIACEAE

RUBIACEAE

RUBIACEAE

MIMOSACEAE

RHAMNACEAE

RHAMNACEAE

RHAMNACEAE

RHAMNACEAE

APOCYNACEAE

APOCYNACEAE

APOCYNACEAE

APOCYNACEAE

APOCYNACEAE

APOCYNACEAE

APOCYNACEAE

APOCYNACEAE

APOCYNACEAE

AMARANTHACEAE

AMARANTHACEAE

AMARANTHACEAE

AMARANTHACEAE

FABACEAE

LYTHRACEAE

LORANTHACEAE

LORANTHACEAE

LORANTHACEAE

LORANTHACEAE

LORANTHACEAE

LORANTHACEAE

LORANTHACEAE

LORANTHACEAE

LORANTHACEAE

LORANTHACEAE

LORANTHACEAECOMMELINACEAELAMIACEAE

LAMIACEAE

LAMIACEAE

LAMIACEAE

3

.

,

1405/994

2302/994

1505/994

1303/989

1505/994

1303/989

1603/989

4031989

1505/994

3031989

2402/989

2302/994

2308/987

1205/994

1205/994

9031989

1405/994

1103/989

1303/989

1103/989

2031989

1505/994

1505/994

1603/989

1303/989

2202/994

1303/989

1505/994

1081961

1603/989

9031989

1405/994

1605/994

1207/992

1202/99'

1403/989

1856

1305/994

9031989

1407/977

1405/994

1405/994

6071983

1305/994

1207/992

2202/994

1605/994

1005/994

1407/977

1407/977

9051994

1403/989

1505/994

1605/994

2202/994

1205/994

1605/994

2402/989

1305/994

150345

144901

150300

144700

1505/5

145800

142200

142300

150300

143100

14/500

1436/4

15/300

144503

1445/2

15/900

150300

150800

144700

15/400

144300

1505/5

150440

14/900

145800

144403

144700

150440

14/700

14/900

151500

1449/9

150500

143300

14/700

152800

145300

144406

152900

152800

144728

150345

15/300

143851

143300

143951

150440

14/835

152500

152500

1422/3

152800

144707

150124

143951

144406

150659

14/500

1435/2

I

1302823

1295840

1303100

1304400

1302845

1300700

1304800

1293500

1303100

1300500

1304100

1294804

1294000

1304757

1304759

1301100

1303100

1303400

1304400

1302300

1294500

1302845

1302830

I310100

1300700

1294407

1304400

1302830

13/0800

13,0100

1300100

1295842

1301000

1303900

1305600

1304900

1301 700

13/0644

1301000

1302200

1300/04

1302823

1304000

1301055

1303800

1294838

1301 020

1304000

1301800

'30/800

1304847

1304900

1300045

1305900

1294838

1304818

1302319

1304100

1301850

.

:

:

glumaceusbaccifera

benthamii

benthamii

benthamii

benthamii

bifurcata

iniqueliiin iqueliivilliflora

villiflora

a

siliculosum

malabarica

malabarica

malabarica

malabarica

Page 160: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

ArithobolusAntidesma

Antidesma

Antidesma

Antidesma

AponogetonAristidaAristida

AristidaAristida

Aristida

Aristida

Aristida

Aristida

Aristida

Aristida

Aristida

Aristida

Aristida

Aristida

AristidaAristida

AristidaArundinellaArundinellaArundinellaArundinellaArundinellaArundinellaArundine!IaArundinellaArundinellaArundinellaArundinellaArundinellaArundinella

AsteromyrtusAtalayaAUStrodolichosAUStrodolichosAvicennia

BacopaBanksiaBlechnumBlechnumBlechnumBlechnum

BlepharocaryaBlepharocaryaBlumea

Blumea

Blumea

Blumea

Blumea

Blumea

Blumea

Blumea

Blumea

Blumea

filifolius

parvifoliumparvifoliumparvifoliumparvifoliumelongatusexserta

exserta

exserta

exserta

exserta

holathera

holathera

ingrataIatifolia

queenslandicaqueenslandicaschultziischultziischultzii

schultziischultzii

SANTALACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAEAPONOGETONACEAEROACEAEROACEAEPOACEAEPOACEAEPOACEAEPOACEAE

POACEAEPOACEAEPOACEAEROACEAEPOACEAEPOACEAEPOACEAEPOACEAE

POACEAEPOACEAEPOACEAEPOACEAEROACEAEPOACEAEROACEAEROACEAEROACEAEPOACEAEPOACEAEPOACEAEPOACEAEPOACEAEPOACEAEPOACEAEMYRTACEAESAPINDACEAEFABACEAEFABACEAEVERBENACEAESCROPHULARIACEAEPROTEACEAEBLECHNACEAEBLECHNACEAEBLECHNACEAEBLECHNACEAEANACARDIACEAEANACARDIACEAEASTERACEAEASTERACEAEASTERACEAEASTERACEAEASTERACEAEASTERACEAEASTERACEAEASTERACEAEASTERACEAEASTERACEAE

4

1305/9941405/994

20319893031989

1305/994

I6051994

1205/9941405/994

1505/9941305/9941005/994

1505/994

1905/9521305/9941905/9522105/9521605/9941205/9941305/9941605/994

2105/9522105/9521405/9941005/9941205/9949051994

1205/9941005/994

1505/994

1105/9941805/95230319899051994

90519941505/9941305/9941005/9941405/994

90519941603/9892302/9941405/9941005/99441019891205/9941505/9941305/9941305/9941405/9941207/9921305/99480819831205/9941605/9942306/98880819831605/9941305/9941305/994

nepalensisnepalensisnepalensisnepalensisnepalensisnepalensisnepalensisnepalensisnepalensisnepalensisnepalensisnepalensisnepalensissymphyocarpavariifolia

errabunduserrabundusmarina

floribundadentata

orientaleorientaleorientaleorientale

depauperatadepauperataaxillarisdiffusa

diffusa

diffusa

diffusa

integrifoliaintegrifoliapsammophilapsammophilasaxatilis

144926

144728

144100

143400

143455

150659

1445/2

150345

150420143455

14/835

150300

145600

144100

144500

145600

145510

144400144100

145510

144400

144400

144728

142130

1435221422/6

144502

142224

150300

142000

144200143100

14/833

1422/31504101435/214/900150248

14222214/900

1436/4

144100142224142700144502150440143455

143851

1449041432001445/614/70014450215065914220014,700150124144926144358

12959231300/0412944001300900

1301835

13023191304759130282313028241301 835

1304000

1303100

1304800

1305300

13/0600130480013/022313048001305300

13/0223

13/080013/0800

1300/04

1304838

1295949

1304844

13048001302048

1303100

1301054

13/070013005001304001

1304847

1302825

130185013006001303036130483813/010012948041305400130204813055001304800130283013018351301055

1295940130380013/0326130100013048001302319129560013010001305900129592213/0615

^

I

^

I

.

I

^

.

I

I

I

Page 161: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

I

*

Blumea

Blumea

Blumea

Blumea

Blumea

Blumea

BlyxaBlyxaBlyxaBlyxaBIWaBlyxaBIWaBoerhavia

Boerhavia

Boerhavia

Bonamia

Bonamia

Bonamia

Boronia

Boronia

Boronia

Boronia

Boronia

Boronia

Boronia

Boronia

Boronia

Boronia

Boronia

Boronia

Boronia

Boronia

Boronia

Boronia

Boronia

Boronia

Bossiaea

Bossiaea

Bossiaea

Bossiaea

Bossiaea

Bothriochloa

Bothriochloa

Brachiaria

Brachiaria

BrachyachneBrachychitonBrachychitonBrachychitonBrachychitonBrachychitonBreyniaBriedelia

Briedelia

Briedelia

Buchanania

Buchnera

Buchnera

.

saxatilis

saxatilis

saxatilis

saxatilis

tenella

tenella

aubertii

aubertii

aubertii

aubertii

aubertii

aubertij

aubertii

coccinea

coccinea

a

,

ASTERACEAE

ASTERACEAE

ASTERACEAE

ASTERACEAE

ASTERACEAE

ASTERACEAE

HYDROCHARITACEAE

HYDROCHARITACEAE

HYDROCHARITACEAE

HYDROCHARITACEAE

HYDROCHARITACEAE

HYDROCHARITACEAE

HYDROCHARITACEAE

NYCTAGINACEAE

NYCTAGINACEAE

NYCTAGINACEAE

CONGOLVULACEAE

CONGOLVULACEAE

CONGOLVULACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

POACEAE

POACEAE

ROACEAE

POACEAE

POACEAE

STERCULIACEAE

STERCULIACEAE

STERCULIACEAE

STERCULIACEAE

STERCULIACEAEEUPHORBIACEAE

EUPHORBIACEAE

EUPHORBIACEAE

EUPHORBIACEAE

ANACARDIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

5

paludosa

1305/994

8081983

1205/994

1405/994

1005/994

1305/994

2031989

1405/994

1205/994

1305/994

1603/989

1405/994

2402/989

1108/949

4031989

1603/989

9051994

1605/994

2202/994

1605/994

1305/994

1205/994

1605/994

2031989

1405/994

2702/986

1305/994

1605/994

9031989

2031989

2202/994

2202/994

9031989

3021989

1405/994

1005/994

2031989

1205/994

2202/994

2031989

1305/994

2702/986

2602/986

9051994

1205/994

9031989

9031989

1205/994

2202/994

5081990

1305/994

1403/98'

1405/994

1603/989

3031989

1303/989

1102/991

1005/994

1405/994

grandisepalagrandisepalalanceolata

lanceolata

lanceolata

lanuginosalanuginosalanuginosalanuginosalanuginosalanuginosalanuginosalanuginosalanuginosalanuginosa

a

143851

14/700

144502

1504/1

142130

144406

144000

150300

1431 05

143455

142200

150345

14/500

152000

144900

14/900

1421 30

150124

143951

150500

143851

143522

I50124

144100

144728

152800

143851

150124

15/900

144300

144403

144403

15/600

144300

144743

142000

144100

144906

144403

144100

143455

153000

152600

142206

144406

152900

152900

144406

143951

150900

144100

152800

1449/9

14/900

143400

144500

14/700

142224

150300

.

1301 055

1301000

1304800

1302825

1304838

13/0644

1294500

1303iOO

1300740

1301835

1304500

1302823

1304100

1293800

1294600

13/0100

1304848

1305900

1294838

1301 000

1301055

1295949

1305900

1294400

1300/04

1300700

1301055

1305900

1295500

1294500

1294407

1294407

1293500

1294500

1300/08

1301000

1294400

1304818

1294407

1294400

1301835

13/0800

13/0600

1304044

1304818

1301000

1301000

1304818

1294838

1302700

1305300

1304900

1295842

13/0100

1300900

1305000

1305700

1302048

1303t 00

bossiaeoides

bossiaeoides

bossiaeoides

bossiaeoides

bossiaeoides

bladhii

bladhii

polyphyllareptansconvergensdiversifolius

spectabilisspentabilistuberCUIatus (3r)

,

I.

cernua

tomentosa

tomentosa

tomentosa

arborescens

asperataasperata

Page 162: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Buchnera

Buchnera

Buchnera

Buchnera

Buchnera

Buchnera

Buchnera

Buchnera

Buchnera

Buchnera

Buchnera

Buchnera

Buchnera

Buchnera

BulbostylisBurmannia

ByblisGalanusGalanusGalanusCajanusCajanusGalanusCajanusGalanusGalanusCajanusGalanusCajanusGalanusCajanusCajanusCajanusGalanusGalanusGalanusGalanusCajanusGalanusCajanusCajanusGalandrinia

Galandrinia

CallicarpaCallicarpaCallicarpaCallicarpaCallicarpaCallicarpaCallicarpaCallicarpaCallitris

Callitris

Callitris

Callitris

Callitris

CalophyllumCalophyllumCalotropis

asperatalinearis

linearis

linearis

linearis

linearis

rainosissima

urncifolia

SCROPHULARIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

SCROPHULARIACEAE

CYPERACEAE

BURMANNIACEAE

BYBLIDACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

PORTULACACEAE

PORTULACACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

CUPRESSACEAE

CUPRESSACEAE

CUPRESSACEAE

CUPRESSACEAE

CUPRESSACEAE

CLUSIACEAE

CLUSIACEAE

AscKEouADACEAE

6

barbata

jinjflora

acutifolius

acutifolius

acutifolius

acutifolius

acutifolius

acutifolius

cinereus

IatisepalusIatisepalusmarmoratus

pubescenspubescenspubescensreticulatus

reticulatus

reticulatus

reticulatus

reticulatus

reticulatus

1305/994

1605/994

1305/994

1405/994

9051994

1205/994

1305/994

8031989

1405/994

9051994

1405/994

1405/994

9051994

1403/989

9031989

1605/994

1405/994

1605/994

1005/994

1105/994

1505/994

1103/989

1303/989

1305/994

I0051994

2202/994

1405/994

1405/994

1305/994

1205/994

9051994

1205/994

1605/994

1303/989

1303/989

2702/986

1405/994

1205/994

8031989

303198'

1505/994

8031989

1202/991

2602/986

1605/994

1505/994

1603/989

203198'

4031989

1103/989

1303/989

1505/994

2031989

1305/994

2031989

1505/994

1108/983

1108/983

1504/987

144100

150124

144100

150406

14/833

143521

1441 00

150800

144728

142222

150406

150406

1422/3

152800

15/500

150124

150345

150500

14/900

142000

150430

15/400

145400

143455

150500

143951

150406

144926

143851

144500

1422/6

143522

150124

144700

144500

152600

144743

1445/2

150800

143400

150440

152700

14/900

152600

150500

150430

14/900

144100

144900

15/400

145400

150300

144300

144100

144300

150420

14/700

14/700

14/400

1305300

1305900

1305300

1302826

1304001

1301848

1305300

1303500

1300/04

1304838

1302826

1302826

1304847

1304900

1300100

1305900

1302823

1301000

1300600

1301100

1303218

1302300

1304100

1301835

1301 000

1294838

1302826

1295923

1301055

1304800

1304844

1295949

1305900

1304400

1305000

13/0600

1300/08

1304759

1303500

1300900

1302830

1302600

1305600

13/0600

1301000

1303218

13/0100

1294400

1294600

1302300

1304100

1303100

1294500

1305300

1294500

1302824

1301000

1301000

13/0200

^

I

,

uniflora

uniflora

candicans

candicans

candicans

candicans

candicans

candicans

candicans

candicans

intratropicaintratropicaintratropicaintratropicaintratropicas il

soulattri

procera *

.:

^

.

I

^

I

^

Page 163: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

,

CalotropisCalycopeplusCalytrixCalytrixCalytrixCalytrixCalyirixCalylrixCalytrixCalytrixCalylrixCalyirixCalytrixCalytrixCalytrixCalylrixCalytrixCalytrixCalytrixCalyirixCalylrixCalytrixCalylrixCalyirixCalytrixCalytrixCalytrixCalytrixCalylrixCalylrixCan ariumCan arium

Can ariumCan ariumCan arium

Can avaliaCanavaliaCanscora

Canscora

Canscora

Canscora

Canscora

CanthiumCanthiumCanthium

CapparisCapparisCaralliaCaralliaCaralliaCaralliaCaralliaCara!Iia

CardiospermumCarpentariaCarpentariaCarpentariaCarpentariaCarpentaria

,

proceracollinus

achaeta

achaeta

achaeta

achaeta

achaeta

achaeta

browniibrowniibrowniibrownii

browniibrowniibrowniibrowniibrownii

exstipulataexstipulataexstipulataexstipulataexstipulataexstipulataexstipulataexstipulataexstipulataexstipulataexstipulatamegaphylla

I

AscKEouADACEAEEUPHORBIACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEBURSERACEAEBURSERACEAEBURSERACEAEBURSERACEAEBURSERACEAEFABACEAEFABACEAEGENTIANACEAEGENTIANACEAEGENTIANACEAEGENTIANACEAEGENTIANACEAERUBIACEAERUBIACEAERUBIACEAECAPPARACEAECAPPARACEAERHIZOPHORACEAERHIZOPHORACEAERHIZOPHORACEAERHIZOPHORACEAERHIZOPHORACEAERHIZOPHORACEAESAPINDACEAEARECACEAEARECACEAEARECACEAEARECACEAEARECACEAE

7

.

.

1508/961

1405/994

1205/994

1202/991

8031989

1505/9941505/9941005/9941505/9941405/9941205/9941305/99490519941305/9941405/994

1605/994

1005/9941405/9941205/9941305/99490519941505/99490519891202/99j

2202/99480319891205/9941005/9941405/99410619951303/9891505/994

1305/9941303/9891505/9941005/9941205/9948051994

1305/9941207/99290519941505/99430319891105t 9941005/9942511/9871105/9941505/9941108/9831305/9941405/9941005/9941305/99440319891205/99420319891303/9891105/9941305/994

14/7001449/914352214/900

15/100150400

1505/5

14/835

144743144728144503

143851

1422/6

143851

144926

150124

14/9001447281445/2143851

1422/615030015270014/900

143951

150800

143521

14/835

144728141800

145800

150430

144100

145400150440

142130143521

142200

14385t

1432001422/3

15040014240014200014200014400014200014492614/70014410015030014/835143455

1449001445/2144000145800142000143455

I

.

13/0800

1295842

12959491305500

1305000I3100001302845

13040001300/051300/041304757

1301055

1304844

1301055

1295923

130540013006001300/0413047591301055

1304844

1303100

1300000130560012948381303500

1295952

13040001300/04130570513007001303218130530013041001302830

13048381295952

13048001301055

1303800

1304847

131000013003001301100130105413045001301100129592313010001305300130310013040001301835129460013047591294500130070013010541301835

australianumaustralianumaustralianum

australianumaustralianum

papuanapapuanadiffusa

diffusa

diffusa

diffusa

diffusa

lucidumschultzii^

Iasianthaumbonata

brachialabrachialabrachialabrachiatabrachiatabrachialahatcacabumacuminataacuminataacuminataacuminataacuminata

Page 164: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Cartonema

Cartonema

Cartonema

Cartonema

Cartonema

Cartonema

GassythaCassythaGassythaCathormion

Cathormion

Geltis

Genchrus

Genchrus

Genchrus

Genchrus

Genchrus

Centranthera

Centranthera

Centranthera

Centranthera

CentrolepisCentrolepisCeratophyllumCeriopsCeriopsChainaecristaChainaecrista

Chainaecrista

ChainaecristaChainaecristaChainaecrista

Chainaecrista

Chainaecrista

Cheilanthes

Cheilanthes

Cheilanthes

CheilanthesCheilanthes

Cheilanthes

CheilanthesCheilanthes

CheilanthesCheilanthesCheilanthesCheilanthesCheilanthesCheilanthesCheilanthesCheilanthesCheilanthesCheilanthesCheilanthesCheilanthesCheilanthesCheilanthesCheilanthesChionachne

Chlorophytum

spicatumspicatumspicatumspicatumtrigonospermum

capillarisfiliform is

filiformis

umbellatum

umbellatum

philippensiselymoideselymoideselymoideselymoideselymoidescochinchinensis

cochinchinensis

cochinchinensis

cochinchinensis

exserta

exserta

demersum

australis

australis

absus

absus

absus

in jinosoides

in jinosoides

in jinosojdes

nictitans

COMMELINACEAECOMMELINACEAE

COMMELINACEAE

COMMELINACEAE

COMMELINACEAE

COMMELINACEAE

LAURACEAE

LAURACEAE

LAURACEAE

MIMOSACEAE

MIMOSACEAE

ULMACEAE

POACEAE

POACEAE

POACEAE

ROACEAE

POACEAE

SCROPHULARIACEAE

SCROPHULARIACEAESCROPHULARIACEAE

SCROPHULARIACEAE

CENTROLEPIDACEAE

CENTROLEPIDACEAEGENATOPHYLLACEAERHIZOPHORACEAE

RHIZOPHORACEAECAESALPINIACEAECAESALPINIACEAECAESALPINIACEAECAESALPINIACEAE

CAESALPINIACEAECAESALPINIACEAECAESALPINIACEAE

CAESALPINIACEAESINOPTERIDACEAESINOPTERIDACEAE

SINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAESINOPTERIDACEAEPOACEAE

LILLIACEAE

8

1102/991

1205/994

2202/994

1405/994

2602/986

8031989

1505/994

1405/994

1205/994

1407/977

1407/977

1603/989

1405/994

1805/952

1103/989

1305/994

9051994

1605/994

1305/994

1405/994

9051994

1605/994

1105/994

1205/994

2302/994

2308/987

1405/994

2102/994

1305/994

1205/994

1605/994

1405/994

1005/994

1505/994

9031989

1405/994

8031989

1205/994

2031989

9051994

3031989

2402/989

3031989

3031989

2702/986

1405/994

1405/994

2602/986

3031989

2302/994

1610/988

2031989

3031989

1403/989

1610/988

2031989

1505/994

8031989

2202/994

14/700

144400

144403

150345

152600

152700

150400

144728

142858

152300

152300

14/900

150300

144400

150800

143455

142130

150124

144100

150406

14/833

150124

142000

143105

1436/4

15/300

150248

144400

143455

14385i

150659

144100

142000

150300

I51500

150300

150800

144406

144300

14/833

142400

14/500

143400

143400

152800

150300

150300

152600

143400

144901

14/400

144100

143400

152800

14/400

144100

1505/5

144900

143951

1305700

1304800

1294407

1302823

13/0600

1302600

1310000

1300/04

1300607

1301 700

1301700

13/0100

1303100

13/0700

1303400

1301 835

1304838

1305900

1305300

1302826

1304001

1305900

1301 100

1300744

1294804

1294000

1303036

1295600

1301835

1301055

1302319

1305400

1301054

1303iOO

1300100

1303100

1303500

1304818

1294500

1304001

1300300

1304100

1300200

1300900

13/0700

1303100

1303100

13/0600

1302000

1295840

1300600

1294400

1300200

1304900

1300600

1294400

1302845

1305000

1294838

.

brownii

brownii

brownii

caudata

caudata

contiguacontiguacontiguacontiguacontiguafragillimafragillimahirsuta

praetermissapumilio

I

,.

,

I

.

cyathopodalaxum

I

I

^

,

Page 165: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

,

,

Christella

Christella

Christia

CISsus

Cissus

Cissus

Cissus

Cissus

Cleome

Cleome

Cleome

Clerodendrum

Clerodendrum

Clerodendrum

Clerodendrum

Clerodendrum

Clerodendrum

Clitoria

CochlospermumCochlospermumGolocasia

Coinmelina

Coinmelina

Coinmelina

Corehorus

Corehorus

Corehorus

Corehorus

Cressa

Cressa

Cressa

Cressa

Crinum

Crotalaria

Crotalaria

Crotalaria

Crotalaria

Crotalaria

Crotalaria

Crotalaria

Crotalaria

Crotalaria

Crotalaria

Orotalaria

Crotalaria

Crotalaria

Crotalaria

Orotalaria

Crotalaria

Crotalaria

Crotalaria

Crotalaria

Crotalaria

Crotalaria

Crotalaria

Croton

Croton

Oroton

Croton

,

:

dentata

dentata

australasica

adnata

reniformis

reniformis

reniformis

reniformis

tetrandra

tetrandra

viscosa

costatum

floribundum

floribundum

floribundum

floribundum

floribundum

australis

fraseri

fraseri

esculenta

ensifolia

ensifolia

ensifolia

sidoides

sidoides

:

THELYPTERIDACEAE

THELYPTERIDACEAE

FABACEAE

VITACEAE

VITACEAE

VITACEAE

VITACEAE

VITACEAE

CAPPARACEAE

CAPPARACEAE

CAPPARACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

VERBENACEAE

FABACEAE

BIXACEAE

BIXACEAE

ARACEAE

COMMELINACEAE

COMMELINACEAE

COMMELINACEAE

TILIACEAE

TILIACEAE

TILIACEAE

TILIACEAE

CONVOLVULACEAE

CONVOLVULACEAE

CONVOLVULACEAE

CONVOLVULACEAE

LILLIACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAEFABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAEFABACEAEFABACEAE

FABACEAE

EUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAE

EUPHORBIACEAE

9

I.

,

,

1205/994

1207/992

1205/994

4031989

9031989

1103/989

1303/989

1303/989

1403/963

1303/989

1305/994

1205/994

1403/989

1005/994

2031989

2602/986

2202/994

2402/989

1405/994

1202/991

1603/989

2402/989

3031989

1303/989

1405/994

1305/994

1202/991

2202/994

9051989

1407/977

2707/949

1908/949

It 051994

1305/994

1305/994

1305/994

1405/994

10/1856

9051994

8031989

1405/994

1855

1505/994

1205/994

2102/994

2702/986

1510/964

2031989

1205/994

9051994

1405/994

1505/994

1405/994

1305/994

1005/994

9031989

1102/991

1305/994

o

1445t 2

1431 00

1445/2

144900

15/900

15/400

145400

144500

142800

145500

144100

143521

152600

142000

144300

152500

143951

14/500

144926

14/900

142200

14/500

143400

144500

1449/9

144100

14/900

144403

152900

152300

151000

152100

142548

144406

143851

144100

150406

143500

1422/3

152700

150406

152600

150440

144400

144400

152500

153000

144100

1445/2

142222

150300

1505/5

150300

1435/2

14/900

15/900

14/700

144100

145300

*

cretica

cretica

cretica

cretica

an gustifoliumalata

alata

alata

alata

brevis

calycinacrispatacrispatacrispatamedicagineamontana

montana

montana

novae-hollandiaenovae-hollandiaeretusa

retusa

retusa

retusa

verrucosa

verrucosa

1304757

1303800

1304759

1294600

1301100

1302300

1304100

1305000

1305500

1300400

1305300

1301848

13/0600

1301100

1294500

13/0900

1294838

1304100

1295923

1305500

1304800

1304100

1300900

1305000

1295842

1305300

1305500

1294407

1301000

1301700

1300000

I301700

1302500

13/0644

1301055

1305300

1302826

1295000

1304847

1302600

1302826

1300600

1302830

1304800

1295600

13/0900

1300500

1294400

1304759

1304838

1303100

1302845

1303100

1301850

1300600

1301100

1305700

1305300

1301700

;

.

,

.

am hemicus

arnhemicus

arnhemicus

am hemicus

Page 166: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Croton

Croton

Croton

CryptocaryaCryptocaryaCucumis

Cucumis

Cucumis

Cucumis

Cucumis

Guilen

CyanotisCyanthilliumCyanthilliumCycasCycasCycasCycasCycasCycasCycasCycasCycasCycasCycasCyclosorusCyclosorusCyclosorusCyclosorusCymbidiumGymbopogonGymbopogonGymbopogonGymbopogonGymbopogonGymbopogonGymbopogonGymbopogonCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperus

am hemicus

arnhemicus

am hemicus

cunning hamiicunning hamiimelo

melo

melo

melo

melo

badocanumCOMMELINACEAEaxillarisASTERACEAEcinereum

ASTERACEAEcinereum

mmwestern Top End""" CYCADACEAE"""Western Top Endmu' CYCADACEAE

CYCADACEAEangulataCYCADACEAEangulataCYCADACEAEangulataCYCADACEAEarmstrongiiCYCADACEAEarmstrongiiCYCADACEAEcalcicolaCYCADACEAEcalcicolaCYCADACEAEpruinosaCYCADACEAEpruinosaTHELYPTERIDACEAEinterruptus (3rC)THELYPTERIDACEAEinterruptus (3rC)THELYPTERIDACEAEinterruptus (3rC)THELYPTERIDACEAEinterruptus (3rC)ORCHIDACEAEcanaliculatumPOACEAEbombycinusPOACEAEbombycinusPOACEAEprocerusPOACEAEprocerusPOACEAEprocerusPOACEAEprocerusPOACEAEprocerusPOACEAEprocerusCYPERACEAEaquatilisCYPERACEAEaquatilisCYPERACEAEaquatilisCYPERACEAEaquatilisCYPERACEAEconicus

CYPERACEAEcunning hamiiCYPERACEAEcuspidatusCYPERACEAEexaltatusCYPERACEAEhaspanCYPERACEAEhaspanCYPERACEAEhaspanCYPERACEAEholoschoenusCYPERACEAEholoschoenusCYPERACEAEholoschoenusCYPERACEAEholoschoenusCYPERACEAEIria

CYPERACEAEmacrostachyosCYPERACEAEmacrostachyosCYPERACEAEmacrostachyosCYPERACEAEmicrocephalusCYPERACEAEmicrocephalus

EUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAELAURACEAELAURACEAECUCURBITACEAECUCURBITACEAECUCURBITACEAECUCURBITACEAECUCURBITACEAE

10

o

1611/9881103/9893031989

3031989

1603/9891103/9898031989

1403/989

1303/9891805/9522602/9861605/9941505/9941/10/98011019881/10/98091019801/10/9801005/9942402/98990519959051995905199590519951005/9941405/9941405/994403198980319891607/9882105/9521805/95240319891005/9941505/9941305/9941305/99480519941305/9941105/9941205/9942602/9861505/9941405/99490519941105/9941605/9941205/9941305/9942602/9861005/9941605/9941205/9941305/9941004/99090319891605/9941505/994

152000

14/400

15/400

143100

14240014/900150800150800

152800

144500142800

152600150500150545

14200014250014200014200014210014200014/500152430

152430152448152448142130150300150345

142300

15/100144300145600144400

14490014/835

150420

143455

143455

142200144726142000144500

152600143851

1449261422/61420001506591435211444061525001420001506591445001445/81427001529001505001505/5

13010001300600130230013005001300300

13/0100

1303400

1303500

1304900130500013/020013/060013010001302825

129380012942001293800129380012935001301054

13041001294030129403012938421293842

1304838130310013028231293600130500013/0700130480013/0700129490013040001302824

1301835

1301835

130480013/0205

1301100130480013/06001301 055

129592313040441301 1001302319129595213,064413/06001301 1001302319130480013/07181294900130100013010001302845

I

I

,

.

I'

:

*

I

*

I

I

Page 167: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

I

:

CyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusCyperusDactylocteniumDactylocteniumDecaisnina

Decaisnina

Decaisnina

Decaisnina

Dendrobium

Dendrobium

Dendrobium

Dendrobium

Dendrobium

DendrophthoeDendrophthoeDenhamia

Denhamia

Denhamia

Dentella

Desmodium

Desmodium

Desmodium

Desmodium

Desmodium

Desmodium

Desmodium

Desmodium

Desmodium

Desmodium

Dichanthium

Dichanthium

DiclipteraDiclipteraDiclipteraDiclipteraDiclipteraDiclipteraDiclipteraDiclipteraDicranopterisDicranopterisDicranopterisDicranopterisDigitaria

.

polystachyos (3rC)portae-tartariportae-tartariportae-tartariportae-tartariportae-tartaripulchellussexflorus

viscidulus

viscidulus

viscidulus:

I

I'

CYPERACEAECYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAECYPERACEAE

CYPERACEAE

CYPERACEAECYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

POACEAE

POACEAE

LORANTHACEAE

LORANTHACEAE

LORANTHACEAE

LORANTHACEAE

ORCHIDACEAE

ORCHIDACEAE

ORCHIDACEAE

ORCHIDACEAE

ORCHIDACEAE

LORANTHACEAE

LORANTHACEAE

CELASTRACEAE

CELASTRACEAE

CELASTRACEAE

RUBIACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

POACEAE

POACEAE

ACANTHACEAE

ACANTHACEAE

ACANTHACEAE

ACANTHACEAE

ACANTHACEAE

ACANTHACEAE

ACANTHACEAE

ACANTHACEAE

GLEICHENIACEAE

GLEICHENIACEAE

GLEICHENIACEAE

GLEICHENIACEAE

POACEAE

11

aegyptium *radulans

petiolatasignatasignatasignataaffine

affine

affine

affine

affine

acacioides

odoritocalyxobscura

obscura

obscura

repensbiarticulatum

brownii

brownii

heterocarponheterocarponinuelleri

inuelleri

inuelleri

inuelleri

trichostachyumfecundum

sericeum

armata

armata

armata

armata

armata

armata

armata

armata

linearis (3rC)linearis (3rC)linearis (3rC)linearis (3rC)bicornis

1405/994

1005/994

2031989

1611/988

3031989

2402/989

1605/994

1305/994

1505/994

1305/994

1505/994

1405/994

1405/994

1205/994

1205/994

1405/994

1505/994

1505/994

2102/994

1305/994

1205/994

1708/949

1708/949

2402/989

2031989

1603/989

3031989

1108/983

1405/994

6/1/980

1205/994

1103/989

1605/994

1108/986

1305/994

2402/989

8031989

1505/994

1005/994

2002/994

1305/994

1505/994

1005/994

1405/994

9051994

1805/952

8051994

9031989

1205/994

1303/989

1103/989

4031989

1303/989

1305/994

1305/994

1205/994

1105/994

1505/994

1205/994

150406

14/900

144100

14/400

143400

14/500

150659

143851

144707

144143

150400

144743

144743

1443/2

1443/2

150345

150420

150400

144549

143851

144400

152100

152100

14/500

144000

142200

143400

14/700

144926

150500

1445/2

150800

150440

153000

144100

14/500

150800

150440

142000

144549

1435/2

150420

14/835

1449/9

1422/3

144000

142200

15/500

144406

145500

15/400

144900

14/500

143455

14385i

144502

142000

1505/5

144406

1302826

1300600

1294400

1300600

1300900

1304100

1302319

1301055

1300045

13/0836

1310000

1300/05

1300/08

1304759

1304759

1302823

1302824

1310000

1295656

1301055

1304800

1305600

1305600

1304100

1294500

1304800

1302000

1301000

1295923

1304500

1304759

1303400

1301020

1303400

1305300

1304100

1303500

1302830

1301100

1295656

1301850

1302824

1304000

1295842

1304847

1304000

1304800

1300100

1304818

1300400

1302300

1294600

1305000

1301835

1301055

1304800

1301100

1302845

1304818

.

Page 168: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

DigitariaDigitariaDigitariaDigitariaDimeria

Dimeria

Dimeria

Dimeria

Dimeria

Dimeria

Dioscorea

Dioscorea

DiospyrosDiospyrosDiplocyclosDipteracanthusDistichostemon

Distichostemon

Distichostemon

Distichostemon

Distichostemon

Distichostemon

Distichostemon

Dodoriaea

Dodoriaea

Dodoriaea

Dodoriaea

Do Iichandrone

Do Iichandrone

Drosera

Drosera

Drosera

Drosera

Drosera

Drosera

Drosera

Drosera

Drosera

Drosera

Drosera

Drosera

Drosera

DrypetesDysoxylumDysoxylumDysphaniaECtrosia

ECtrosia

ECtrosia

Eatrosia

ECtrosia

ECtrosia

Eatrosia

ECtrosia

ECtrosia

ECtrosia

ECtrosia

Eatrosia

ECtrosia

breviglumisciliaris

gibbosastenostachyaornithopodaornithopodaornithopodaomithopodaornithopodaomithopodatransversa

transversa

calycanthacordifolia

palmatusaustralasicus

his pidulushis pidulushis pidulushis pidulushis pidulushis pidulushis piduluslanceolata

lanceolata

oxypteraplatypterafiliform is

filiform is

burmanni

burmanni

burmanni

burmanni

indica

indica

indica

indica

indica

indica

indica

lariata

petiolarisdeplancheiIatifolium

Iatifolium

plantaginellaagrostoidesagrostoidesagrostoidesagrostoidesdanesii

IeporinaIeporinaIeporinaIeporinaIeporinaIeporinaIeporina

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

ROACEAE

POACEAE

POACEAE

POACEAE

POACEAE

DIOSCOREACEAE

DIOSCOREACEAE

EBENACEAAE

EBENACEAAE

CUCURBITACEAE

ACANTHACEAE

SAPINDACEAE

SAPINDACEAE

SAPINDACEAE

SARINDACEAE

SAP!NDACEAE

SAPINDACEAE

SAPINDACEAE

SAPINDACEAE

SARINDACEAE

SAPINDACEAE

SARINDACEAE

BIGNONIACEAE

BIGNONIACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

RUTACEAE

EUPHORBIACEAE

MELIACEAE

MELIACEAE

CHENOPODIACEAE

POACEAE

ROACEAE

POACEAE

ROACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

12

1605/994

9051994

1503/961

1205/994

1305/994

1205/994

1405/994

1105/994

1205/994

1505/994

9031989

2031989

1108/983

2402/989

1603/989

9051994

1505/994

1405/994

2031989

1405/994

3031989

2031 989

2702/986

1605/994

1103/989

2108/949

1305/994

9051994

1202/991

1205/994

2302/994

1405/994

1505/994

1205/994

1305/994

1205/994

1105/994

1405/994

1505/994

2704/995

9051989

1305/994

2031989

4031989

4031989

9051989

1205/994

1405/994

1305/994

1305/994

1305/994

1305/994

1205/994

1605/994

1005/994

1605/994

1207/994

1005/994

1205/994

1455t O

1422/3

14/800

1443/2

144726

143522

144926

142000

144500

1505/5

15/900

144100

14/700

141500

14/900

1422/3

144703

150400

144000

150406

143400

144100

153000

150500

15/400

144800

144100

142222

14/700

144502

14490t

150345

150400

144503

144726

1443/2

142548

150406

150400

14/800

152700

144100

144300

142300

142300

152900

143527

1449/9

144100

1435/2

144100

144726

143522

150124

142224

150659

143521

14/835

1445/2

13/0223

1304847

1302800

1304759

13/0205

1295949

1295923

1301100

1304800

1302845

1301100

1294400

1301000

1304100

13/0100

1304847

1300031

1303/30

1294500

1302826

1300900

1294400

13/0800

1301000

1302300

13/0200

1305300

1304838

1305600

1304800

1295840

1302823

1310000

1304757

13/0205

1304759

1302500

1302826

1310000

1305705

1300000

1305300

1294500

1293500

1293600

1301000

1295949

1295842

1305300

1301850

1305300

13/0205

1295949

1305900

1302048

1302319

1295952

1304000

1304759

I

J

^

,

.

.

.

.

.

I

t

^

I

Page 169: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

,

^

* ECtrosia

ElaeocarpusEleocharis

Eleocharis

Eleocharis

Eleocharis

Eleocharis

Eleocharis

Eleocharis

Eleocharis

Eleocharis

Eleocharis

Eleocharis

Eleocharis

Eleocharis

Eleocharis

Eleocharis

ElytrophorusElytrophorusElytrophorusElyirophorusElylrophorusEragrostisEragrostisEragrostisEragrostisEragrostisEragrostisEragrostisEragrostisEragrostisEragrostisEragrostisEragrostisEragrostisEragrostisEragrostisEragrostisEriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

,

:

..

arnhemicus

A56424

01486

acutangulacaespitosissimacaespitosissimacaespitosissimageniculatageniculatanuda

nuda

nuda

ochrostachyssundaica

sundaica

,

^

.I

I

POACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

ELEAOCARPACEAE

POACEAE

POACEAE

ROACEAE

POACEAE

POACEAE

POACEAE

ROACEAE

POACEAE

POACEAE

ROACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

ROACEAE

POACEAE

POACEAE

ROACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

13

,

,

,:

spicatusspicatusspicatusspicatusspicatusA42909

pubescenspubescensrigidiusculaschultzii

schultzii

spamnoidestenella

tenellula

tenellula

tenellula

tenellula

tenellula

1305/994

3031989

1405/994

1205/994

1405/994

1205/994

1405/994

1205/994

9051994

1505/994

1605/994

1105/994

1205/994

1305/994

1205/994

1405/994

1205/994

1405/994

1405/994

1205/994

1605/994

1101988

1505/994

1405/994

1505/994

1005/994

1205/994

1005/994

1605/994

1505/994

1305/994

8031989

1605/994

1505/994

1505/994

1205/994

1305/994

1305/994

8051994

2602/986

1205/994

1205/994

1205/994

1405/994

1305/994

1205/994

1005/994

1205/994

1405/994

2402/994

1605/994

2102/994

2603/988

1108/983

1405/994

1205/994

1405/994

1205/994

1305/994

144726

142400

144926

143105

150345

142858

144926

143105

1422/6

150400

150124

142000

143521

143455

142858

150300

1445/2

144728

1449/9

144500

150659

142500

150430

150300

150400

142000

142858

14/835

150659

1505/5

144406

15/200

150659

150400

150400

1445/2

144726

144358

142200

152600

143521

144503

143522

150345

1435/2

142858

142224

143105

144926

144901

145510

144400

145400

14/700

144728

144400

144728

143521

144358

13/0205

1300300

1295923

1300744

1302823

1300607

1295923

1300744

1304844

1310000

1305900

1301 100

1295952

1301835

1300607

1303100

1304759

1300/04

1295842

1304800

1302319

1294900

1303218

1303100

1310000

1301 100

1300607

1304000

1302319

1302845

13/0644

1303400

1302319

1310000

1310000

1304759

I310205

13/0615

1304800

I310600

1295952

1304757

1295949

1302823

1301850

1300607

1302048

1300744

1295923

1295840

13/0223

1295600

1300000

1301000

1300/04

1304800

1300/04

1295952

13/0615

5

avenacea

avenacea

avenacea

basedowii

basedowii

basedowii

basedowii

burkittii

burkittii

burkittii

capillariscapillarisciliata

ciliata

ciliata

festucacea

filiformis

me Iicacea

nodosa

obtusa

schultziana

.

.

^

Page 170: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

EriachneEriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

Eriachne

EriocaulonEriocaulonEriocaulon

EriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriocaulonEriochloa

ErythrinaErythrophleumErythrophleum

schultzianaschultzianaschultzianaschultzianaschultziana

schultzianaschultziana

stipaceasuicata

triseta

triseta

triseta

triseta

cinereum

cinereum

cinereum

cinereum

cinereum

cinereum

concretum

depressumdepressumdepressumdepressumdepressumfistulosum

fistulosum

fistulosum

k

k

lividum

monoscapum

pusillumpusillumscullioniisetaceum

setaceum

setaceum

setaceum

setaceum

setaceum

setaceum

setaceum

spectabilespectabilespectabilespectabiletortuosum

tortuosum

tortuosum

tortuosum

tortuosum

unicursum

POACEAEPOACEAEROACEAEROACEAEPOACEAEPOACEAEROACEAEROACEAEPOACEAEPOACEAEPOACEAEPOACEAEPOACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEERIOCAULACEAEPOACEAEFABACEAECAESALPINIACEAECAESALPINIACEAE

14

1505/9941205/9941205/9941005/9941905/9529051994

1305/9941205/9941405/9941405/9941405/9941005/99490519941205/9941405/9941305/9941005/9941605/994

1205/994

9051994

1405/994

1405/994

1405/9941105/9941005/9941305/9941005/9941605/99430319891405/994

o

1101855

1105/99420319892302/9941405/9941405/9941405/9941005/9941505/9941609/99430319891207/9941205/9941005/9941605/9941205/9941305/9941603/98930319891505/9941005/9941205/9941205/9941205/9942102/9941207/9921207/9921305/994

144707

142858

144502142000

14350014/8331435/2143105

150345

144728144243142000

14/833

1445/2

144743

144406

142000

150659

143521

14/833144743

144743144728142000142000

144726

14/900150659

143400

150406

144100144100

142000

144300144901

144743144728144926142224

150430150659

142600

143521

144503

142000150659143521

144726

14220014340015041014/8351445031443/2142858144549143400143300144100

1300045

1300607

1304800130110013/0700

1304001

1301850

1300740

1302823

1300/04

1300/05

13011001304001

13047591300/05

13/0644

1301 100

1302319

1295952

1304001

1300/05

1300/08

1300/04

1301100

1301100

13/0205

13006001302319

1302000

130282612947001294700

1301100129450012958401300/081300/041295923130204813032i81302919130020012959521304757

13011001302319129595213/020513048001300900130282513040001304757130475913006071295656130390013039001305300

tI

;

,

.

.

pseudoacrotrichavespertiliochiorostachyschlorostachys

.

.

^

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,

.

Page 171: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

,

.

.

ErythrophleumErythrophleumEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptus

,

.

chiorostachyschlorostachysabbreviata

abbreviata

apodophyllaapodophyllaaspera

bigaleritableeseri

bleeseri

bleeseri

bleeseri

brachyandrabrachyandrabrachyandracarnaldulensis

contentflora

conferIiflora

cupularisdichromophloiadichromophloiadichromophloiadichromophloiaferrugineafoelscheana

foelscheana

grandifoliaherbertiana

herbertiana

Iatifolia

jarifolia

Iatifolia

Iatifolia

Iatifolia

miniata

miniata

miniata

miniata

miniata

miniata

miniata

papuana

patellarisphoeniceaphoeniceaphoeniceaphoeniceapolycarpapolycarpapruinosa

ptychocarpaptychocarpaptychocarpaptychocarpateatifica

tectifica

tentifica

teatifica

terminalis

.

:

;'

^

CAESALPINIACEAE

CAESALPINIACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAEMYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

MYRTACEAE

15

*

I1021991

1305/994

2205/952

2602/986

1305/994

1205/994

1605/994

1205/994

6091970

1505/994

1305/994

1805/957

4101989

1303/989

3031989

1407/977

4061952

1005/994

1405/994

1605/994

1101855

1005/994

1505/994

8051994

8051960

9051994

2105/952

1505/994

1303/989

8051994

1305/994

1207/994

1205/994

1405/994

1405/994

1403/989

4051957

1405/994

1305/994

1605/994

1005/994

1605/994

9051994

1205/994

4101989

9051989

1405/994

1205/994

1002/991

2061967

2702/986

1005/994

1205/994

1505/994

1205/994

1405/994

2061949

1605/994

2507/965

I

14/700

1435/2

150600

152500

1441 00

143521

150124

143521

143300

150430

144100

15/400

142700

145800

143400

152800

150900

141835

144728

150124

145000

14/835

150420

142200

144500

1422/3

145200

150300

144700

142200

144100

1431 05

143521

150345

1449/9

152600

153000

150300

144100

150406

14/835

150440

1422/3

1445/2

14/800

15/900

150406

143105

143500

145500

152800

142224

143521

150410

143521

150345

143400

150440

142800

I

1305700

1301850

1304300

13/0900

1305300

1301848

1305900

1301848

1305000

1303218

1305300

1305000

1305500

1300700

1300900

1302200

1310000

1304000

1300/04

1305900

1301000

1304000

1302824

1304800

13/0800

1304847

1305700

1303100

1304400

1304800

1305300

1300744

1301848

1302823

1295842

13/0600

13/0900

1303/30

1305300

1302826

1304000

1301020

1304847

1304759

1305700

1295500

1302826

1300740

1304000

1305500

13/0700

1302048

1295952

1302825

1301848

1302823

13/1000

1301020

1304600

,

.

:

Page 172: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

EucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEucalyptusEUlalia

EUlalia

EUlalia

EuphorbiaEuphorbiaEuphorbiaEuphorbiaEuphorbiaEuphorbiaEuphorbiaEuphorbiaEuphorbiaEuphorbiaEvolvulusExacum

Excoecaria

Excoecaria

ExocarposExocarposExocarposExocarposFagraeaFagraeaFagraeaFagraeaFagraeaFicus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

tetrodonta

tetrodonta

tetrodonta

tetrodonta

tintinnans

tintinnans

tintinnans

umbrawarrensis

MYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEMYRTACEAEPOACEAEPOACEAEPOACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAECONVOLVULACEAEGENTIANACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAEEUPHORBIACEAELOGANIACEAELOGANIACEAELOGANIACEAELOGANIACEAELOGANIACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAE

16

aurea

mackinlayimackinlayidallachyana (3rC)hima *

maconochieanainitchelliana

schizolepisschizolepisschultzii

vachellii

1605/994

1207/9921105/994

1005/994

1405/994

1205/9941505/9942105/9522507/965

1905/9521005/9949051994

1407/977

1405/994

8031989

2402/989

1505/994

1305/9942002/994

1305/994

9051994

1305/994

2402/9891205/9942308/9876081987

1005/9942702/9861505/9941005/994

1305/994

1108/983

2031989

3031989

30319892402/98930319891305/994

1305/9941005/994

1405/994

1305/9941303/9891005/9941303/9891403/9891305/9941605/9941605/9941205/994

1103/9891505/9941407/9771505/9941407/9771303/9891609/9691205/9941407/977

alsinoides

tetragonumovalis

parvifoliaIatifolius

Iatifolius

Iatifolius

Iatifolius

racemosa

racemosa

racemosa

racemosa

racemosa

congestacongestacongestacoronulata

hispidahispidahispidahispidaIeucotrichaIeucotrichaIeucotrichaIeucotrichaIeucotrichaIeucotrichaIeucotricha

OPPOsitaOPPOSitaOPPositaOPPositaOPPositaplatypodaracemosa

racemosa

racemosa

150500

143300

142000

14/835

150248

143521

150420

145300

142800

145500

142224

14/833

152300

150248

144900

14/500150440

1435/2144549

144100

142222

144726

14/5001443/215/300153000142000

153000

15044014/835

143851

14/700144000

143400

14340014/500

143400

1435/2

1435/2

142130

150300

144100

145500

142130144700

152800

143455

150500

150124

144502

1508001505/5

152500

150430152500

145800152500144406152800

^

13010001303900130,054

13040001303036

1295952

1302824

1305600

1304600

1305500

13020481304001

1301700

1303036

1305000

1304100

1302830

1301850

1295656

13053001304838

13/0205

13041001304759

12940001302400

1301054

13/0700

13028301304000

1301055

1301000

1294500

1300200

1300200

1304100

1300900

1301850

13018501304838

1303100

1305300

1300400

1304838130440013049001301835130,0001305900130480013034001302845

1301800130321813018001300700130200013048181302200

I

^

.

I

;

.

.

,

,

I

I

.

.

I~

I

I

Page 173: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

,

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

Ficus

FimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisF1mbristylisFimbristylisFimbristylisFimbristylisF1mbristylisF1mbristylisFimbristylisFimbristylisF1mbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisF1mbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisF1mbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisF1mbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylis

subpuberula

.

virens

virens

virens

,

A64431acicularis

acuminata

acuminata

acuminata

arthrostyloidesblakei

caespitosacardiocarpacephalophoracompactacompactacoinpositacymosadensa

densa

depauperatadichotoma

dichotoma

furva

furva

furva

fulva

furva

lanceolata

lanceolatalanceolatalanceolatalittoralis

littoralis

microcarya

microcaryanutans

nutans

nutans

nutans

pachypterapachypterapauciflorapauciflorapauciflorapauciflorapauciflorapauciflorapterygospermapunctatapunctatarara

schultzii

simplexsphaerocephalasphaerocephala

I

.

MORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAEMORACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAECYPERACEAE

17

^

,

I

1605/994

1303/989

1305/994

1505/994

1405/994

1405/9941205/994

1305/9941105/994

1305/9941005/994

1305/994

1605/9941405/994

2602/9868031989

1505/9941205/994

1005/994

1505/994

9051995

1305/994

8031989

1305/994

9051994

1205/9941205/994

1005/9941205/9949051994

1303/9891205/9941605/9941105/994303198980519941405/9941005/9941205/9941605/9941205/9941405/9941205/99480319892704/9952702/9861205/9941405/9941105/9941205/9941505/994803198980319891303/9891004/9901205/9941205/99480519941405/994

I

,

150500

145800

143455

1505/5

144728144728

1443/2144100142000

144726

142130

144100

150500150248152600143800

150400

142858

142224

144728

1506/8

144100

143800

144100

1422/6

144502

144400

142224

14450014/833

145500

142858150124

142000143100142200

150248142130

144400150124144406150406143521

14380014/80015280014302214494i

142000143521

1505/5

152700152700145500142600144400143105

142200144926

6

1301 000

1300700

1301835

1302845

1300t 04

1300/04

1304759

13053001301 100

13/0205

1304828

1305300

1301000

1303036

13/06001304400

13100001300607

1302048

1300/04

1294/30

1305300

130440013053001304844

1304800

1304800

13020481304800

1304001

13004001300607

1305900

1301054

13005001304800

13030361304848

1304800130590013048i8130282612959521304400130570513/0700129594912959401301iOO1295952130284513026001302600130040012951001304800130074413048001295923

,

,

Page 174: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

FimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisFimbristylisF1mbristylisFimbristylisFlagellariaFlagellariaFlagellariaFlagellariaFlemingiaFlemingiaFlemingiaFlemingiaFlemingiaFuirena

Fuirena

Fuirena

Fuirena

Fuirena

Fuirena

Fuirena

Fuirena

Fuirena

Fuirena

Fuirena

Fuirena

Fuirena

Galactia

Galactia

Galactia

Gardenia

Gardenia

Gardenia

Gardenia

Gardenia

Gardenia

Geodorum

Geodorum

Geodorum

Germainia

sphaerocephalasphaerocephalasphaerocephalastenostachyatetragonatetragonatetragonatetragonatetragonatetragonatetragonatetragonatetragonatetragonatrigastrocaryatrigastrocaryatrigastrocaryatrigastrocaryatrigastrocaryatristachya

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

FLAGELLARIACEAE

FLAGELLARIACEAE

FLAGELLARIACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

CYPERACEAE

FABACEAE

FABACEAE

FABACEAE

RUBIACEAE

RUBIACEAE

RUBIACEAE

RUBIACEAE

RUBIACEAE

RUBIACEAE

ORCHIDACEAE

ORCHIDACEAE

ORCHIDACEAE

POACEAE

18

2031989

1205/994

2302/994

2102/994

1305/994

1205/994

1205/994

1405/994

1605/994

1005/994

1205/994

1205/994

9051994

1405/994

1305/994

2031989

1305/994

2402/989

1507/994

2602/986

1205/994

1205/994

1305/994

2602/986

1305/994

1205/994

9051995

3031989

3031989

1207/992

1205/994

1005/994

1305/994

1305/994

1405/994

1205/994

1105/994

1505/994

1405/994

1205/994

1405/994

1405/994

9051994

1505/994

4031989

1305/994

1005/994

1505/994

1031986

4101989

1305/994

9051994

1005/994

1305/994

2302/994

1405/994

1205/994

1303/989

1105/994

indica

indica

indica

indica

039269

lineata

lineala

lineata

lineala

ciliaris

ciliaris

ciliaris

ciliaris

ciliaris

nudiflora

umbellata

umbellata

umbellata

umbellata

umbellata

umbellata

umbellata

megalophyllatenuiflora

tenuiflora

resinosa

144300

144400

144901

144100

144726

1445/2

142858

1429/9

150124

142224

144400

144400

14/833

150406

142926

144300

144100

14/500

152047

152600

1443/2

1445/2

144726

152500

143851

144400

1506/8

143400

142600

143100

144406

14/835

1435/2

144726

1449/9

144500

142548

150410

150248

1445/2

150248

150406

14/833

150400

142300

143455

141835

150420

153000

14/800

143851

1422/6

141900

144100

14490t

150300

144406

145500

142000

1294500

1304800

1295840

1295500

13/0205

1304759

1300607

1295842

1305900

1302048

1304800

1304800

1304001

1302826

1295923

1294500

1305300

1304100

1304635

13/0600

1304759

1304759

13/0205

13/0900

1301055

1304800

1294/30

1300900

1300200

1303800

1304818

1304000

1301 850

13/0205

1295842

1304800

1302500

1302825

1303036

1304759

1303036

1302826

1304001

1310000

1293600

1301835

1304000

1302824

13/0800

1305700

1301055

1304044

1300600

1305300

1295840

1303100

1304818

1300400

1301100

.

.

.

.

,

neocaledonicum

neocaledonicum

neocaledonicum

grandiflora

.

;

.

.*

I

,

I

.

Page 175: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

,

^

.

Germainia

Germainia

Germainia

Germainia

Germainia

Germainia

Germainia

Germainia

Germainia

Glochidion

Glochidion

GlycineGlycineGlycineGlycineGlycineGlycosmisGlycosmisGlycosmisGompholobiumGompholobiumGompholobiumGomphrenaGomphrenaGomphrenaGomphrenaGomphrenaGomphrenaGomphrenaGomphrenaGomphrenaGomphrenaGonocarpusGonocarpusGonocarpusGonocarpusGonocarpusGonocarpusGonocarpusGonocarpusGoodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

grandifloragrandifloratruncatiglumistruncatiglumistruncatiglumistruncatiglumistruncatiglumistruncatiglumistruncatiglumisperakenseperakensearenaria

himcaulis

tomentella

tomentella

;

POACEAE

ROACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

POACEAE

EUPHORBIACEAE

EUPHORBIACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

FABACEAE

RUTACEAE

RUTACEAE

RUTACEAE

FABACEAE

FABACEAE

FABACEAE

AMARANTHACEAE

AMARANTHACEAE

AMARANTHACEAE

AMARANTHACEAE

AMARANTHACEAE

AMARANTHACEAE

AMARANTHACEAE

AMARANTHACEAE

AMARANTHACEAE

AMARANTHACEAE

HERNANDIACEAE

HERNANDIACEAE

HERNANDIACEAE

HERNANDIACEAE

HERNANDIACEAE

HERNANDIACEAE

HERNANDIACEAE

HERNANDIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAEGOODENIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAE

GOODENIACEAE

19

sapindoidestrifoliata

trifoliata

subulatum

subulatum

subulatum

canescens

canescens

canescens

conferIa

cunning hamiidiffusa

flaccida

flaccida

parviflora

,

9051994

1205/994

9051994

1605/994

1005/994

1205/994

2105/952

1205/994

1305/994

3031989

1505/994

1405/994

9031989

2602/986

1305/994

1305/994

1405/994

1405/994

2031989

2602/986

9031989

1005/994

9051994

1202/991

1205/994

o

1403/989

8031989

1305/994

1405/994

8051994

2002/994

1205/994

1605/994

1105/994

1605/994

1605/994

2202/994

1605/994

2702/986

1205/994

1105/994

1005/994

1305/994

9051994

1303/994

1605/994

1305/994

1405/994

1305/994

1405/994

2704/995

1405/994

2202/994

1405/994

1305/994

1205/994

1303/989

1605/994

.

.

14/833

143105

1422/6

150124

14/900

144500

145500

143521

1435/2

142600

150420

150406

I51800

152600

14385t

144143

1449/9

144728

144300

152600

15/800

142000

1422/6

14/900

143521

152700

152800

152700

144358

150345

142200

144549

142858

150124

142000

150500

150124

144403

150659

153000

142858

142000

142224

144100

14/833

144726

150124

144100

150345

143455

150345

14/800

144743

143951

144728

143455

144400

144500

150659

1304001

1300740

1304844

1305900

1300600

1304800

13/1000

1295952

1301850

1300200

1302824

1302826

1294000

13/0600

1301055

13/0836

1295842

1300/04

1294500

13/0600

1294000

1301 100

1304844

1305500

1301848

1295700

1304900

1302600

13/0615

1302823

1304800

1295656

1300607

1305900

1301100

1301000

1305900

1294407

1302319

13/0800

1300607

130,100

1302048

1305300

130400i

13/0205

1305900

1305300

1302823

1301835

1302823

1305705

1300/08

1294838

1300/04

1301835

1304800

1305000

1302319

chinensis

chinensis

chinensis

IeptothecusIeptothecusIeptothecusIeptothecusIeptothecusarmstrongianaarmstrongianaarmstrongianaarmstrongianaarmstrongianabicolor

bicolor

bicolor

bicolor

bicolor

coronopifoliacoronopifoliagloeophylla910eophyllahePPIeanahispidaianambaodorinellii

purpurascens

.

Page 176: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

Goodenia

GossypiumGossypiumGossypiumGossypiumGossypiumGrevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grevillea

Grewia

Grewia

Grewia

GymnantheraGymnemaGymnemaGymnemaGymnemaGymnemaGymnemaGyrocarpusHaemodorumHaemodorumHaemodorum

purpurascensredacta

sepalOSasepalOSa

australe

australe

australe

hirsutum *

GOODENIACEAE

GOODENIACEAEGOODENIACEAEGOODENIACEAE

GOODENIACEAEGOODENIACEAE

GOODENIACEAE

MALVACEAE

MALVACEAE

MALVACEAE

MALVACEAE

MALVACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAEPROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAEPROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAEPROTEACEAE

PROTEACEAE

PROTEACEAE

PROTEACEAEPROTEACEAEPROTEACEAE

PROTEACEAEPROTEACEAETILIACEAETILIACEAE

TILIACEAE

AscLEPiADACEAEASOLEPIADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPiADACEAEAscLEPIADACEAEAscLEPiADACEAEHERNANDIACEAEHAEMODORACEAEHAEMODORACEAEHAEMODORACEAE

20

071680

angulataangulatabenthamiana

benthamiana

benthamiana

decurrens

decurrens

decurrens

decurrens

decurrens

decurrens

dryandridryandridryandridryandridryandridryandridryandrihe IiospermaparallelaPIuricaulisprasina

prasina

prasina

pteridifoliapteridifoliapteridifoliarefracta

refracta

refracta

striata

1405/994

2202/994

1806/967

1005/994

1205/994

1405/994

2031989

8031989

1407/977

1407/977

1108/986

1305/994

1605/994

1005/994

1505/994

4101989

1202/991

1202/99'

2031989

1005/994

2202/994

1207/994

1005/994

1505/994

1505/994

2031989

9031989

1005/994

2202/994

1405/994

1605/994

8031989

9081983

2206/988

1005/994

2202/994

2031989

2102/986

1105/994

1205/994

1405/994

1202/991

1305/994

8031989

1405/994

4031989

1205/994

1605/994

9051995

1603/989

2402/989

2031989

9051994

1103/989

9031989

1207/992

1105/994

9031989

1305/994

144100

144403

153000

14/835

1445/2

144743

144100

150800

152500

152500

153000

144406

150124

14/900

150440

14/700

14/900

14/900

144000

142000

144403

143105

14/835

150420

144703

144300

15/800

142000

144403

1449/9

150500

143800

14/700

144000

143851

144403

144100

152600

142000

144400

1449/9

14/900

144000

1521 00

144743

144900

1445/2

150500

1506/8

14/900

14/500

144100

142222

150800

15/500

143200

142000

15/800

144100

1305400

1294407

1305500

1304000

1304759

1300t 05

1294400

1303500

1301800

1301800

1303400

13/0644

1305900

1300600

1302830

1305600

1305500

1305600

1294500

1301 100

1294407

1300744

1304000

1302824

130003t

1294500

1294000

1301iOO

1294407

1295842

1301000

1304400

1300300

1304000

1301 055

1294407

1294400

13/0600

1301100

1304800

1295842

1305500

1305300

13029001300/08

1294600

1304759

1301000

1294/30

13/0100

1304100

1294400

1304838

1303400

1300100

1303800

1301100

1294000

1305300

*

*

,

L

.

nun, ,, ,, I, ,,

retusifoliaretusifolia

oblongageminatumgeminatumgeminatumstenophyllumstenophyllum

,

^

,

americanus

ensifolium

ensifolium

ensifolium

,

.

L

^

I

,

.

.

*

:

Page 177: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

^.

.

.

,

;

,

,

, Appendix 5

Vegetation eommunities

*

I

*

;

.

^

COMMERCIAL-IN-CONFIDENCE

Prepared for: Connell WagnerPrepared by: ERA Environmental Services Pty Ltd

SepU97Job NO XI32

Page 178: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

Appendix 5 Vegetation communities of Bradshaw Station. Species in bracketsindicate co-occurring but subordinate species. Species separated by commas

indicate codominant species. + indicates that a mix of other species are present. *indicates an introduced species.

Cor inbia/EUCal

C. Iatifolia over annual sor hum

C Iatifolia over Piectrachne

C. Iatifolia over erennial

C. Iatifolia over sed

C. jarifolia over Eriachne obtusa Eriachne triseta, Eriachne burkittii

E. tectjfjca E. jarjfolja over erennjaj

tus Woodland

E. tectifica

E. tentifiica over Piectrachne

C. dichromo hloia

es etc.

E. tintinnans over erennial

un ens

E. miniata, E. hoenicea over PIectrachne un ens + Sor hum intrans

rasses

E. miniata E. tetrodonta, C. bleeseri over PiectrachneE. bleeseri over PIectrachne

E.

E.

E. tetrodonta over PIectrachne

hoenicea over hummock + annual

E.

hoenicea

E.

un ens

hoenicea

E.

hoenicea

rasses

E.

hoenicea

E.

C. bleeseri over hummock + erennial

hoeniceaover PIectrachne un ens Sor hum sti oideum

rasses

Acacia s

hoenicea over Sor hum sti oideum

C. o1 car aover erennial

C. dichromo hloia over PIectrachne

C. o1

un ens

E. miniata, E. tetrodonta over Piectrachne

E. tetrodonta C. terminalis over erenniai

car a Me Iaieuca viridiflora + Acacia s

over Eriachne obtusa and PIectrachne

E. tetrodonta

Site number

E. tetrodonta

un ens

112, 125, 14873, 136

,

rasses

C. randifoliaover erennial

77, 120I I I

E. tintinnans over Pleatrachne

C. terminalis

192

E. tintinnans E. tectifica over erennial

un ens

C. Iatifolia over erennial

E. microtheca MeIaieucaminutifolia over erennial

rasses

:

118, 88, 65, 87, 44

E. microtheca

81

E. microtheca over Chr so

rasses

100

E. microtheca bare round

over PIectrachne

un ens

E. microthecaover Terminalia Iat

185

E. microtheca E. a uana overDichanthium fecundum

92

Excoecaria arvifolia

un ens

E.

rasses

un ens

143, 80, 135

over PIectrachne + sed es

E.

ruinosaover erennial rasses + Sor hum sti oideum

102

rasses

E.

ruinosa MeIaleucaminutifolia over erennial

rasses

un ens

E. pruinosa (Terminalia platyptera) over Aristida in aequiglumis and Aristidah rometrica

3, 107, 71

un ens

ruinos, EUCal tus randifolia over Themeda triandra, Sehima nervosa

134

o on fallax

163

MeIaleuca Woodland

164,165

M. viridiflora over erennial

184

rasses

over Brach achne conver ens

190

COMMERCIAL-IN-CONFIDENCE

Prepared for: ConnellWagnetPrepared by: ERA Environmental Services Pty Ltd

67

tera over

23, 89, 954

rasses

103

erennial

79

140

rasses

26

rasses

rasses

124

83

55

I

32

52, 20256

.

13

171

99, 17

,

114, 7530

169

.

1/9

:

.

SepU97Job NO XI32

I

Page 179: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

,

I

I

:

viridflora over sed es +

viridiflora, M. minutifolia overviridiflora over Chr so

,

:

viridiflora over Dichanthium fecundum

,

.,

erennial rasses

. sericea over

o on fallax an

erennials

M. minutifolia, M. ar entea over

erennial

:

M. minutifolia (Terminala canescens) over perennia gra

rasses + annual

eme a

M. minutifolia, M. sericea over sor

Chr so o

E. arvifolia

s s inescens

rasses

Eriachne obtusa

on fallax

L. cunnin hamii

Terminala volucris over

,

L. cunning hamii

L. cunnin

,

hum

Atala ahemilauca

hamii E. ruinosa, E.

E. inIata, E. hoenjcea, C. bleeseri, E. tetroOn d

annual

ermina

,

E. papuana, C. po ycarpa,Sehima nervosum

erennial rasses + s

,

E. IatifoliaE. tintinnans, . gran 10 ,

over Chr so o

o1 car a overChr so o on

Terminala arostrata over

01

,

Terminalia r'"' hamjj, M. minutifolia)over

on fallaxfallax and Sehima

. . .

TerminalIaa"' ' tjficaoverSorghumstipoideumandErythrophleum chioros ac ys,

dland

nescens over Sor hum sti

I

d P. uadriloculare

E. Iatifolia, Acacia difficiis over se

35, 57

erennial rassess E. chiorostachys ov

Co inbialEucal

C. Iatifolia over Piectrachne

46

,

175

prepare ntalServicesPtyLtd

oldeum

tus O en Woodland

94

42

un ens

Sorghum

I 31

COMMERCIAL-IN-CONFIDENCE

S

S

61

3

204

hum Intrans

145

72

117

Job NO Xi32SepV97

Page 180: VEGETATON STUDY - NTEPA · A vegetation survey of Bradshaw Field Training Area was conducted in June 1997. From 151 sites, a total of 422 species were identified including three rare

C. Iatifoliaover erennial rasses

E. tectificaoverSor hum stiiodeum annual +Themeda erennialE. tectifica over mixed

E. techfica (C. polycarpa, T. platyptera) over Sehima nervosum, Chrysopogonfallax, Themeda triandra

E. microtheca over Panicum decom OSitum and Era rostis setifoliaE. microtheca over Sehima nervosum

E. microtheca/E. cainauldulensis over Chr so oE. microtheca Excoecaria arvifolia over BrachE. microtheca

E. microtheca over Aristida h

E. a uana G rocar us americanus over Sor hum IumosumE. a uana over Sehima nervosum and Themeda triandra

bare

E

C. d car a M. viridiflorahoenicea, C. dichromo hloia over PIectrachne

round

MeIaleuca O en Woodland

M. acacioides, M. minutifolia over erennialM. minutifolia over annual

erennia

Mininutifolia T. Iat tera

rometrica

Terminalia O en Woodland

T. Iat tera, E. microtheca, L SI h 11umcunnin

on fallax

T. canescens PetalOSti am ubescens over Sor

achne conver ens

T. canescens over Eriachne ciliate, Sor

over Chr so o on fallax and Aristida s

T. bursarina over Eriachne fasti iata

129

T. platyphylla (E. cainauldulensis) over Cynodon dactylon (Arundinellane alensis

erennial

123

T. volucris (M. miniata, M. viridiflora) over Sorghum plumosum and Sorghumintrans

31

rass

I 91

over Chr so o on fallax

T. arostrata over Sehima nervosum and Eriachne triseta

T. latipes (E. ferruginea, Owenia vernicosa) over PIectrachne pungens andSor hum intrans

annual

:

205

un ens

T.

erennial

49

rass

erennial

24

Iat tera M. minutifolia, M. sericea

:

Acacia s

33

168

Lysiphyllum Open WoodlandL. cunning hamii(Terminalia platyptera, Atalaya hemiglauca) overCh so o on fallax

I

:

hum sti oideum

64, 85

erennial

E. o1

hamiover erennial

L. cunning hamii(T. platyptera, E. conferIiflora) over Themeda triandra,Sor hum intrans

93

.

car a over Aristidah rometricaand Sor hum Iumosum

hum stiiodeum annual

L. cunnin hamii over Era rostis setifolia, Sor

167

.

178

,

Mixed Open Woodland

.

C. conferIiflora, E. chlorostachys, L. cunning hamii, Adansonia gregorii over S.

19

nervosum

C. grandifolia, E. papuana, C. Iatifolia, Lysiphyllum cunning hamii overEriachne and sed es

I I 6

over Themeda triandra

rasses

174

E. microtheca, Cathormium umbellatum, Erythrophleum chiorostachys,L si h 11um cunnin hamii, Atala a hemilauca over Chr so o on fallax

.

C. Iatifolia, C. grandifolia, TerminalIa arostrata over Sehima nervosum andThemeda triandra

14, 53104, 122207

COMMERCIAL-IN-CONFIDENCE

Prepared for: Connell WagnerPrepared by: ERA Environmental Services Pty Ltd

106

156

186

I

hum Iumosum

188, 193189

9

206

162

179

.

.

187

194, 195

.

29

37

12

41

I

I

SepV97Job NO XI32

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.

E. pruinosa, C. confer!iflora, M. minutifolia, T. platyptera, Acacia valida, L.cunnin hamii over T. triandra and S. sti oldeum

.

C. Iatifolia, C. confer11flora, E. papuana, Terminalia arostrata over Sehimanervosum

C. foelscheana, E. techfica, C. randifolia over Sehima nervosumC. o1 car aover Sor hum sti

I

E. randifolia, Terminalia IatAcacia validaover Sehima nervosum, Sor hum Iumosum

Lysiphyllum cunning hamii, Me Ialeuca minutifolia, Cochlospermum fraseri, Eruinosa over T. triandra and C. fallax

Excoecaria parviflorum and Lysiphyllum cunning hamii over Aristida andCh so o on fallax

Adansonia re orii L si h 11umcunnin hamii) over Brach achneconver ens

EUCal

E. miniata over Sor hum IumosumE. miniata

oldeum

tus O en Forest

tera over Themeda triandra ++

E. techfica over Sor hum sti oldeum

,

E. hoenicea over PIectrachne

E. tetrodonta over PIectrachne

MeIaleuca O en Forest

M. minutifolia over

M. minutifolia (PetalOStigma pubescens) over Schizachyrium fragile(annual)and Chr so o on fallax

M. minutifolia (Excoecaria parvifolia) over Themeda triandra andChr so o on fallax

M. sericea

M. sericea, M. minutifolia over Sor hum Iumosum and Sehima nervosum

I 51

M. sericea, M. minutifolia over Themedra triandra and Schizach rium fra Ile

erennial

M. sericea over Ch so o on fallax and Sor hum sti oideum

43

,

M. viridiflora over Sehima nervosum

un ens

M. minutifolia over erennial rasses and Sor hum sti oldeum

un ens

M. viridiflora over Eleocharis

141

M. viridiflora over sed es

86

rasses

M. citrolens M. minutifolia over Chr so o on fallax Eriachne setifolia

82

^

^

39

132

Lysiphyllum Open ForestL. cunnin hamiiover Chr so o on fallax

11

L. cunnin hamii over Sehima nervosum

L. cunning hamii, C. dichromophloia (Cochlospermum fraseri) overPledrachne un ens

28

Ri arian O en Forest/Forest

I

M. viridiflora, M. Ieucadendra over Dicanthium fecundum

127, 128

M. Ieucadendra C. t chocar a over Germainiatruncatilumis

78

M. Ieucadendra over Mnesithia rotlboelliodes/PanicumMieucadendra over Vetivera auciflora

146

M. Ieucadendra over Arundinella ne alensis

I

62

Lo hostemon randiflorus Ficuss

E. microtheca, TerminaliaE. microtheca over SIda acuta*, Senna occidentalis*Terminalia sericocar a, Sterculia holtzii closed forest over various herbs

109

105

^

Me Iico

38

Shrubland

e eller iana, Terminalia sericocar a, Ficus racemosa, ++

Acacia kelleri + Acacia s ecies over PIectrachne

74, 50

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11 3

133

208

hat h

9

91

., Nauclea, M. Ieucadendra

149

aover Ch so o on fallax

197

58

108

183

150

137

un ens

130

142

144

84

16

266

126

70

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Acacia Iat car aover Sor hum sti oldeum and Pledrachne un ensTerminalIa bursarina, Acacia difficilis, Lysiphyllum cunning hamii, Oweniavernicosa over PIectrachne

Grasslands

Chr so o on fallax, Sehima nervosumSehima nervosum, Brach achne conver ensSehima nervosum (Hetero o on contortus, Chr so o on fallax)Chr

Sor

so o

Aristida s

hum

Sed es and Xerochloa

on fallax

Sed es

Eriachne s ecies and Sor hum stiiodeum

Iumosum and sed esecies

Themeda triandra, Chr soGermainiatruncatilumis Eleocharis, EUlaliaHetero o

Sor hum

PiectrachChr

on triticeus

Chr

so o

Brach achne conver ens Aristida Iatifolia, Dichanthium fecundum

Iumosum, Sehima nervosum

so o

Dichanthium fecundum, Chr so o on fallax

e

Sor hum Iumosum Era rostis setifolia, Chr so o on fallax

on fallax Dichanthium sun

on fallax

o on fallax, sed es

ens

200

18

48

I

,

.

I 21,

*

*

.

,

.

,

.

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^

,

.

,

.

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^

.

;

:.

I

I*

tI

,

^

Appendix 6

Vegetation habitats and mapping units

I

I

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.

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SepV97Job NO XI32

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Appendix 6 Eight broad habitats and mapping units within those habitats. Species inbrackets occur in the unit but are subordinate. Species separated by commas are

coodominants. + indicates that a mix of other species are present.

MAPPING UNIT

MONSOON FOREST

I mixed s ecies

RIPARIAN FOREST, OPEN-FOREST2 Me Ialeuca Ieucandendra

3 EUCal

4 EUCal

CORYMBIA/EUCALYPT OPEN-FOREST, WOODLAND

tus microtheca, TerminalIa

5 EUCal tus miniata, E. tetrodonta over annual and erennial

tus cainauldulensis, E. microtheca

6 Eucalyptus miniata (E. tetrodonta, C. bleeseri, C. dichromophloia)over hummock rasses

7 EUCal tustetrodonta

8 Cor inbia bleeseri over hummock

9 Gorymbia bleeseri(E. tetrodonta, E. miniata) over annual andhummock rasses

10 EUCal tus tectifica over annual and erennial11 EUCal

Ia

12 EUCal

13 EUCal

era

tus tectifica over hummock rasses

14 Gorymbia Iatifolia over annual and perennial grasses and sedges

tus hoeniceaoverhummock rass annual

SITE NUMBER

15 Cor inbia Iatifolia over hummock

tus hoenicea, C. dichromo hloia over hummock

16 EUCal tus ruinosaover erennial

rasses

66, 87, 126, 144

17 EUCal tus tintinnans over hummock

18Cor inbia d car a+

84, 130, 137, 150

.

.

16

rasses

19 EUCal tusalba, C. randifoliaover erennial

2, 24

4

20 Eucalyptus microtheca (Excoecaria parvifolia) over perennial

rasses

127, 128

rasses

21 EUCal tusmicrothecaover erennial

78, 80, 92, 135, 143, 184

22 EUCal

79, 103, 140

rasses

LowoPEN FOREST, WOODLAND

102

23 Me Ialeuca viridiflora over Eleocharis

185

rasses

.

24 Me Ialeuca viridiflora over perennial grasses

rasses

tus microtheca over bare round

42, 44, 65, 88, 1/8, 146

rasses

rasses

25 Me Ialecua minutifolia, M. sericeum over annual and perennialgrasses

100

62, 67, 71, 107, 134

,

3, 163, 164, 165

26 Excoecaria arvifolia Terminaliavolucris over erennial

77, 120, 111, 112, 125,148, 192

27 L si h 11umcunnin hamiiover erennial

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rasses

:

73, 136

rasses

17, 130, 75, 99, 114, 169

124, 131

23, 69, 89, 94, 95

5

26, 83

I, 32, 202, 205

13, 52, 55, 19133, 56

rasses

91

.

5, 9, 22, 47, 1/9, 181,186, 201

rasses

10, 15, 38, 45, 51, 54, 50,74, 76, 96, 105, 109, 113,133, 197, 206

:

:

34, 35, 577, 25, 46, 59, 170

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28 TerminalIa canescens, Erythrophleum chlorostachys over annual

.

rasses

CORYMBIA/EUCALYPTOPEN-WOODLAND

29 Cor inbia Iatifolia over hummock

30 Cor

31 Eucalyptus papuana, C. polycarpa, E. bigalerita over perennial

inbia Iatifolia over erennial

rasses

~

32 EUCal tus microtheca over

33 EUCal tustectifica over annual and erennial

=

OTHER OPEN-WOODLAND

,

34 Lysiphyllum cunning hamii over perennial grasses

35 Terminalis bursarina over annual

.

36 Acacia valida over erennial

rasses

37 Me Iaieuca minutifolia, M. sericea over bare round

rasses

38 TerminalIa arostrata, T. volucris over erennial39 Terminalia arsotrata, EUCal

.

40 Mixed over hummock

erennial

SHRUBLAND

41 Acacia over hummock

rasses

GRASSLAND

29, 60, 63, 104, 122, 145

42 Chrysopogon fallax, Sehima nervosa, Sorghum plumosum,Themeda triandra

.

.

43 Xerochloa jinberbis, Eleocharis

rasses

44 Sor hum stiiodeum, Eriachne s ecies, Aristida s ecies

rasses

72, 1/5

rasses

:

45 PIectrachne b noei

rasses

1/7, 129

46 Sed eland

tuss ecies, over erennial rasses

64, 85, 86, 93, 139

rasses

14, 49, 53, 168, 204

.

123

rasses

.

11, 58, 108, 132, 175,179, 194, 195, 198106

39

19, 116188, 18340, 41, 43, 20318, 183, 189

,

70

*

6, 8, 48, 147, 173, 180,196, 19968

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27, 97, 11090

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Appendix 7

Photographs of mapping units

,

,

:

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