Strike Limited Flora and Vegetation Survey Ocean Hill 3D Seismic Survey

27 April 2021 JBS&G59367- 136,162 (Rev 0) JBS&G Australia Pty Ltd T/A Strategen-JBS&G

Table of Contents

1. Introduction ...... 1 1.1 Scope ...... 1

2. Context ...... 3 2.1 Legislative Context ...... 3 2.1.1 Environmental Protection and Biodiversity Conservation Act 1999 .... 3 2.1.2 Biodiversity Conservation Act 2016...... 3 2.1.3 Environmental Protection Act 1986 ...... 3 2.1.4 Biosecurity and Agriculture Management Act 2007 ...... 3

3. Environmental Setting ...... 5 3.1 Climate ...... 5 3.2 Soils and Landforms ...... 5 3.2.1 Hydrology ...... 8 3.2.2 Environmentally Sensitive Areas ...... 8 3.2.3 Conservation Areas ...... 8 3.2.4 Land Use ...... 8 3.2.5 Regional Vegetation ...... 8

4. Methods ...... 10 4.1 Rationale for Survey Approach ...... 10 4.2 Desktop assessment ...... 10 4.2.1 Field assessment ...... 10 4.3 Survey limitations and constraints ...... 12

5. Results ...... 14 5.1 Desktop assessment ...... 14 5.1.1 Threatened and Priority Flora ...... 14 5.1.2 Threatened and Priority Ecological Communities...... 15 5.2 Field Survey ...... 18 5.2.1 Native Flora ...... 18 5.2.2 Introduced (exotic) Taxa ...... 18 5.2.3 Vegetation ...... 18 5.2.4 Vegetation condition ...... 19 5.2.5 Conservation significant communities ...... 19 5.2.6 Conservation significant flora ...... 22

6. Discussion ...... 24

7. Limitations ...... 25

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8. References ...... 26

List of Tables Table 3.1: DAFWA Soil landscape subsystems (Source DPIRD 2018) ...... 6 Table 4.1: Database searches conducted for the desktop assessment...... 10 Table 4.2: Survey Plan...... 10 Table 4.3: Survey Personnel...... 10 Table 4.4: Vegetation condition scale for South West and Interzone Botanical Provinces (EPA 2016)...... 12 Table 4.5: Flora and vegetation survey potential limitations and constraints ...... 13 Table 5.1: Vegetation units within the Survey Area ...... 18 Table 5.2: Vegetation Condition within the Survey Area ...... 19 Table 5.3: Conservation significant flora identified during 2016 and 2020 surveys...... 22

List of Figures Figure 1.1: Survey Area ...... 2 Figure 3.2: Soil landscape subsystems ...... 7 Figure 5.1: Vegetation Types in the Survey Area ...... 20 Figure 5.2: Vegetation condition ...... 21 Figure 5.3: Conservation Significant Flora Recorded within the Survey Area ...... 23

Appendices Appendix A Conservation significant flora and ecological community definition Appendix B Desktop assessment results Appendix C Conservation significant flora species potentially occurring within Survey Area. Appendix D Native vascular taxa recorded within the survey area Appendix E Location of Priority Listed Flora species recorded during reconnaissance and targeted surveys.

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1. Introduction

Strike West Pty Ltd (Strike) is proposing to undertake a 3D seismic acquisition survey in the Shire Carnamah in the mid-west region of Western Australia within the petroleum exploration permit EP 495 (the Project) (Figure 1.1). The Project is proposed to be undertaken within an area of approximately 276.1 km2 (maximum 32.3 km in length by 8.9 km in width) within the Perth Basin (the Project Area). The northern extent is approximately 8 km east of Eneabba the Project Area is approximately 75 - 100 km southeast of Dongara, extending along Carnamah-Eneabba Road (north) and Coorow-Green Head Road (south) (Project Area). The Project will largely be undertaken in rural areas previously cleared for farming activities. The seismic lines have been aligned to use previously cleared areas where possible to undertake the Project with the minimum amount of clearing and disturbance via mulching of native vegetation. The Project will however require temporary disturbance of native vegetation via mulching to enable access for the vibroseis trucks and light vehicles. A maximum vegetation clearing width of 3.5m will be maintained for the seismic lines. The clearing of significant trees i.e. with a truck diameter greater than 100 mm will not occur. An Ecological Survey was therefore necessary to determine the environmental values within the areas of native vegetation within which temporary disturbance will be required. Areas requiring clearing of native vegetation formed the Survey Area for the purpose of this Ecological Survey (Figure 1.1). In total, the Survey Area comprises an area of approximately 4,600 ha, containing approximately 140 km of source lines that require clearing that intersect with native vegetation. The Survey Area contains approximately 4,200 ha of remnant vegetation. 1.1 Scope The scope of the Ecological Survey was to undertake a desktop assessment and field assessment within the Survey Area. The objectives of the Ecological Survey included: • Undertake desktop assessments for flora and vegetation within, and adjacent to, the Project Area; • Undertake a flora and vegetation survey of areas of native vegetation within, and adjacent to, areas that may be impacted by clearing; and This Ecological Survey report provides the results of the desktop assessments and the in-field flora and vegetation, and fauna surveys. The assessment has been undertaken to support Strike with the required environmental approvals for the Project, including informing management and mitigation measures implemented in response to the potential interaction between the proposed works and the flora and vegetation values identified. This assessment builds on the Flora and Vegetation survey undertaken by ecologia in 2016 across a portion of the current Project Area. Data and results where relevant to this assessment from ecologia (2016) report have been consolidated and presented in this report.

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Legend Scale 1:150,000 at A4 012 Survey area Kilometres Cadastral boundary Coord. Sys. GDA2020 MGA Zone 50 SITE LOCATION Highways Z Main road Job No: 59367 Minor road Track Client: Strike West Ltd FIGURE 1.1

Version: A Date: 29-Mar-2021

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2. Context

2.1 Legislative Context Flora and fauna in Western Australia (WA) are protected formally and informally by various legislative and non-legislative measures, which are as follows: • Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act) – Australian Government; • Biodiversity Conservation Act 2016 (BC Act) – State; • Environmental Protection Act 1986 (EP Act) – State and • Biosecurity and Agriculture Management Act 2007 (BAM Act) – State. Non-legislative measures: • WA Department of Biodiversity, Conservation and Attractions (DBCA) Priority lists for flora, ecological communities and fauna; • Weeds of National Significance; and • Recognition of locally significant populations by the DBCA. A short description of each legislative measure is provided below. Other definitions, including species conservation categories, are provided in Appendix A. 2.1.1 Environmental Protection and Biodiversity Conservation Act 1999 The EPBC Act aims to protect matters of national environmental significance, which are detailed in Appendix A. Under the EPBC Act, the Commonwealth Department of Agriculture, Water and Environment (DAWE) lists protected species and Threatened Ecological Communities (TECs) by criteria set out in the Act. Species are conservation significant if they are listed as Threatened (i.e. Critically Endangered, Endangered and Vulnerable) or Migratory. 2.1.2 Biodiversity Conservation Act 2016 DBCA lists taxa (flora and fauna) under the provisions of the BC Act as protected and are classified as according to their need for protection (see Appendix A). The BC Act makes it an offence to ‘take’ threatened species without an appropriate licence. There are financial penalties for contravening the BC Act. 2.1.3 Environmental Protection Act 1986 Threatened flora, fauna (and significant habitat necessary for the maintenance of indigenous fauna) and TECs are given special consideration in environmental impact assessments and have special status as Environmentally Sensitive Areas (ESAs) under the EP Act and the Environmental Protection (Clearing of Native Vegetation) Regulations 2004. Exemptions for a clearing permit do not apply in an ESA. 2.1.4 Biosecurity and Agriculture Management Act 2007

The BAM Act provides for management and control of listed organisms, including introduced flora species (weeds). Species listed as declared pests under the BAM Act are classified under three categories: • C1 Exclusion: Pests assigned under this category are not established in Western Australia, and control measures are to be taken to prevent them entering and establishing in the State. • C2 Eradication: Pests assigned under this category are present in Western Australia in low enough numbers or in sufficiently limited areas that their eradication is still a possibility.

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• C3 Management: Pests assigned under this category are established in Western Australia, but it is feasible, or desirable, to manage them in order to limit their damage. Control measures can prevent a C3 pest from increasing in population size or density or moving from an area in which it is established into an area that is currently free of that pest. Under the BAM Act, land managers are required to manage populations of declared pests as outlined under the relevant category.

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3. Environmental Setting

3.1 Climate The Lesueur Sandplain has a dry warm Mediterranean climate with warm, dry summers and cool, wet winters, but 7-8 dry months per year. The nearest weather station which records both temperature and rainfall data relevant to the area was the Carnamah (Station 008278) which operated from 1937- present. The average annual rainfall during this period was 367.7 mm, with the highest monthly rainfall occurring from June to August (Figure 3.1). The average monthly maximum temperature ranges from 18.0°C in July to 36.1°C in January. Average monthly minimum temperatures range from 7.3°C in July and August to 19.2°C in February. Total winter rainfall (June to August) in the months preceding the 2020 survey was approximately 70 mm less than the long- term average.

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Figure 3.1: Climate statistics for the survey area, Mean annual rainfall and monthly averages for 2020 (BoM 2020) 3.2 Soils and Landforms The Interim Biogeographic Regionalisation for Australia (IBRA, Version 6.1) classifies the Australian continent into regions (bioregions) of similar geology, landform, vegetation, fauna and climate characteristics. The Project lies within the Geraldton Sandplains bioregion, which comprises three subregions; the Edel, Geraldton Hills and Lesueur Sandplain subregions. The Project lies within the Lesueur Sandplains subregion. The Geraldton Sandplains are characterised by a series of old dunes which run parallel to the coast. The younger Quindalup dunes occur near the contemporary coastline, with the Spearwood dunes occurring further inland. The soils are typically sandy with some areas of exposed limestone, and a series of wetlands occurs along the plains. In the east, lateritic rises occur. There are 11 soil subsystems across the Survey Area (Table 3.1; Figure 3.2). These soil sub-systems were used to inform vegetation unit mapping and potential presence of conservation significant flora and communities.

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Table 3.1: DAFWA Soil landscape subsystems (Source DPIRD 2018) Map Symbol Soil Subsystem Description 224Bh_1 Boothendarra 1 Subsystem Crests and upper slopes of undulating low hills and gravelly rises; Sands, sandy gravels and sandy duplexes with occasional loams and clays 224Bh11 Boothendarra 11 Subsystem Gently to very gently inclined hillslopes and footslopes with sands, sandy gravels and sandy duplexes with occasional loams. 224Ye_1 Yerramullah 1 Subsystem Laterite plateau residual; shallow gravel, shallow sand over duricrust, sandy gravels 224Ye_2 Yerramullah 2 Subsystem Plateau residuals, very gently to gently inclined hillcrest and hillslopes; pale sandy gravels, shallow gravel over duricrust, gravelly pale deep sand, pale and yellow deep sands 224Ye_3 Yerramullah 3 Subsystem Colluvial slopes and some plateau remnants, very gently to gently inclined hillslopes and sand filled minor valleys; pale and yellow deep sands, pale sandy gravels, shallow gravel over duricrust, some sandy duplexes and sandy earths 224Ye_3a Yerramullah 3 slopes Phase Colluvial slopes; pale and yellow deep sands, pale sandy gravels, shallow gravel over duricrust, some sandy duplexes and sandy earths 224Ye_7 Yerramullah 7 Subsystem Gentle slopes and drainage depressions; Grey sandy duplex soils; minor gravelly soils and wet soils some salt risk 224Ye_8 Yerramullah 8 Subsystem Breakaways, moderately inclined to steep hillslopes; exposing underlying kaolinitic clays and Mesozoic sediments; gravels, loamy earths 224Ye_9 Yerramullah 9 Subsystem Narrow alluvial flats of minor creeks; pale to brown deep sands, sandy and loamy duplexes, shallow sand over pans

©JBS&G Australia Pty Ltd T/A Strategen-JBS&G | JBS&G59367- 136,162 (Rev 0) 6 Legend Scale 1:130,000 at A4 012 Survey area 224Ye_2 Kilometres Soil landscape (DPRID) 224Ye_3 224Bh11 224Ye_3a Coord. Sys. GDA2020 MGA Zone 50 Z SOIL LANDSCAPE SUBSYSTEMS 224Bh_1 224Ye_7 224Ye_1 224Ye_8 Job No: 59367 224Ye_9 Client: Strike West Ltd FIGURE 3.2

Version: A Date: 29-Mar-2021

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3.2.1 Hydrology Surface drainage in the region is made up of eight (8) main sub-catchments: Arrowsmith River, Cockleshell, Hill River, Logue, Minyulo, North Coastal Dunes and the South Coastal Dunes catchments. The Project Area occurs within the Hill River and Indoon-Logue catchments, with watercourses in these catchments flowing predominantly in an east-west direction from the upland areas in the east into large swamps or lakes in interdunal depressions on the Swan Coastal Plain. Surface water movement in the Logue catchment is only apparent at the end of winter when the chains of lakes and swamps are filled and often connect via broad streams. Surface water flows are generally considered to be low in the region due to the sandy nature of the surface soils and their corresponding high infiltration rates. Although these soils have high saturated infiltration rates and hydraulic conductivities, their permeability decreases significantly when in an unsaturated condition (e.g. drought), therefore surface runoff is common following rapid and intense rainfall events following extended dry periods. The Warradarge Creek flows through the central portion of the Project Area. The Eneabba region overlies the Dandaragan Trough, which is part of the Perth Basin, extending east to the Urella and Darling Fault and west to the coast. The trough consists of up to 30m of Quaternary sand and clay sediments of the Perth Superficial Formation overlaying early Jurassic to late Cretaceous sediments of the Yarragadee Formation (ecologia 2017). Groundwater of the Yarragadee North aquifer is confined to the coastal plain by the superficial formations, by the South Perth Shale in the south, and by the Otorowiri Siltstone in the east (Department of Water, 2013) and occurs as unconfined to confined. On a regional level, groundwater is recharged into the aquifer via rainfall and surface runoff, infiltrating through the overlying surficial and superficial sediments. The main regional use for ground water in the area is stock water supplies, although this water has a relatively high salinity. 3.2.2 Environmentally Sensitive Areas One Environmentally Sensitive Area (ESA) intersects the north west of the Project Area. The ESA is related to the buffered extent of a Threatened Ecological Community location. This TEC occurrence is discussed further in Section 5.1. No other mapped ESAs occur within the Project Area. 3.2.3 Conservation Areas No conservation areas occur within the Project Area. The nearest conservation areas to the Project Area are: • South Eneabba Nature Reserve (3.2 km west); • Un-named Nature Reserve - R 46713 9 (2 km west); • White Gums Nature Reserve (4.7 km north); and • Tathra National Park (8 km east). 3.2.4 Land Use Land uses within the survey area include agricultural (wheat, canola, sheep, tree farms etc.), bee keeping, and public access routes. 3.2.5 Regional Vegetation The Project Area is located within the Lesueur Sandplain subregion of the Geraldton Sandplains bioregion under the Interim Biogeographic Regionalisation for Australia (IBRA) (Department of the Environment, 2012).

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Two associations of Beard (1976) occur over the Project Area: Shrublands; scrub-heath on lateritic sandplain in the central Geraldton Sandplain Region (Association 379), and Shrublands; mixed heath (Association 49). Association 379 occurs predominantly in the southern portion of the study area and consists primarily of a mixed open woodland or Allocasuarina mixed shrubland over Anigozanthos mixed open forbland. In the northern portions of the Project Area, Association 379 occurs as a mosaic with Association 49 which consists primarily as a heath of , Allocasuarina humilis, and Dryandra fraseri.

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4. Methods

4.1 Rationale for Survey Approach The following survey methods determined as being appropriate to define impacts on flora and vegetation by the Project: 1. Desktop assessment of available ecological data and reports. 2. Reconnaissance level flora and vegetation survey. 3. Targeted survey for conservation significant flora along planned seismic lines requiring clearing. 4.2 Desktop assessment Database searches were undertaken to generate a list of vascular flora, and ecological communities previously recorded within, and nearby the survey area – with an emphasis on species and communities of conservation significance and introduced species. A desktop review of the Survey Area was undertaken in June 2020 and included a review of the area within 10 km of the Project Area. Government databases were queried to identify the potentially conservation significant species which might occur at the Project Area. These searches were reviewed in August 2020 to ensure no changes to listings had occurred since the searches were first requested. Habitat information, where available, was reviewed to determine likelihood that each species might occur within the search area (Table 4.1). Table 4.1: Database searches conducted for the desktop assessment. Custodian Database Taxonomic group Buffer DAWE Protected Matters Search Tool Flora, Vegetation and Fauna 10 km DBCA NatureMap Flora and Fauna 10 km DBCA Threatened (Declared Rare) and Priority Flora 10 km Flora (TPFL) 4.2.1 Field assessment An outline of the field assessments to date is shown in Table 4.2. Table 4.2: Survey Plan. Phase Dates Target Targeted Flora Survey Spring 2020 15- 20 November 2020 Targeted survey Reconnaissance Survey update 15-20 November 2020 Reconnaissance flora and vegetation survey Field surveys were conducted by three Botanists in November 2020 (Table 4.3). All collected were taken under flora collecting permits listed in Table 4.3, pursuant to Regulation 62 of the Biodiversity Conservation Regulations 2018. Table 4.3: Survey Personnel. Name Role Flora collection permit Jason Webb Planning, fieldwork and data interpretation and FB62000168 Senior Botanist report preparation. TFL-75-1920 Adrianne Hortle Fieldwork and data FB62000174 Botanist Lachlan Warner Fieldwork and data FB62000175 Environmental Consultant 4.2.1.1 Reconnaissance Flora and Vegetation Survey A reconnaissance level flora and vegetation survey was undertaken as per EPA technical guidance, Flora and Vegetation Surveys for Environmental Impact Assessment (2016) supplementing the existing surveys conducted and extending the vegetation mapping to include the entire Project Area.

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The purpose of the reconnaissance survey was to delineate vegetation within the Survey Area. Data was collected from several relevés within vegetation which appeared representative of an area of vegetation type and collections were made of dominant flora species. At each relevé the following information was recorded: • Name of recorder; • Date; • GPS co-ordinates (recorded in GDA94 UTM 50H); • Photograph of the vegetation; • Vegetation condition; • Brief vegetation description; • Dominant vascular flora taxa present (with average height and total percentage foliage cover of each taxon); • Topography; • Soil type and colour; • Geology (type, size and cover of any rocks, stones, gravel or outcropping); • Average percentage cover of leaf litter and bare ground; and • Disturbance details including fire history (time since last fire), and physical disturbance including evidence of erosion, grazing and weed invasion. For any populations of taxa known to be conservation significant or introduced flora observed, a GPS location and a count of the individuals present, or percentage foliar cover for a given area for the species, were recorded. The extent of the populations were also recorded to enable mapping of populations and to inform avoidance and mitigation strategies.

Targeted Flora Survey The targeted survey along planned lines was proposed to fully inform the density and distribution of conservation significant flora species with potential to be impacted by the Project. A transect width of 10 m was selected to maximise survey efficiency while still allowing flexibility for seismic operators during acquisition. Botanists walked the mapped seismic lines with the aid of a GPS-enabled tablet. The mapping package included known locations of Threatened and Priority Flora identified from database searches. Each line covered a 5m distance either side of the seismic line (10m transect width). For occurrences of taxa thought to be conservation significant, a GPS location and a count of the individuals present for a given area for the species, were recorded. The extent of this population was also recorded to enable mapping of populations and inform avoidance and mitigation strategies. Prior to the survey, a list of conservation significant flora with the potential to occur within the Survey area was compiled. Field personnel familiarised themselves with photographs, reference samples and descriptions of these taxa before conducting the survey. A pdf document containing photographs and descriptions of conservation significant flora was also stored on tablets used in the field, for quick reference to identification information. The locations of any suspected conservation significant species were recorded and where identification was not certain, specimen was collected for identification confirmation. Information on population size, surrounding vegetation, and soils was also collected at each point that a known or suspected conservation significant flora species was encountered, and a photograph taken in

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most circumstances. Given the large number of conservation significant flora species potentially occurring within the Survey area, a cautious approach was undertaken with respect to collecting and identifications. This on some occasion may have resulted in populations not being defined. Should these instances require a population boundary defined for avoidance purposes, these locations will be revisited prior to final line planning. Where conservation significant flora species were recorded, population extents were defined to enable avoidance strategies to be implemented. This creates an exclusion zone, allowing the opportunity for the deviation of lines through areas where no conservation significant flora species were recorded. Where populations extents could not be defined, or where high densities extended for over 50 m, this was noted to inform seismic survey planners. Flora Identification and Nomenclature All plant specimens collected during the field surveys were identified using appropriate reference material or through comparisons with pressed specimens housed at the Western Australian Herbarium, where necessary. Nomenclature of the species recorded is in accordance with Western Australian Herbarium (1998-).

Vegetation Condition Vegetation condition was recorded at all relevés, and opportunistically within the Survey Area during the field assessment where required. Vegetation condition was described using the vegetation condition scale for the South West Botanical Province (EPA, 2016); (Table 4.4). Vegetation condition polygon boundaries were developed using this information in conjunction with aerial photography interpretation and were digitised as for vegetation type mapping polygon boundaries. Table 4.4: Vegetation condition scale for South West and Interzone Botanical Provinces (EPA 2016). Vegetation Condition Description Pristine Pristine or nearly so, no obvious signs of disturbance or damage caused by human activities since European settlement. Excellent Vegetation structure intact, disturbance affecting individual species and weeds are non- aggressive species. Damage to trees caused by fire, the presence of non-aggressive weeds and occasional vehicle tracks. Very Good Vegetation structure altered, obvious signs of disturbance. Disturbance to vegetation structure caused by repeated fires, the presence of some more aggressive weeds, dieback, logging and grazing. Good Vegetation structure significantly altered by very obvious signs of multiple disturbances. Retains basic vegetation structure or ability to regenerate it. Disturbance to vegetation structure caused by very frequent fires, the presence of very aggressive weeds, partial clearing, dieback and grazing. Degraded Basic vegetation structure severely impacted by disturbance. Scope for regeneration but not to a state approaching good condition without intensive management. Disturbance to vegetation structure caused by very frequent fires, the presence of very aggressive weeds at high density, partial clearing, dieback and grazing. Completely Degraded The structure of the vegetation is no longer intact, and the area is completely or almost completely without native species. These areas are often described as ‘parkland cleared’ with the flora comprising weed or crop species with isolated native trees and shrubs. 4.3 Survey limitations and constraints There are possible limitations and constraints that can impinge on the adequacy of vegetation, flora and fauna surveys. The flora and vegetation assessment was evaluated against a range of potential limitations (Table 4.5).

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Table 4.5: Flora and vegetation survey potential limitations and constraints Potential limitation Impact on assessment Comment Sources of information and Not a constraint. Many surveys have been undertaken in the region, with availability of contextual previous flora and vegetation surveys conducted within parts information (i.e. pre-existing of the current Survey Area. background versus new material). Scope (i.e. what life forms, Not a constraint. Number of species recorded, number of relevés sampled and etc., were sampled). timing of the survey (i.e. spring) were adequate for this level of survey. Proportion of flora/fauna Not a constraint. This survey effort is sufficient to assess any potential clearing collected and identified (based impacts. on sampling, timing and intensity). Flora determination. Not a constraint. Specialist taxonomic advice is readily available for the bioregion. Completeness and further Not a constraint. This survey effort is sufficient to assess any potential clearing work which might be needed impacts. (i.e. was the relevant Survey area fully surveyed). Timing, weather, season, cycle. Minor Constraint Flora and vegetation surveys are normally conducted following winter rainfall in the South-West Province, ideally during spring (EPA 2016a). The field assessment was conducted in November 2020 (late spring) in fine weather conditions. Disturbances (fire flood, Not a constraint Small areas with minor disturbance were recorded; however, accidental human these did not impact the result of the survey. intervention, etc.). Intensity (in retrospect, was Not a constraint. The Survey Area was traversed on foot and all differences in the intensity adequate). vegetation structure were recorded appropriately. Resources (i.e. were there Not a constraint. Survey team had sufficient experience and resources to adequate resources to conduct the survey. complete the survey to the required standard). Access problems (i.e. ability to Not a Constraint. The Survey Area was traversable on foot, enabling adequate access Survey area). access to survey the vegetation and fauna habitat within the Survey area. Experience levels (e.g. degree Not a constraint. The lead botanist undertaking the survey and the plant of expertise in species taxonomist both have greater than five years’ experience in identification to taxon level). the flora of the Lesueur Sandplain.

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5. Results

5.1 Desktop assessment 5.1.1 Threatened and Priority Flora Flora within Western Australia that is considered to be under threat may be classed as either Threatened flora or Priority flora. Where flora has been gazetted as Threatened flora under the BC Act, the taking of such flora without the written consent of the Minister is an offence. The BC Act defines “to take” flora as to gather, pluck, cut, pull up, destroy, dig up, remove or injure the flora or to cause or permit the same to be done by any means. DBCA (2018a) contains the current list of Threatened flora in Western Australia. Priority flora are considered to be species which are potentially under threat, but for which there is insufficient information available concerning their distribution and/or populations to make a proper evaluation of their conservation status. DBCA categorises Priority flora according to their conservation priority using five categories, P1 (highest conservation significance) to P5 (lowest conservation significance), to denote the conservation priority status of such species. Priority flora species are regularly reviewed and may have their priority status changed when more information on the species becomes available. Appendix A defines levels of Threatened and Priority flora (Western Australian Herbarium 1998). At the national level, the EPBC Act lists Threatened species as extinct, extinct in the wild, critically endangered, endangered, vulnerable, or conservation dependent. Appendix A defines each of these categories of Threatened species. The EPBC Act prohibits an action that has or will have a significant impact on a listed Threatened species without approval from the Australian Government Minister for the Environment. The current EPBC Act list of Threatened flora may be found on the DAWE (2017b) website.

A total of 83 flora taxa of conservation significance were identified by database searches as potentially occurring within the Project Area (Appendix B; Appendix C).

Of these, 11 species are listed as Threatened under the Biodiversity Conservation Act 2016 (BC Act) and the Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act). The remaining 72 flora taxa identified are priority listed flora species under the BC Act. • Threatened flora - 11 taxa • Priority 1 flora (P1) -1 taxa • Priority 2 flora (P2) - 14 taxa • Priority 3 flora (P3) - 36 taxa • Priority 4 flora (P4) - 21 taxa. Two species of Threatened Flora (see below) have previously been identified within the Survey Area: • Hakea megalosperma; and • Thelymitra stellata. Both taxa are known to occur on lateritic hills and breakaways, which are present within the Survey Area. Of the priority species returned from the database searches, 14 have been previously recorded within the Survey Area: • Priority 2: o Calectasia browneana; and o clavate.

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• Priority 3: o Acacia epacantha; o Allocasuarina ramosissima; o Banksia fraseri var. crebra; o Drosera prophylla; o Hemiandra sp. Eneabba (H. Demarz 3687) (H. Demarz 3687) ; o Jacksonia anthoclada; o filiformis; o Phlebocarya pilosissima subsp. pilosissima; and o Stylidium drummondianum. • Priority 4: o Calytrix chrysantha; o Calytrix eneabbensis; and o rudis. 5.1.2 Threatened and Priority Ecological Communities The flora and vegetation of the Geraldton Sandplain is composed mainly of proteaceous scrub- heaths and is rich in endemic flora (Desmond & Chant, 2002). Burbidge et al. noted that even at a scale of 1:10,000 it was difficult to draw meaningful boundaries between vegetation types, which occurred in such a fine-scale mosaic that mapping could only indicate the presence of a complex of vegetation types (Burbidge, Hopper, & Leeuwen, 1990). Six Threatened Ecological Communities are known from the Geraldton Sandplains. All six communities occur on restricted landforms and are known to be locally restricted in their occurrences. These communities are described below. • Thetis-microbialite - Stromatolite community of stratified hypersaline coastal lakes Lake Thetis contains a distinctive and diverse group of benthic microbial assemblages, each producing a mat that is associated with one specific zone within the lake. Crenulate cyanobacterial mats occur in the low-lying areas adjacent to the lake. Lithified stromatolites, resembling those at Shark Bay, with patches of living cyanobacterial mats and nodular mats characterize the littoral areas. Filamentous mats reside in cavities and coat the surface of the flocculant mat in the basin, a mobile diatomaceous mat occurs in the shallows, and thick flocculant mats of phototrophic prokaryotes, other microbes and/or diatoms occur in the central basin. Lake Thetis differs from other coastal saline lakes because it has benthic microbial mats adjacent to the lithified stromatolites and well-developed flocculant mats in the basin. Under current conditions “microbial reef-forming” communities and flocculant mat communities are both scarce, and such strong joint development is unusual. Also, some stromatolites have branching columns which are rare in modern environments. There are only ephemeral lakes within the Survey Area and therefore this TEC does not occur within the Survey Area. • Greenough River Flats - Acacia rostellifera low forest with scattered Eucalyptus camaldulensis on Greenough Alluvial Flats. Front Flats - Acacia rostellifera and Melaleuca sp.. thickets with scattered Eucalyptus

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camaldulensis over an understorey that includes Drosera bulbosa, Hypoxis glabella var. leptantha, Wurmbea densiflora, Wurmbea tubulosa, Marsilea drummondii, and Amphibromus nervosus. Back Flats - Acacia rostellifera thickets with scattered Eucalyptus camaldulensis, Eucalyptus loxophleba and Banksia sp.. scrub over an understorey that includes Hypoxis glabella var. leptantha, Panicum decompositum, Rhodanthe chlorocephala, Schoenus verbena, Wurmbea monantha and Amphibromus nervosus. This community is only known from occurrences within the Shire of Greenough. Given this, this community is not considered to occur within the Survey Area. • Ferricrete floristic community (Rocky Springs type) This tall shrubland is located on irregularly inundated red brown sandy loams over ferricrete dominated by Acacia blakelyi, Allocasuarina campestris, Banksia stricta and Labichea lanceolata subsp. lanceolata. Associated species include Alyogyne hakeifolia, Borya sphaerocephala, Isotoma hypocrateriformis, , Stylidium dichotomum, Thysanotus patersonii and Waitzia paniculata. This community was identified by DBCA database searches as occurring to the east of the Project Area. The Ferricrete floristic community (Rocky Springs type) is largely defined by the combined presence of Acacia blakelyi, Banksia strictifolia (previously Dryandra stricta) and Labichea lanceolata subsp. lanceolata. Banksia strictifolia were not identified during field surveys. Based on the survey data and the floristic composition recorded, along with the absence of ferricrete identified in the soil sub-system mapping, it is considered unlikely that the Ferricrete floristic community (Rocky Springs type) occurs within the Survey Area . • Assemblages of organic mound springs of the Three Springs area Description: This community is characterised by continuous discharge of groundwater in raised areas of peat. The community is reliant on the hydrological catchment of the Dandaragan Trough which contributes to the ‘artesian’ aquifer systems that feed the mound springs. Many moisture loving species are common to this community, including an overstorey of Melaleuca preissiana trees. Eucalyptus camaldulensis and E. rudis are also found in a number of the mound springs. The shrub layer often includes Hypocalymma angustifolium and Acacia saligna over Baumea vaginalis and other sedges, with the herbaceous Patersonia occidentalis (swamp variant) occurring at several mound springs. This community was identified by DBCA database searches as occurring to the east of the Project Area. The Dandaragan Trough does not extend westwards into the Survey Area except at the north-eastern corner of the Project Area, and no mound springs are known to occur within the proposal area. It is unlikely that the Assemblages of organic mound springs of the Three Springs area floristic community (Rocky Springs type) occurs within the Survey Area. • Lesueur-Coomallo Floristic Community D1 Description: This community comprises a species-rich low heath, on moderately to well- drained lateritic gravels on lower slopes and low rises, dominated by Allocasuarina microstachya with A. ramosissima, A. humilis, Baeckea grandiflora, Borya nitida, Calytrix flavescens, Calothamnus sanguineous, Conostylis androstemma, Cryptandra pungens, Dryandra armata, Gastrolobium polystachyum, Hakea auriculata, H. incrassata, H. aff. erinacea, Hibbertia hypericoides, Hypocalymma xanthopetalum, Melaleuca trichophylla, Petrophile chrysantha, Schoenus subflavus and Xanthorrhoea drummondii.

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This community is restricted to the lower slopes and low rises of the Banovich Uplands which do not occur within or adjacent to the Survey Area. In addition, this community is only known from one 0.1 ha occurrence on private freehold land immediately adjacent (south) to in the Shire of Dandaragan. Given this, this community is not considered to occur within the Survey Area. • Lesueur-Coomallo Floristic Community A1.2. Description: Species-rich heath with emergent on sand with faithful species of Hakea obliqua and Beaufortia aff. elegans and constant species of Dasypogon bromeliifolius and latifolia over well-drained grey sand over pale yellow sand on lateritic uplands. Associated species include Allocasuarina humilis, Calothamnus sanguineous, Hibbertia hypericoides, Hypocalymma xanthopetalum and Schoenus subflavus. This community is restricted to the lower slopes and low rises of the Banovich Uplands which do not occur within or adjacent to the Survey Area. In addition, is known only from one 31 ha occurrence within Lesueur National Park. Given this, this community is not considered to occur within the survey area. The Critically Endangered TEC Eucalypt Woodlands of the Western Australian Wheatbelt was identified by the Commonwealth PMST database search, however, the diagnostic criteria for this community specify that it only occurs in other IBRA regions. Several Priority Ecological Communities are known to occur in the Geraldton Sandplains. All seven communities occur on restricted landforms and are known to be locally restricted in their occurrences. These communities are described below. • Lesueur-Coomallo Floristic Community M2 (Melaleuca preissiana woodland) Woodland dominated by Melaleuca preissiana along sandy drainage lines, with faithful species of Anigozanthos pulcherrimus and constant species of Chamaescilla corymbosa, and Xanthorrhoea reflexa. While ephemeral drainage lines are known to occur within the project area, the above species composition does not occur. Given this, this community is not considered to occur within the Survey Area. • Lesueur-Coomallo Floristic Community DFGH Mixed species-rich heath on lateritic gravel with , Melaleuca platycalyx and Petrophile seminuda: a fine scale mixture of four floristically-defined communities occurring on lateritic slopes. This community is restricted to the lower slopes and low rises of the Banovich Uplands which do not occur within or adjacent to the Survey Area. Given this, this community is not considered to occur within the Survey Area. • Coastal sands dominated by Acacia rostellifera, Eucalyptus oraria and Eucalyptus obtusiflora Floristically, this community is similar to other Acacia rostellifera communities but is differentiated on structure, being dominated by mallee eucalypts. The community occurs on limestone ridges, in some swales in the coastal dunes between Cape Burney and Dongara, on the Greenough Alluvial Flats on limestone soil and near Tarcoola Beach. Some very small occurrences have also been recorded on the limestone scarp north of the Buller River. Coastal sands are not present within the Survey Area. As such this community is not considered to occur with the Survey Area.

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• Petrophile chrysantha low heath on Lesueur dissected uplands (Gp200-170) Low heath dominated by Petrophile chrysantha on Lesueur Dissected Uplands. Associated species include Dryandra armata and . Petrophile chrysantha, and Hakea undulata were not identified as occurring within 20 km of the survey area during the NatureMap database search. Given this, this community is not considered to occur within the Survey Area. • Subtropical and Temperate Coastal Saltmarsh Consists of the assemblage of plants, animals and micro-organisms associated with saltmarsh in coastal regions of sub-tropical and temperate Australia (south of 23°S latitude). The habitat is coastal areas under tidal influence. The Survey Area is not located within a coastal region. Given this, this community is not considered to occur within the Survey Area. 5.2 Field Survey 5.2.1 Native Flora A total of 211 native taxa from 35 plant families and 81 genera were recorded within the Survey Area (Appendix D). 5.2.2 Introduced (exotic) Taxa A total of 7 introduced (exotic) taxa were recorded within the Survey Area, as follows: • Briza maxima; • Cotula coronopifolia; • Ehrharta calycina; • Lolium sp.; • Polypogon monspeliensis; • Sonchus oleraceus; and • Ursinia anthemoides. 5.2.3 Vegetation The reconnaissance survey identified broad floristic information about the Survey Area to inform the targeted survey. Information gathered during the targeted surveys was used to supplement the data collected during the reconnaissance survey, further informing the delineation of vegetation units. Seven vegetation types (VT) (Table 5.1) were defined and mapped within the Survey Area (Figure 5.1). The most dominant VT was BaAh, which represented 43% of mapped vegetation within the Survey Area. Table 5.1: Vegetation units within the Survey Area Proportion Vegetation Description Area (ha) of Survey Code Area BaAh Mid to low shrubland to open shrubland typically dominated by Banksia 1976.44 43% attenuata and/or Allocasuarina humilis with mixed Proteaceous and Myrtaceous low shrubs (typically Banksia carlinoides, Banksia candolleana, Beaufortia elegans, and Melaleuca leuropoma) over Ecdeiocolea monostachya and/or Mesomelaena pseudostygia sparse sedgeland. BgBk Banksia glaucifolia and Banksia kippistiana var. kippistiana low shrubland to 371.24 8% open shrubland over Mesomelaena spp. Sparse sedgeland. Cl Calothamnus longissimus low shrubland. 43.97 1%

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Proportion Vegetation Description Area (ha) of Survey Code Area Er Eucalyptus rudis open woodland over Acacia saligna ad Melaleuca 1.47 0% rhaphiophylla tall shrubland. Et Eucalyptus todtiana open mallee woodland to isolated mallee trees over 1871.17 41% mixed proteaceous and myrtaceous low shrubland to open shrubland(typically dominated by Allocasuarina humilis, , Banksia candolleana, Banksia kippistiana var. kippistiana, Eremaea violacea, Hibbertia hypericoides, multiflora, Beaufortia elegans, Melaleuca leuropoma, melaleuca trichophylla, and angustifolium) over Mesomelaena pseudostygia sparse sedgeland. Patches of Eucalyptus conveniens, E. drummondii, E. gittinsii and E. macrocarpa occur within this unit. Hp and Scholtzia sp. Tall open shrubland with isolated 26.45 1% Eucalyptus todtiana. Mr Melaleuca rhaphiophylla tall shrubland with patches of Acacia blakelyi and 73.48 2% Acacia saligna tall open shrubland. Cleared 242.31 5% Total 4606.54 100% 5.2.4 Vegetation condition Most of the Survey Area was in Excellent to Pristine condition with few weeds and high native species richness (Table 5.2; Figure 5.2). Reduced vegetation condition occurred where human/livestock traffic was frequent such as farmland and near tracks. Man-made disturbances in the area included: • access tracks; • exploration tracks for drilling or seismic surveys; • borrow pits; • fences and firebreaks; • stock grazing; • off-track vehicle traffic; and • man-made structures such as sheds. In addition to man-made disturbance, the Survey Area has a varied fire history, with the most recent occurring in 2018. While the floristic composition has been impacted in parts, no evidence of frequent fire impacts were recorded. Table 5.2: Vegetation Condition within the Survey Area Proportion of Survey Condition Area (ha) Area Excellent-Pristine 4224.69 92% Excellent 107.14 2% Very Good 13.16 0% Degraded-Good 19.23 0% No vegetation 242.31 5% Total 4606.54 100% 5.2.5 Conservation significant communities No conservation significant communities were identified with the Survey Area in 2020. This is consistent with the desktop assessment of likelihood.

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Legend Scale 1:130,000 at A4 012 Survey area Vegetation type Kilometres Highways BaAh Main road BgBk Coord. Sys. GDA2020 MGA Zone 50 Z VEGETATION UNIT MAPPING Minor road Cl Track Er Job No: 59367 Et Client: Strike West Ltd FIGURE 5.1 Hp Mr Version: A Date: 29-Mar-2021 Cleared Drawn By: cthatcher Checked By: TS

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Legend Scale 1:130,000 at A4 012 Survey area Highways Kilometres Vegetation condition Main road Excellent-pristine Minor road Coord. Sys. GDA2020 MGA Zone 50 Z VEGETATION CONDITION MAPPING Excellent Track Very good Job No: 59367 Degraded-good Client: Strike West Ltd FIGURE 5.2 No vegetation Version: A Date: 29-Mar-2021

Drawn By: cthatcher Checked By: TS

File Name: W:\Projects\1)Open\Strike West\59367 Ocean Hill Ecology Surveys\GIS\Maps\R01_Rev_A\59367_04_2_VegCond.mxd Image Reference: Source: Esri, DigitalGlobe, GeoEye, Earthstar Geographics, CNES/Airbus DS, USDA, USGS, AeroGRID, IGN, and the GIS User Community & Client imagery June 2020. 5.2.6 Conservation significant flora No Threatened flora species listed under the EPBC Act were recoded with the Survey Area in either the 2016 or 2020 survey. There were 15 Priority flora species (Table 5.3; Figure 5.3; Appendix E) recorded across both surveys. The dominate Priority listed taxa within the survey area were Allocasuarina ramosissima (P3) Banksia fraseri var. crebra (P3), Hemiandra sp. Eneabba (H. Demarz 3687) (P3), and Calytrix chrysantha (P4). Two taxa, unable to be positively identified to species level were also recorded, Hemiandra aff. sp. Eneabba (H. Demarz 3687) and Hemiandra aff. sp. Kalbarri (D. Bellairs 1505). Both taxa have affinities to Priority listed flora; however, identification with current taxonomic data was not possible. In the absence of further taxonomic work, impacts to these taxa should be avoided. Table 5.3: Conservation significant flora identified during 2016 and 2020 surveys. Taxon Conservation status Number of individuals Verticordia luteola var. rosea P1 5 Persoonia filiformis P2 4 Allocasuarina ramosissima P3 360 Banksia fraseri var crebra P3 164 Jacksonia anthoclada P3 126 P3 1 Phlebocarya pilosissima subsp. pilosissima P3 28 Stylidium ?hymenocraspedum P3 1 Verticordia fragrans P3 3 Hemiandra sp. Eneabba (H. Demarz 3687) P3 163 P4 105 Calytrix chrysantha P4 1825 Calytrix eneabbensis P4 84 Eremaea acutifolia P4 6 Verticordia aurea P4 18 Hemiandra aff. sp. Eneabba (H. Demarz 3687) Other 9 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) Other 89

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Survey area ! Hemiandra sp. Eneabba Scale 1:62,000 at A4 00.51 ! Jacksonia anthoclada Conservation significant flora Kilometres ! # Allocasuarina ramosissima Persoonia filiformis # ! Persoonia rudis CONSERVATION SIGNIFICANT FLORA Banksia chamaephyton Coord. Sys. GDA2020 MGA Zone 50 RECORDED WITHIN THE SURVEY AREA # Banksia fraseri var crebra " Phlebocarya pilosissima Z subsp. pilosissima # Banksia fraseri var. crebra # " Stylidium Job No: 59367 Calytrix chrysantha ?hymenocraspedum # Calytrix eneabbensis " ?endothrix Client: Strike West Ltd FIGURE 5.3 ! Hemiandra aff. Eneabba (H. " Demarz 3687) Verticordia aurea " Verticordia fragrans Version: A Date: 30-Mar-2021 Hemiandra aff. sp. Kalbarri ! " Verticordia luteola var. rosea (D. Bellairs 1505) Drawn By: cthatcher Checked By: TS

File Name: W:\Projects\1)Open\Strike West\59367 Ocean Hill Ecology Surveys\GIS\Maps\R01_Rev_A\59367_04_3_ConSigFlora.mxd Image Reference: Source: Esri, DigitalGlobe, GeoEye, Earthstar Geographics, CNES/Airbus DS, USDA, USGS, AeroGRID, IGN, and the GIS User Community & Client imagery June 2020.

6. Discussion

All proposed seismic lines within the main Survey Area have been assessed by targeted surveys in 2020. The Survey Area exhibited a high degree of variability and native species richness, consistent with intact vegetation of the region. The vegetation was generally in Excellent-Pristine condition in areas of remnant vegetation which had no human traffic. Six (6) TECs and seven (7) PECs were identified during the desktop study as potentially occurring with the Survey Area. These conservation significant communities were considered unlikely to occur within the Survey Area which was confirmed by the field assessment, with no similarities to conservation significant communities present within the bioregion. No threatened (T) listed taxa were recorded by Strategen JBS & G within the survey area in 2020. Two threatened flora have previously been recorded within the Survey Area; Hakea megalosperma and Thelymitra stellata. Both taxa have a preference to occur on exposed laterite. This habitat is present within the Survey Area; however, the proposed seismic lines which were surveyed avoided these areas. The absence of this habitat occurring within the survey lines is the likely reason for these two taxa not being recorded during this surveys. Of the 72 Priority Flora species identified by the DBCA and NatureMap database searches 15 were recorded over the 2016 and 2020 field surveys. Two Priority flora taxa have a wide geographic distribution both within the current survey boundary and outside the Survey Area, which reduces the potential impacts caused by the project. These species include: • Banksia fraseri var. crebra (P3) • Hemiandra sp. Eneabba (H. Demarz 3687) (P3). The remaining 13 priority listed taxa recorded within the Survey Area (including the P1 listed species Verticordia luteola var. rosea) were recorded in low numbers (less than 50 total individual plants) (Table 5.3) within the Survey Area. These species are not well represented within the region and it is suggested that avoidance strategies be implemented to reduce the impact of clearing via mulching on the extant populations of these species.

©JBS&G Australia Pty Ltd T/A Strategen-JBS&G | JBS&G59367- 136,162 (Rev 0) 24 7. Limitations

This report has been prepared for use by the client who has commissioned the works in accordance with the project brief only and has been based in part on information obtained from the client and other parties. The advice herein relates only to this project and all results conclusions and recommendations made should be reviewed by a competent person with experience in environmental investigations, before being used for any other purpose. Strategen-JBS&G accepts no liability for use or interpretation by any person or body other than the client who commissioned the works. This report should not be reproduced without prior approval by the client, or amended in any way without prior approval by Strategen-JBS&G, and should not be relied upon by other parties, who should make their own enquires.

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8. References

ANZECC. (2000). Review of the National Strategy for the Conservation of Australia's Biological Diversity. Canberra: Australian and New Zealand Environment and Conservation Council (ANZECC), Environment Australia. BOM. (2020). Climate Data Online. (Station 009225, Perth Metro WA). Bureau of Meterology (BOM). Retrieved February 11, 2020, from http://www.bom.gov.au/climate/data Burbidge, A., Hopper, S. D., & Leeuwen, S. v. (1990). Nature Conservation, Landscape and Recreation Values of the Lesueur area. Perth: Department of Conservation and Land Management for the Environmental Protection Authority. CANBR. (2015). EUCLID: Eucalypts of Australia (Fourth Edition). (Fourth). Centre for Australian National Biodiversity Research (CANBR), CSIRO Publishing. Crayn, D., Hislop, M., & Puente-Lelievre, C. (2020). A phylogenetic recircumscription of Styphelia (Ericaceae, Epacridoideae, Styphelieae). Australian Systematic Botany, 33, 137-168. CSIRO. (1991). Digital Atlas of Australian Soils. DBCA. (2019). DBCA Fire History (DBCA_060). Perth: Department of Biodiversity, Conservation and Attractions (DBCA). Retrieved from https://data.wa.gov.au/ Department of the Environment. (2012). Interim Biogeographic Regionalisation for Australia v. 7 (IBRA) [ESRI shapefile]. Retrieved 2018, from http://intspat01.ris.environment.gov.au/fed/catalog/search/resource/details.page?uuid=%7 B3C182B5A-C081-4B56-82CA-DF5AF82F Desmond, A., & Chant, A. (2002). Geraldton Sandplain 3 (GS3 - Lesueur Sandplain subregion). In D. o. Management, A Biodiversity Audit of Western Australia’s 53 Biogeographical Subregions in 2002 (pp. 293-313). Perth. DPIRD. (2018). Soil-landscape mapping Western Australia – Best available (DPIRD-027). Western Australia: Department of Primary Industries and Regional Development (DPIRD). Retrieved January 23, 2019, from https://data.wa.gov.au/ Ecologia. (2012). DRAFT RPS Origin Dongara Targeted Flora Assessment. West Perth: Unpublished report produced for RPS Group Australia by Ecologia Environment (Ecologia). EPA. (2000). Position Statement No. 2. Environmental Protection of Native Vegetation in Western Australia. Perth: Environmental Protection Authority (EPA). EPA. (2016). Environmental Factor Guideline Flora and Vegetation. Perth: Environmental Protection Agency (EPA). EPA. (2016). Technical Guidance - Flora and Vegetation Surveys for Environmental Impact Assessment. Perth: Environmental Protection Authority (EPA). French, M., & Nicolle, D. (2019). Eucalypts of Western Australia The South-west Coast and Ranges. Perth: Malcolm French. NVIS Technical Working Group. (2017). Australian Vegetation Attribute Manual Version 7.0. Canberra: NVIS Technical Working Group, Department of the Environment and Energy.

©JBS&G Australia Pty Ltd T/A Strategen-JBS&G | JBS&G59367- 136,162 (Rev 0) 26 Appendix A Conservation significant flora and ecological community definition CONSERVATION CODES For Western Australian Flora and Fauna

Threatened, Extinct and Specially Protected fauna or flora1 are species2 which have been adequately searched for and are deemed to be, in the wild, threatened, extinct or in need of special protection, and have been gazetted as such.

The Wildlife Conservation (Specially Protected Fauna) Notice 2018 and the Wildlife Conservation (Rare Flora) Notice 2018 have been transitioned under regulations 170, 171 and 172 of the Biodiversity Conservation Regulations 2018 to be the lists of Threatened, Extinct and Specially Protected species under Part 2 of the Biodiversity Conservation Act 2016.

Categories of Threatened, Extinct and Specially Protected fauna and flora are:

T Threatened species

Listed by order of the Minister as Threatened in the category of critically endangered, endangered or vulnerable under section 19(1), or is a rediscovered species to be regarded as threatened species under section 26(2) of the Biodiversity Conservation Act 2016 (BC Act). Threatened fauna is that subset of ‘Specially Protected Fauna’ listed under schedules 1 to 3 of the Wildlife Conservation (Specially Protected Fauna) Notice 2018 for Threatened Fauna. Threatened flora is that subset of ‘Rare Flora’ listed under schedules 1 to 3 of the Wildlife Conservation (Rare Flora) Notice 2018 for Threatened Flora. The assessment of the conservation status of these species is based on their national extent and ranked according to their level of threat using IUCN Red List categories and criteria as detailed below.

CR Critically endangered species

Threatened species considered to be “facing an extremely high risk of extinction in the wild in the immediate future, as determined in accordance with criteria set out in the ministerial guidelines”. Listed as critically endangered under section 19(1)(a) of the BC Act in accordance with the criteria set out in section 20 and the ministerial guidelines. Published under schedule 1 of the Wildlife Conservation (Specially Protected Fauna) Notice 2018 for critically endangered fauna or the Wildlife Conservation (Rare Flora) Notice 2018 for critically endangered flora.

EN Endangered species

Threatened species considered to be “facing a very high risk of extinction in the wild in the near future, as determined in accordance with criteria set out in the ministerial guidelines”. Listed as endangered under section 19(1)(b) of the BC Act in accordance with the criteria set out in section 21 and the ministerial guidelines. Published under schedule 2 of the Wildlife Conservation (Specially Protected Fauna) Notice 2018 for endangered fauna or the Wildlife Conservation (Rare Flora) Notice 2018 for endangered flora.

VU Vulnerable species

Threatened species considered to be “facing a high risk of extinction in the wild in the medium-term future, as determined in accordance with criteria set out in the ministerial guidelines”. Listed as vulnerable under section 19(1)(c) of the BC Act in accordance with the criteria set out in section 22 and the ministerial guidelines. Published under schedule 3 of the Wildlife Conservation (Specially Protected Fauna) Notice 2018 for vulnerable fauna or the Wildlife Conservation (Rare Flora) Notice 2018 for vulnerable flora.

Conservation codes for Western Australian flora and fauna

Extinct species

Listed by order of the Minister as extinct under section 23(1) of the BC Act as extinct or extinct in the wild.

EX Extinct species

Species where “there is no reasonable doubt that the last member of the species has died”, and listing is otherwise in accordance with the ministerial guidelines (section 24 of the BC Act). Published as presumed extinct under schedule 4 of the Wildlife Conservation (Specially Protected Fauna) Notice 2018 for extinct fauna or the Wildlife Conservation (Rare Flora) Notice 2018 for extinct flora.

EW Extinct in the wild species

Species that “is known only to survive in cultivation, in captivity or as a naturalised population well outside its past range; and it has not been recorded in its known habitat or expected habitat, at appropriate seasons, anywhere in its past range, despite surveys over a time frame appropriate to its life cycle and form”, and listing is otherwise in accordance with the ministerial guidelines (section 25 of the BC Act). Currently there are no threatened fauna or threatened flora species listed as extinct in the wild. If listing of a species as extinct in the wild occurs, then a schedule will be added to the applicable notice.

Specially protected species

Listed by order of the Minister as specially protected under section 13(1) of the BC Act. Meeting one or more of the following categories: species of special conservation interest; migratory species; cetaceans; species subject to international agreement; or species otherwise in need of special protection. Species that are listed as threatened species (critically endangered, endangered or vulnerable) or extinct species under the BC Act cannot also be listed as Specially Protected species.

MI Migratory species

Fauna that periodically or occasionally visit Australia or an external Territory or the exclusive economic zone; or the species is subject of an international agreement that relates to the protection of migratory species and that binds the Commonwealth; and listing is otherwise in accordance with the ministerial guidelines (section 15 of the BC Act). Includes birds that are subject to an agreement between the government of Australia and the governments of Japan (JAMBA), China (CAMBA) and The Republic of Korea (ROKAMBA), and fauna subject to the Convention on the Conservation of Migratory Species of Wild Animals (Bonn Convention), an environmental treaty under the United Nations Environment Program. Migratory species listed under the BC Act are a subset of the migratory animals, that are known to visit Western Australia, protected under the international agreements or treaties, excluding species that are listed as Threatened species. Published as migratory birds protected under an international agreement under schedule 5 of the Wildlife Conservation (Specially Protected Fauna) Notice 2018.

CD Species of special conservation interest (conservation dependent fauna)

Fauna of special conservation need being species dependent on ongoing conservation intervention to prevent it becoming eligible for listing as threatened, and listing is otherwise in accordance with the ministerial guidelines (section 14 of the BC Act). Published as conservation dependent fauna under schedule 6 of the Wildlife Conservation (Specially Protected Fauna) Notice 2018.

OS Other specially protected species

Fauna otherwise in need of special protection to ensure their conservation, and listing is otherwise in accordance with the ministerial guidelines (section 18 of the BC Act). Published as other specially protected fauna under schedule 7 of the Wildlife Conservation (Specially Protected Fauna) Notice 2018.

Conservation codes for Western Australian flora and fauna

P Priority species

Possibly threatened species that do not meet survey criteria, or are otherwise data deficient, are added to the Priority Fauna or Priority Flora Lists under Priorities 1, 2 or 3. These three categories are ranked in order of priority for survey and evaluation of conservation status so that consideration can be given to their declaration as threatened fauna or flora. Species that are adequately known, are rare but not threatened, or meet criteria for near threatened, or that have been recently removed from the threatened species or other specially protected fauna lists for other than taxonomic reasons, are placed in Priority 4. These species require regular monitoring. Assessment of Priority codes is based on the Western Australian distribution of the species, unless the distribution in WA is part of a contiguous population extending into adjacent States, as defined by the known spread of locations.

1 Priority 1: Poorly-known species Species that are known from one or a few locations (generally five or less) which are potentially at risk. All occurrences are either: very small; or on lands not managed for conservation, e.g. agricultural or pastoral lands, urban areas, road and rail reserves, gravel reserves and active mineral leases; or otherwise under threat of habitat destruction or degradation. Species may be included if they are comparatively well known from one or more locations but do not meet adequacy of survey requirements and appear to be under immediate threat from known threatening processes. Such species are in urgent need of further survey.

2 Priority 2: Poorly-known species Species that are known from one or a few locations (generally five or less), some of which are on lands managed primarily for nature conservation, e.g. national parks, conservation parks, nature reserves and other lands with secure tenure being managed for conservation. Species may be included if they are comparatively well known from one or more locations but do not meet adequacy of survey requirements and appear to be under threat from known threatening processes. Such species are in urgent need of further survey.

3 Priority 3: Poorly-known species Species that are known from several locations, and the species does not appear to be under imminent threat, or from few but widespread locations with either large population size or significant remaining areas of apparently suitable habitat, much of it not under imminent threat. Species may be included if they are comparatively well known from several locations but do not meet adequacy of survey requirements and known threatening processes exist that could affect them. Such species are in need of further survey.

4 Priority 4: Rare, Near Threatened and other species in need of monitoring (a) Rare. Species that are considered to have been adequately surveyed, or for which sufficient knowledge is available, and that are considered not currently threatened or in need of special protection but could be if present circumstances change. These species are usually represented on conservation lands. (b) Near Threatened. Species that are considered to have been adequately surveyed and that are close to qualifying for vulnerable but are not listed as Conservation Dependent. (c) Species that have been removed from the list of threatened species during the past five years for reasons other than .

1 The definition of flora includes algae, fungi and lichens 2Species includes all taxa (plural of taxon - a classificatory group of any taxonomic rank, e.g. a family, , species or any infraspecific category i.e. subspecies or variety, or a distinct population).

Last updated 3 January 2019

Appendix B Desktop assessment results

NatureMap Species Report Created By Lachlan Warner on 12/06/2020

Origin Native Conservation Status Conservation Taxon (T, X, IA, S, P1-P5) Current Names Only Yes Core Datasets Only Yes Method 'By Polygon' Vertices 29° 36' 37" S,115° 08' 58" E 29° 36' 48" S,115° 27' 55" E 29° 41' 31" S,115° 38' 56" E 30° 15' Group By 52" S,115° 38' 50" E 30° 15' 34" S,115° 08' 24" E Conservation Status

Conservation Status Species Records Other specially protected fauna 1 2 Priority 1 14 59 Priority 2 58 456 Priority 3 87 846 Priority 4 43 732 Protected under international agreement 9 31 Rare or likely to become extinct 40 1098 TOTAL 252 3224

Name ID Species Name Naturalised Conservation Code 1Endemic To Query Area Rare or likely to become extinct 1. 3341 Acacia forrestiana (Forrest's Wattle) T 2. 14154 Acacia wilsonii T 3. 32622 Banksia catoglypta T Y 4. 32083 subsp. perissa T 5. 24784 Calidris ferruginea (Curlew Sandpiper) T 6. 24734 Calyptorhynchus latirostris (Carnaby's Cockatoo, White-tailed Short-billed Black T Cockatoo) 7. 48400 Calyptorhynchus sp. (white-tailed black cockatoo) T 8. 25086 Cyclodomorphus branchialis (Gilled Slender Blue-tongue Skink) T 9. 34776 Darwinia chapmaniana T 10. 13632 Daviesia speciosa T 11. 25107 Egernia stokesii subsp. badia (Western Spiny-tailed Skink, Gidgee Skink) T 12. 17605 Eleocharis keigheryi T 13. 17150 Eremophila glabra subsp. chlorella T 14. 48632 Eremophila subangustifolia T 15. 24043 Eubalaena australis (Southern Right Whale) T 16. 12885 Eucalyptus crispata (Yandanooka Mallee) T 17. 13532 Eucalyptus impensa T Y 18. 5680 Eucalyptus johnsoniana (Johnson's Mallee) T 19. 5691 Eucalyptus lateritica (Laterite Mallee) T 20. 13543 Eucalyptus leprophloia (Scaly Butt Mallee) T 21. 14280 Eucalyptus rhodantha var. rhodantha T 22. 5781 Eucalyptus suberea (Mount Lesueur Mallee) T 23. 3904 Gastrolobium hamulosum (Hookpoint Poison) T 24. 33558 subsp. althoferorum T Y 25. 1960 T Y 26. 15987 T 27. 2180 Hakea megalosperma (Lesueur Hakea) T 28. 6841 Hemiandra rutilans (Colourful Snakebush) T 29. 33917 Idiosoma nigrum (Shield-backed Trapdoor Spider) T 30. 6418 Leucopogon obtectus (Hidden Beard-heath) T Y 31. 24180 Macroderma gigas (Ghost Bat) T 32. 13867 Paracaleana dixonii T 33. 19769 T Y 34. 41348 Pezoporus flaviventris (Western Ground Parrot) T 35. 24905 Pogona minor subsp. minima (Abrolhos Dwarf Bearded Dragon, Dwarf Bearded T Dragon (Houtman Abrolhos Is.)) 36. 2360 Spirogardnera rubescens (Spiral Bush) T

NatureMap is a collaborative project of the Department of Biodiversity, Conservation and Attractions and the Western Australian Museum.

Page 1 Name ID Species Name Naturalised Conservation Code 1Endemic To Query Area 37. 48294 Styphelia longissima T Y 38. 23989 Tetratheca nephelioides T 39. 10862 Thelymitra stellata (Star Orchid) T 40. 12389 Verticordia albida T Protected under international agreement 41. 41323 Actitis hypoleucos (Common Sandpiper) IA 42. 24779 Calidris acuminata (Sharp-tailed Sandpiper) IA 43. 24780 Calidris alba (Sanderling) IA 44. 24788 Calidris ruficollis (Red-necked Stint) IA 45. 24843 Plegadis falcinellus (Glossy Ibis) IA 46. 24383 Pluvialis squatarola (Grey Plover) IA 47. 24716 Puffinus pacificus (Wedge-tailed Shearwater) IA 48. 24806 Tringa glareola (Wood Sandpiper) IA 49. 24808 Tringa nebularia (Common Greenshank, greenshank) IA Other specially protected fauna 50. 25624 Falco peregrinus (Peregrine Falcon) S Priority 1 51. 48324 Chamaescilla maculata (Red-Spotted Squill) P1 52. 17440 Grevillea metamorpha P1 Y 53. 48402 Grevillea sp. Cooljarloo (B.J. Keighery 28 B) P1 54. 19556 Grevillea stenogyne P1 Y 55. 5820 Hypocalymma linifolium P1 56. 19847 Korthalsella arthroclada P1 57. 19245 Lyginia excelsa P1 58. 45768 Poranthera asybosca (Cerebriform-seeded Poranthera) P1 Y 59. 44468 Ptilotus falcatus P1 Y 60. 30715 Stylidium carnosum subsp. Narrow leaves (J.A. Wege 490) P1 61. 48461 Stylidium strigosum P1 Y 62. 19316 Stylidium tinkeri P1 63. 4542 Tetratheca remota P1 64. 14688 Verticordia luteola var. rosea P1 Priority 2 65. 14055 Acacia carens P2 66. 14931 Acacia lasiocarpa var. lasiocarpa Cockleshell Gully variant (E.A. Griffin 2039) P2 67. 3518 Acacia retrorsa P2 68. 14153 Acacia vittata P2 69. 43509 Amanita lesueurii P2 70. 17647 Andersonia sp. Mt Lesueur (E.A. Griffin 5536) P2 Y 71. 32526 Banksia fraseri var. effusa P2 Y 72. 4600 Beyeria similis P2 73. 16625 Boronia ramosa subsp. lesueurana P2 Y 74. 16637 Boronia scabra subsp. condensata P2 75. 19304 Calectasia browneana P2 76. 19196 Calectasia palustris P2 77. 35697 Calothamnus arcuatus P2 78. 5475 Calytrix purpurea P2 79. 17812 Catacolea enodis P2 80. 13765 Caustis gigas (Giant Twigrush) P2 81. 19243 Chordifex reseminans P2 82. 14663 Comesperma griffinii P2 83. 44485 Conostylis sp. Eneabba (M. Hislop 3864) P2 Y 84. 35837 Cristonia biloba subsp. pubescens P2 85. 18441 Dampiera sp. Jurien (G. Lullfitz s.n. 10/7/1986) P2 86. 42900 Darwinia sp. Strawberry (M.G. Corrick 8279) P2 87. 11562 Daviesia debilior subsp. debilior P2 Y 88. 12898 Eucalyptus abdita P2 89. 13545 Eucalyptus angularis P2 90. 20162 Fabronia hampeana P2 91. 7566 Goodenia xanthotricha (Yellow-haired Goodenia) P2 92. 15815 Grevillea delta P2 Y 93. 17286 Guichenotia quasicalva P2 94. 33976 Hemisaga vepreculae (thorny bush katydid (Moora), bush cricket (Moora)) P2 95. 5807 Homalocalyx chapmanii P2 96. 31412 Hypocalymma sp. Gairdner Range (C.A. Gardner 9091) P2 Y 97. 16179 Hypocalymma tenuatum P2 Y 98. 14751 Jacksonia rubra P2 99. 48757 Lasiopetalum decoratum P2 100. 48347 Lasiopetalum rutilans P2

NatureMap is a collaborative project of the Department of Biodiversity, Conservation and Attractions and the Western Australian Museum.

Page 2 Name ID Species Name Naturalised Conservation Code 1Endemic To Query Area 101. 19241 Lepyrodia curvescens P2 102. 6432 Leucopogon plumuliflorus P2 103. 17837 Loxocarya gigas P2 104. 46515 Micromyrtus uniovulum P2 105. 14220 Millotia jacksonii P2 106. 19763 Petrophile clavata P2 107. 11906 Phlebocarya pilosissima subsp. teretifolia P2 108. 44602 Ptilotus clivicola P2 Y 109. 12583 Scaevola eneabba P2 Y 110. 19945 Schoenus sp. Eneabba (F. Obbens & C. Godden I154) P2 111. 49108 Scholtzia calcicola (Tiny-flowered Scholtzia) P2 112. 14236 Stenanthemum limitatum P2 113. 40943 Stylidium cornuatum P2 114. 20531 Stylidium diplotrichum P2 Y 115. 33080 Stylidium sp. Three Springs (J.A. Wege & C. Wilkins JAW 600) P2 116. 15530 Synaphea lesueurensis P2 117. 16764 Synaphea sparsiflora P2 118. 30452 Synaphea xela P2 119. 20734 Thelymitra pulcherrima P2 120. 44700 Thryptomene spicata P2 121. 12391 Verticordia argentea P2 122. 2792 Walteranthus erectus P2 Priority 3 123. 14066 Acacia cummingiana P3 124. 3319 Acacia epacantha P3 125. 3338 Acacia flabellifolia P3 126. 14612 Acacia latipes subsp. licina P3 127. 3493 Acacia plicata P3 128. 13075 Acacia telmica P3 129. 1729 Allocasuarina grevilleoides P3 130. 1736 Allocasuarina ramosissima P3 131. 1263 Arnocrinum gracillimum P3 132. 19959 Austrostipa sp. Cairn Hill (M.E. Trudgen 21176) P3 133. 32596 Banksia cypholoba P3 134. 32527 Banksia fraseri var. crebra P3 135. 32216 Banksia kippistiana var. paenepeccata P3 136. 32206 Banksia nana (Dwarf Dryandra) P3 137. 32201 Banksia nobilis subsp. fragrans P3 138. 32138 Banksia pteridifolia subsp. vernalis P3 139. 32073 Banksia splendida subsp. macrocarpa P3 140. 32037 Banksia subulata (Awled Honeypot) P3 141. 5377 Beaufortia bicolor (Badgingarra Beaufortia) P3 142. 5384 Beaufortia eriocephala (Woolly Bottlebrush, Woolly Beaufortia) P3 143. 4596 Beyeria gardneri P3 144. 31606 Blackallia nudiflora (Wedge-leaved Cryptandra) P3 145. 19980 Calytrix ecalycata subsp. brevis P3 146. 19979 Calytrix ecalycata subsp. ecalycata P3 147. 45093 Centrolepis milleri P3 148. 4560 Comesperma rhadinocarpum (Slender-fruited Comesperma) P3 149. 1870 eatoniae P3 150. 1881 Conospermum scaposum P3 151. 14201 Daviesia pteroclada P3 Y 152. 16593 Desmocladus biformis P3 153. 48789 Drosera prophylla P3 154. 16887 Eucalyptus macrocarpa x pyriformis P3 155. 23489 Gompholobium gairdnerianum P3 156. 15764 subsp. cymbiformis P3 157. 12219 P3 158. 1999 Grevillea erinacea P3 159. 19567 Grevillea florida P3 160. 2013 P3 161. 2030 Grevillea leptopoda P3 162. 2036 Grevillea makinsonii P3 163. 14423 subsp. thyrsoides P3 164. 13900 Grevillea uniformis P3 165. 13233 Guichenotia alba P3 166. 1469 Haemodorum loratum P3 167. 12230 Hakea longiflora P3 168. 19411 Hemiandra sp. Eneabba (H. Demarz 3687) P3 169. 1292 Hensmania stoniella

NatureMap is a collaborative project of the Department of Biodiversity, Conservation and Attractions and the Western Australian Museum.

Page 3 Name ID Species Name Naturalised Conservation Code 1Endemic To Query Area P3 170. 17742 Hopkinsia anoectocolea P3 171. 33977 Hylaeus globuliferus (woolybush bee) P3 172. 20851 Hypocalymma gardneri P3 173. 29775 drummondii P3 174. 14747 Jacksonia anthoclada P3 175. 4003 Jacksonia carduacea P3 176. 7578 Lechenaultia juncea (Reed-like Leschenaultia) P3 177. 13775 Lepidobolus quadratus P3 178. 48179 Leucopogon foliosus P3 179. 11623 Mesomelaena stygia subsp. deflexa P3 180. 25249 Neelaps calonotos (Black-striped Snake, black-striped burrowing snake) P3 181. 1541 Patersonia argyrea P3 182. 14563 Persoonia filiformis P3 183. 2271 Persoonia rudis P3 184. 2285 Petrophile biternata P3 185. 40742 Petrophile septemfida P3 186. 11557 Phlebocarya pilosissima subsp. pilosissima P3 187. 11132 Platysace ramosissima P3 188. 43540 Stackhousia sp. Red-blotched corolla (A. Markey 911) P3 189. 12855 Stylidium drummondianum P3 190. 13127 Stylidium maritimum P3 191. 7766 Stylidium nonscandens P3 192. 7771 Stylidium periscelianthum (Pantaloon Triggerplant) P3 193. 17414 Stylidium torticarpum P3 194. 48296 Styphelia filamentosa P3 195. 48297 Styphelia filifolia P3 196. 16858 Synaphea endothrix P3 197. 15531 Synaphea oulopha P3 198. 23982 Tetratheca angulata P3 199. 4543 Tetratheca retrorsa P3 200. 1317 Thysanotus anceps P3 201. 1359 Thysanotus vernalis P3 202. 19038 Triglochin protuberans P3 203. 12390 Verticordia amphigia P3 204. 12413 Verticordia densiflora var. roseostella P3 205. 12425 Verticordia fragrans P3 206. 12434 Verticordia insignis subsp. eomagis P3 207. 14715 Verticordia luteola var. luteola P3 208. 14716 Verticordia muelleriana subsp. muelleriana P3 209. 12456 Verticordia rutilastra P3 Priority 4 210. 4397 Asterolasia drummondii (Gairdner Range Starbush) P4 211. 1810 Banksia chamaephyton (Fishbone Banksia) P4 212. 1816 Banksia elegans (Elegant Banksia) P4 213. 1853 Banksia tricuspis (Pine Banksia) P4 214. 5396 Calothamnus accedens P4 215. 5447 Calytrix chrysantha P4 216. 5455 Calytrix eneabbensis P4 217. 5480 Calytrix superba (Superb Starflower) P4 218. 19026 Conostephium magnum P4 219. 15828 Desmocladus elongatus P4 220. 12936 Diuris recurva P4 221. 5642 Eucalyptus exilis (Boyagin Mallee) P4 222. 16886 Eucalyptus loxophleba x wandoo P4 223. 13531 Eucalyptus macrocarpa subsp. elachantha (Small-leaved Mottlecah) P4 224. 5741 Eucalyptus pendens (Badgingarra Mallee) P4 225. 16944 Eucalyptus x carnabyi P4 226. 13544 Eucalyptus zopherophloia (Blackbutt Mallee) P4 227. 5202 Frankenia glomerata (Cluster Head Frankenia) P4 228. 2054 (Olive Grevillea) P4 229. 2086 P4 230. 2087 (Pouched Grevillea) P4 231. 2186 P4 232. 14595 Hemiandra sp. Watheroo (S. Hancocks 4) P4 233. 35518 Hibbertia propinqua P4 Y 234. 6233 Hydrocotyle lemnoides (Aquatic Pennywort) P4 235. 17622 Hypolaena robusta P4 236. 3042 Lepidium pseudotasmanicum P4 237. 13774 Lepidobolus densus

NatureMap is a collaborative project of the Department of Biodiversity, Conservation and Attractions and the Western Australian Museum.

Page 4 Name ID Species Name Naturalised Conservation Code 1Endemic To Query Area P4 238. 36203 Liparophyllum congestiflorum P4 239. 24328 Oxyura australis (Blue-billed Duck) P4 240. 6825 Pityrodia viscida P4 241. 17026 Scaevola kallophylla P4 242. 17606 Schoenus griffinianus P4 243. 1314 Stawellia dimorphantha (Arrowsmith Stilt-lily) P4 244. 7680 Stylidium aeonioides P4 245. 7743 Stylidium inversiflorum P4 246. 7756 Stylidium longitubum (Jumping Jacks) P4 247. 11032 Thelymitra apiculata P4 248. 48135 Thinornis rubricollis (Hooded Plover, Hooded Dotterel) P4 249. 1334 Thysanotus glaucus P4 250. 12393 Verticordia aurea P4 251. 6106 Verticordia penicillaris P4 252. 6294 Xanthosia tomentosa (Lesueur Southern Cross) P4

Conservation Codes T - Rare or likely to become extinct X - Presumed extinct IA - Protected under international agreement S - Other specially protected fauna 1 - Priority 1 2 - Priority 2 3 - Priority 3 4 - Priority 4 5 - Priority 5

1 For NatureMap's purposes, species flagged as endemic are those whose records are wholely contained within the search area. Note that only those records complying with the search criterion are included in the calculation. For example, if you limit records to those from a specific datasource, only records from that datasource are used to determine if a species is restricted to the query area.

NatureMap is a collaborative project of the Department of Biodiversity, Conservation and Attractions and the Western Australian Museum.

Page 5

Appendix C Conservation significant flora species potentially occurring within Survey Area. Table C.1: Likelihood of occurrence of Threatened flora species Likelihood Taxon Habitat Flowering period of occurrence Banksia catoglypta Lateritic breakaways. June to July Likely Eucalyptus johnsoniana White/grey sand with lateritic gravel. Sandplains, lateritic July to August, Likely breakaways. October to December or January to May Eucalyptus lateritica White or grey sand with gravel. Lateritic breakaways & August to October Likely mesas. Eucalyptus leprophloia White or grey sand over August to October Likely laterite. Valley slopes. Eucalyptus suberea Grey sand. Near or on lateritic breakaways. November to Recorded December or January Gastrolobium hamulosum Sandy, often gravelly soils or clay. Flats, slopes, ridges. August to October Likely Hakea megalosperma Grey sand, loam. Lateritic hills & rocks. May to June Recorded Paracaleana dixonii Grey sand over granite. October to Likely December or January Petrophile nivea Dry bare white sand over May to July Likely gravel over laterite. Uplands. Tetratheca nephelioides White-grey sand, yellow-brown clayey sand, gravel, September Likely laterite. Outcrops, undulating hills, ridges. Thelymitra stellata Sand, gravel, lateritic loam. October to Recorded November Table C.2: Likelihood of occurrence of Priority flora species Likelihood Conservation Taxon Habitat Flowering period of Status occurrence Ptilotus falcatus P1 Slopes in low heath on gravelly, grey to light brown sandy October to Likely loam soils. November Acacia retrorsa P2 Grey sand & lateritic gravel, sandy loam. August to Likely September Arnocrinum gracillimum P2 White, grey, yellow or lateritic sand. October to Likely November Boronia scabra subsp. P2 Sandy clay or gravel. Upper slopes, edges of lateritic August Likely condensata breakaways. Calectasia browneana P2 White-grey sand, laterite. Adjacent to wet areas of creek June to August Recorded line. Catacolea enodis P2 Deep white sand over laterite. Tall heath. No information Likely Desmocladus microcarpus P2 Open sandy dry heath or woodland. September to Likely November Hypocalymma tenuatum P2 Sandy loam over sandstone. Outcrops, ridges. July to August Likely Lepyrodia curvescens P2 Sand, laterite. Seasonally inundated swampland. September to Unlikely November Loxocarya gigas P2 Sandy gravelly lateritic soils. Low hills & ridges, sandplains. October Likely Persoonia filiformis P2 Yellow or white sand over laterite. November to Likely December Petrophile clavata P2 Grey sand, laterite. Hilltops and rises. September Recorded Ptilotus clivicola P2 Kwongan heath on gently sloping gravelly rises with shallow October to Likely coarse sand. November Synaphea endothrix P2 Gravelly loam, sand. Lateritic rises. August to Likely September Verticordia argentea P2 White, grey or yellow sand. Sand ridges, undulating plains. Nov to Dec or Jan Likely to Apr

Likelihood Conservation Taxon Habitat Flowering period of Status occurrence Acacia cummingiana P3 Grey or yellow sand, lateritic gravel. Sandplains, lateritic May to June or Likely breakaways. August Acacia epacantha P3 Lateritic gravelly loam or clay. July to August Recorded Allocasuarina P3 Sand over laterite, gravel. Likely grevilleoides Allocasuarina P3 Lateritic soils, gravel. September Recorded ramosissima Banksia fraseri var. crebra P3 White sand, lateritic soil. July Recorded Banksia kippistiana var. P3 Lateritic gravelly soils. October to Likely paenepeccata November Banksia nobilis subsp. P3 Lateritic rises. July to September Likely fragrans Banksia splendida subsp. P3 Lateritic gravel. July to August Likely macrocarpa Beaufortia bicolor P3 White sand over laterite. Sandplains. November to Likely December Conospermum scaposum P3 White-grey sand, sandy clay. Low swampy areas, road January to Likely verges. February Daviesia pteroclada P3 Sandy or clay gravelly soils over laterite. Hills. July to August Likely Drosera prophylla P3 Laterite-silica sand soils. Hilltops. June to July Recorded Grevillea florida P3 Sand, sandy clay, gravel, laterite. Sandplain, slopes, road July to September Likely verges. Grevillea thyrsoides P3 Sand or sandy lateritic gravel. February or Likely subsp. thyrsoides August to September Grevillea uniformis P3 Sand or sandy loam on sandstone, lateritic gravel. July or September Likely Sandstone outcrops, creek lines. to November Hakea longiflora P3 White sand, loam, gravel, laterite. Breakaways. June to Likely September Hemiandra sp. Eneabba P3 Sand. Disturbed sites. February Recorded (H. Demarz 3687) (H. Demarz 3687) Hensmania stoniella P3 White, grey or lateritic sand, often winter-wet. September to Likely November Hypocalymma gardneri P3 Grey-brown sand, laterite. Sandplains, upper slopes, August to Likely heathland. September Jacksonia anthoclada P3 White or grey sand. Sandplains. April Recorded Lepidobolus quadratus P3 Lateritic gravel, grey/white sand. Dry kwongan. August to Likely September Leucopogon sp. Bifid P3 White, grey or yellow sand, gravel, laterite. Hills, middle April to May or Likely Eneabba (M. Hislop 1927) slopes of valleys, disturbed ground. Oct or Dec Mesomelaena stygia P3 White, grey or lateritic sand, clay, gravel. March to October Likely subsp. deflexa Persoonia rudis P3 White, grey or yellow sand, often over laterite. Sept to Dec or Jan Likely Persoonia filiformis P3 White sand over laterite Sept to Dec or Jan Recorded Petrophile biternata P3 Yellow/grey sand & gravel, laterite, quartzite soils. Lateritic August to October Likely ridges, plains. Petrophile septemfida P3 Well drained sand. July to September Likely Phlebocarya pilosissima P3 White or grey sand, lateritic gravel. August to October Recorded subsp. pilosissima Stylidium P3 Lateritic breakaway August to October Recorded drummondianum Stylidium maritimum P3 Sand over limestone. Dune slopes and flats. Coastal heath September to Likely and shrubland, open Banksia woodland. November Stylidium nonscandens P3 Sand over laterite. Hillslopes and crests. Banksia woodland, September to Likely heath, mallee shrubland. November Synaphea aephynsa P3 Gravelly laterite, sand over laterite. July to October Likely

Likelihood Conservation Taxon Habitat Flowering period of Status occurrence Synaphea endothrix P3 Gravelly loam, sand. Lateritic rises. August to Likely September Verticordia fragrans P3 White, grey or yellow sand, clay loam. Low-lying areas, September to Likely sandplains. November Verticordia insignis subsp. P3 Sandy soils over laterite. Sandplains, rocky rises. August to Likely eomagis November Verticordia rutilastra P3 Sand & lateritic gravel. Hills. September to Likely November Banksia chamaephyton P4 Grey or white sand over laterite. October to Likely December Banksia sclerophylla P4 White or grey sand over laterite, gravel. September to Likely October Calytrix chrysantha P4 White, grey or yellow/brown sand. Flats. December or Recorded January to February Calytrix eneabbensis P4 White, grey or yellow sand over laterite. Sandplains. July to October Recorded Calytrix superba P4 Sand over laterite. Flats. December or Likely January to February Chordifex chaunocoleus P4 Grey, siliceous or peaty sand, well to poorly drained. September Likely Drainage lines, depressions. Conostephium magnum P4 White-grey sands or laterite gravels. Sand dunes, July to September Likely swampland, drainage channels, open woodland. Desmocladus elongatus P4 White or grey sand. Dry kwongan. August to Likely December Eucalyptus macrocarpa P4 White or grey sand over laterite. Hillslopes, ridges, Aug to Sept or Likely subsp. elachantha sandplains. Nov to Dec Eucalyptus pendens P4 White or grey sand with lateritic gravel. Hillsides, August to Likely breakaways, sandplains. November Grevillea olivacea P4 White or grey sand. Coastal dunes, limestone rocks. June to Unlikely September Grevillea rudis P4 White, grey, yellow or red sand, often with gravel & over Jan, Apr, June to Recorded laterite. Sept or Nov to Dec Hakea neurophylla P4 Lateritic sandy soils. Hillsides. August Likely Hibbertia propinqua P4 Gravelly loam, lateritic gravel. August to Likely September Hypolaena robusta P4 White sand. Sandplains. September to Likely October Liparophyllum P4 Drainage lines, wet sand. September to Unlikely congestiflorum October Schoenus griffinianus P4 White sand. September to Likely October Stylidium inversiflorum P4 White or grey sand over laterite. Sandplains, hillslopes and September to Likely gullies. Heath, open woodland. November Thysanotus glaucus P4 White, grey or yellow sand, sandy gravel. Oct to Dec or Jan Likely to March Verticordia aurea P4 Deep sand. Sandplains. September to Likely December Xanthosia tomentosa P4 Lateritic gravelly soils. September to Likely December

Appendix D Native vascular plant taxa recorded within the survey area Family Taxon Conservation Status Amaranthaceae Ptilotus polystachyus Asparagaceae Lomandra hastilis Asparagaceae Lomandra sp. Asteraceae Pithocarpa pulchella Asteraceae Podotheca gnaphalioides Boraginaceae Halgania sp. Byblidaceae Byblis lamellata Casuarinaceae Allocasuarina acuaria Casuarinaceae Allocasuarina campestris Casuarinaceae Allocasuarina humilis Casuarinaceae Allocasuarina microstachya Casuarinaceae Allocasuarina ramosissima P3 Casuarinaceae Allocasuarina thuyoides Celastraceae Stackhousia sp. Celastraceae Tripterococcus brunonis Chenopodiaceae Atriplex sp. Colchicaceae Burchardia congesta Cupressaceae Callitris acuminata Cupressaceae Callitris arenaria Cyperaceae Caustis dioica Cyperaceae Cyathochaeta sp. Cyperaceae Lepidosperma ?squamatum Cyperaceae Lepidosperma apricola Cyperaceae Lepidosperma costale Cyperaceae Mesomelaena pseudostygia Cyperaceae Mesomelaena stygia subsp. stygia Cyperaceae Mesomelaena tetragona Cyperaceae Schoenus curvifolius Cyperaceae Schoenus pedicellatus Cyperaceae Schoenus subfascicularis Dasypogonaceae Calectasia narragara Dasypogonaceae Dasypogon obliquifolius Dilleniaceae Hibbertia acerosa Dilleniaceae Hibbertia hypericoides subsp. septentrionalis Dilleniaceae Hibbertia leucocrossa Dilleniaceae Hibbertia sericosepala Dilleniaceae Hibbertia spicata subsp. spicata Dilleniaceae Hypocalymma xanthopetalum Ecdeiocoleaceae Ecdeiocolea monostachya Ericaceae Andersonia heterophylla Ericaceae Astroloma sp. Ericaceae Leucopogon ?conostephioides sens. lat. (indet.) Ericaceae Leucopogon simulans Ericaceae Lysinema pentapetalum Fabaceae Acacia alata var. tetrantha Fabaceae Acacia barbinervis Fabaceae Acacia blakelyi Fabaceae Acacia fagonioides Fabaceae Acacia lasiocarpa Fabaceae Acacia pulchella Fabaceae Acacia saligna Fabaceae Acacia sessilis Fabaceae Acacia stenoptera Fabaceae Bossiaea eriocarpa Fabaceae Daviesia angulata

Family Taxon Conservation Status Fabaceae Daviesia epiphyllum Fabaceae Daviesia nudiflora subsp. nudiflora Fabaceae Daviesia podophylla Fabaceae Gastrolobium ?plicatum Fabaceae Gastrolobium polystachyum Fabaceae Gastrolobium spinosum Fabaceae Gompholobium confertum Fabaceae Gompholobium pungens Fabaceae Gompholobium tomentosum Fabaceae Jacksonia ?ramulosa Fabaceae Jacksonia ?sternbergiana Fabaceae Jacksonia anthoclada P3 Fabaceae Jacksonia floribunda Fabaceae Jacksonia lehmannii Fabaceae Jacksonia nutans Fabaceae Jacksonia ramulosa Gentianaceae Schenkia australis Goodeniaceae Lechenaultia hirsuta Goodeniaceae Verreauxia reinwardtii Blancoa canescens Haemodoraceae Conostylis ?aurea Haemodoraceae Conostylis androstemma Haemodoraceae Conostylis aurea Haemodoraceae Conostylis sp. Haemodoraceae Conostylis tomentosa Haemodoraceae Haemodoraceae Phlebocarya pilosissima subsp. pilosissima P3 Haloragaceae Gonocarpus pithyoides Hemerocallidaceae Arnocrinum preissii Iridaceae Patersonia occidentalis Lamiaceae Hemiandra aff. sp. Jurien (B.J. Conn & M.E. Tozer BJC 3885) Lamiaceae Hemiandra aff. sp. Eneabba (H. Demarz 3687) Other Lamiaceae Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) Other Lamiaceae Hemiandra pungens Lamiaceae Hemiandra sp. Eneabba (H. Demarz 3687) P3 Lamiaceae Microcorys sp. Coomallo (L. Haegi 2677) Lamiaceae Quoya verbascina Malvaceae Lasiopetalum drummondii Myrtaceae ?Scholtzia sp. (indet.) Myrtaceae Babingtonia erecta Myrtaceae Beaufortia bracteosa Myrtaceae Beaufortia elegans Myrtaceae Calothamnus longissimus Myrtaceae Calothamnus quadrifidus Myrtaceae Calothamnus sanguineus Myrtaceae Calytrix chrysantha P4 Myrtaceae Calytrix drummondii Myrtaceae Calytrix eneabbensis P4 Myrtaceae Calytrix flavescens Myrtaceae Calytrix fraseri Myrtaceae Calytrix sapphirina Myrtaceae Darwinia speciosa Myrtaceae Eremaea acutifolia P4 Myrtaceae Eremaea beaufortioides var. microphylla Myrtaceae Eremaea violacea Myrtaceae Eucalyptus ?rigidula Myrtaceae Eucalyptus accedens

Family Taxon Conservation Status Myrtaceae Eucalyptus conveniens Myrtaceae Eucalyptus drummondii Myrtaceae Eucalyptus gittinsii subsp. illucida Myrtaceae Eucalyptus macrocarpa subsp. macrocarpa Myrtaceae Eucalyptus rudis subsp. rudis Myrtaceae Eucalyptus todtiana Myrtaceae Eucalyptus drummondii Myrtaceae Leptospermum oligandrum Myrtaceae Leptospermum spinescens Myrtaceae Melaleuca ?trichophylla (white tomentose leaves) Myrtaceae Melaleuca leuropoma Myrtaceae Melaleuca rhaphiophylla Myrtaceae Melaleuca trichophylla Myrtaceae Melaleuca uncinata Myrtaceae Melaleuca viminea Myrtaceae Pileanthus filifolius Myrtaceae Scholtzia ?laxiflora Myrtaceae Scholtzia laxiflora Myrtaceae Scholtzia sp. Myrtaceae Verticordia aurea P4 Myrtaceae Verticordia densiflora var. cespitosa Myrtaceae Verticordia densiflora var. densiflora Myrtaceae Verticordia drummondii Myrtaceae Verticordia eriocephala Myrtaceae Verticordia fragrans P3 Myrtaceae Verticordia grandis Myrtaceae Verticordia laciniata Myrtaceae Verticordia luteola var. rosea P1 Myrtaceae Verticordia ovalifolia Myrtaceae Verticordia pennigera Myrtaceae Verticordia pholidophylla Olacaceae Olax scalariformis Pittosporaceae Billardiera ?venusta Poaceae Amphipogon turbinatus Poaceae Neurachne alopecuroidea Polygalaceae Comesperma acerosum cygnorum Proteaceae Banksia ?micrantha Proteaceae Banksia ?sphaerocarpa Proteaceae Banksia attenuata Proteaceae subsp. multifida Proteaceae Banksia candolleana Proteaceae Banksia carlinoides Proteaceae Banksia chamaephyton P4 Proteaceae Proteaceae Banksia dallanneyi var. dallanneyi Proteaceae Banksia fraseri var. crebra P3 Proteaceae Banksia glaucifolia Proteaceae Banksia grossa Proteaceae Banksia incana Proteaceae Banksia kippistiana var. kippistiana Proteaceae Banksia lanata Proteaceae Banksia leptophylla Proteaceae Proteaceae Banksia sclerophylla Proteaceae Banksia shuttleworthiana Proteaceae Banksia tortifolia

Family Taxon Conservation Status Proteaceae Banksia tridentata Proteaceae Conospermum canaliculatum Proteaceae Conospermum crassinervium Proteaceae Conospermum nervosum Proteaceae Proteaceae subsp. pachyphylla Proteaceae Hakea ?lissocarpha Proteaceae Hakea auriculata Proteaceae Proteaceae Proteaceae Hakea flabellifolia Proteaceae Proteaceae Proteaceae Hakea psilorrhyncha Proteaceae Proteaceae Hakea smilacifolia Proteaceae Proteaceae Proteaceae Proteaceae Persoonia ?angustiflora Proteaceae Persoonia comata Proteaceae Persoonia filiformis P2 Proteaceae Persoonia rudis P3 Proteaceae Petrophile ?macrostachya Proteaceae Petrophile brevifolia Proteaceae Petrophile chrysantha Proteaceae Proteaceae Petrophile scabriuscula Proteaceae Proteaceae Synaphea aephynsa Proteaceae Restionaceae ?Chordifex stenandrus Restionaceae Alexgeorgea nitens Restionaceae Alexgeorgea subterranea Restionaceae Desmocladus parthenicus Restionaceae Desmocladus virgatus Restionaceae Lyginia barbata Restionaceae Lyginia imberbis Rutaceae Diplolaena eneabbensis Santalaceae Leptomeria empetriformis Stylidiaceae Stylidium ?hymenocraspedum (indet.) P3 Stylidiaceae Stylidium repens Xanthorrhoeaceae Xanthorrhoea sp.

Appendix E Location of Priority Listed Flora species recorded during reconnaissance and targeted surveys.

Taxa Cons Cat Area of population (m2) Abundance Latitude Longitude Allocasuarina ramosissima P3 100 15 -30.0318 115.3964607 Allocasuarina ramosissima P3 100 10 -30.0317 115.3964817 Allocasuarina ramosissima P3 100 2 -30.031 115.3972444 Allocasuarina ramosissima P3 100 6 -30.031 115.3970637 Allocasuarina ramosissima P3 100 5 -30.031 115.3969073 Allocasuarina ramosissima P3 100 4 -30.031 115.3966914 Allocasuarina ramosissima P3 100 5 -30.031 115.3962259 Allocasuarina ramosissima P3 100 5 -29.8677 115.3782568 Allocasuarina ramosissima P3 100 1 -29.8677 115.3782539 Allocasuarina ramosissima P3 100 6 -29.8678 115.3782354 Allocasuarina ramosissima P3 100 1 -29.868 115.3782394 Allocasuarina ramosissima P3 100 5 -29.8682 115.3782354 Allocasuarina ramosissima P3 100 4 -29.8682 115.3782258 Allocasuarina ramosissima P3 100 40 -30.0348 115.3819196 Allocasuarina ramosissima P3 100 4 -29.8979 115.3855036 Allocasuarina ramosissima P3 100 20 -29.8976 115.3854906 Allocasuarina ramosissima P3 100 20 -29.8953 115.3854741 Allocasuarina ramosissima P3 100 10 -29.8829 115.3855101 Allocasuarina ramosissima P3 100 20 -29.8827 115.385492 Allocasuarina ramosissima P3 100 5 -29.8799 115.3854935 Allocasuarina ramosissima P3 100 20 -29.8792 115.3854832 Allocasuarina ramosissima P3 100 40 -29.8768 115.3854903 Allocasuarina ramosissima P3 100 50 -29.8657 115.3854887 Allocasuarina ramosissima P3 100 40 -29.8661 115.3854899 Allocasuarina ramosissima P3 100 30 -29.9262 115.3601105 Allocasuarina ramosissima P3 100 10 -29.9102 115.3637619 Allocasuarina ramosissima P3 100 10 -29.9149 115.3637521 Allocasuarina ramosissima P3 100 10 -29.9152 115.3637711 Allocasuarina ramosissima P3 100 20 -29.9158 115.3637663 Allocasuarina ramosissima P3 100 1 -30.0317 115.3964656 Allocasuarina ramosissima P3 100 5 -30.0311 115.3972548 Allocasuarina ramosissima P3 100 4 -30.0311 115.3970483 Allocasuarina ramosissima P3 100 4 -30.0311 115.3969295 Allocasuarina ramosissima P3 100 10 -30.0311 115.396726 Allocasuarina ramosissima P3 100 6 -30.0311 115.3965966 Allocasuarina ramosissima P3 100 2 -29.8809 115.3600976 Allocasuarina ramosissima P3 100 12 -29.8697 115.3601413 Allocasuarina ramosissima P3 100 12 -29.8695 115.3601641 Allocasuarina ramosissima P3 100 3 -29.8886 115.3673557 Arnocrinum gracillimum P2 100 1 -29.9658 115.3710251 Arnocrinum gracillimum P2 100 1 -29.9636 115.371015 Banksia chamaephyton P4 100 1 -30.0455 115.3965076 Banksia chamaephyton P4 100 1 -30.031 115.3775618 Banksia chamaephyton P4 100 2 -30.031 115.3775244 Banksia chamaephyton P4 100 3 -30.031 115.3750473 Banksia chamaephyton P4 100 4 -30.031 115.3749414 Banksia chamaephyton P4 100 1 -29.9285 115.3565126 Banksia chamaephyton P4 100 3 -29.9287 115.3565127 Banksia chamaephyton P4 100 4 -29.9307 115.3565213 Banksia chamaephyton P4 100 5 -29.9308 115.3565083 Banksia chamaephyton P4 100 8 -29.9313 115.3565214 Banksia chamaephyton P4 100 1 -29.9358 115.3564956 Banksia chamaephyton P4 100 2 -29.9363 115.356517 Banksia chamaephyton P4 100 1 -29.9363 115.3565008 Banksia chamaephyton P4 100 1 -29.9365 115.3565218

Taxa Cons Cat Area of population (m2) Abundance Latitude Longitude Banksia chamaephyton P4 100 2 -29.9681 115.3746697 Banksia chamaephyton P4 100 2 -29.9682 115.37467 Banksia chamaephyton P4 100 1 -29.9683 115.374654 Banksia chamaephyton P4 100 2 -29.9684 115.3746565 Banksia chamaephyton P4 100 2 -29.9684 115.3746577 Banksia chamaephyton P4 100 2 -29.9748 115.3710349 Banksia chamaephyton P4 100 2 -29.972 115.3710109 Banksia chamaephyton P4 100 4 -29.9331 115.3601467 Banksia chamaephyton P4 100 4 -29.933 115.360121 Banksia chamaephyton P4 100 3 -29.9323 115.3601374 Banksia chamaephyton P4 100 2 -29.9322 115.3601638 Banksia chamaephyton P4 100 2 -29.9319 115.3601166 Banksia chamaephyton P4 100 2 -29.931 115.3600976 Banksia chamaephyton P4 100 1 -29.9309 115.3601869 Banksia chamaephyton P4 100 2 -29.9308 115.3601526 Banksia chamaephyton P4 100 1 -29.9295 115.3601201 Banksia chamaephyton P4 100 2 -29.929 115.3601604 Banksia chamaephyton P4 100 3 -29.922 115.3637481 Banksia chamaephyton P4 100 1 -29.9303 115.3637814 Banksia chamaephyton P4 100 1 -29.931 115.3637802 Banksia chamaephyton P4 100 1 -29.9315 115.3637706 Banksia chamaephyton P4 100 1 -29.9316 115.3637854 Banksia chamaephyton P4 100 2 -29.9391 115.3782823 Banksia chamaephyton P4 100 1 -30.0456 115.3964678 Banksia chamaephyton P4 100 2 -30.0311 115.3748847 Banksia chamaephyton P4 100 1 -29.9364 115.3456131 Banksia chamaephyton P4 100 3 -29.9364 115.3456061 Banksia chamaephyton P4 100 2 -29.9362 115.3456601 Banksia chamaephyton P4 100 1 -29.9362 115.3456612 Banksia chamaephyton P4 100 2 -29.9362 115.3456642 Banksia chamaephyton P4 100 2 -29.9362 115.3456322 Banksia chamaephyton P4 100 2 -29.9359 115.3456319 Banksia chamaephyton P4 100 2 -29.9358 115.3456046 Banksia chamaephyton P4 100 1 -29.9357 115.3456121 Banksia chamaephyton P4 100 1 -29.9357 115.34559 Banksia chamaephyton P4 100 1 -29.9357 115.3456541 Banksia chamaephyton P4 100 1 -29.9358 115.3456551 Banksia chamaephyton P4 100 1 -29.9351 115.3456285 Banksia chamaephyton P4 100 3 -29.9697 115.3673778 Banksia chamaephyton P4 100 4 -30.0278 115.3710717 Banksia chamaephyton P4 100 2 -30.0334 115.3710409 Banksia chamaephyton P4 100 2 -29.9453 115.3818951 Banksia chamaephyton P4 100 1 115.3569 -29.9286667 Banksia chamaephyton P4 100 2 115.3568 -29.9320186 Banksia chamaephyton P4 100 1 115.3568 -29.9349127 Banksia chamaephyton P4 100 3 115.3883 -29.8404626 Banksia chamaephyton P4 100 5 115.3882 -29.8447497 Banksia chamaephyton P4 100 3 115.3593 -29.9333299 Banksia chamaephyton P4 200 8 115.3593 -29.9327043 Banksia chamaephyton P4 100 6 115.3593 -29.9309846 Banksia chamaephyton P4 100 1 115.3594 -29.9303057 Banksia chamaephyton P4 100 9 115.3594 -29.9292464 Banksia chamaephyton P4 25 10 115.3633 -29.8433587 Banksia fraseri var crebra P4 100 1 115.368 -29.8553707 Banksia fraseri var crebra P4 100 3 115.3784 -29.8295533 Banksia fraseri var crebra P4 100 1 115.3754 -29.8621762 Banksia fraseri var crebra P4 108 1 115.375 -29.8818177 Banksia fraseri var crebra P4 100 1 115.374 -29.8889433 Banksia fraseri var crebra P4 100 3 115.3776 -29.8749591

Taxa Cons Cat Area of population (m2) Abundance Latitude Longitude Banksia fraseri var crebra P4 100 1 115.3783 -29.8305299 Banksia fraseri var crebra P4 100 4 115.3811 -29.8274313 Banksia fraseri var crebra P4 12 4 115.359 -29.8720118 Banksia fraseri var crebra P4 12 4 115.3589 -29.8625751 Banksia fraseri var crebra P4 4 3 115.359 -29.8617859 Banksia fraseri var crebra P4 10 1 115.3538 -29.8585885 Banksia fraseri var crebra P4 100 1 115.3537 -29.8680082 Banksia fraseri var crebra P4 9 4 115.3534 -29.8742644 Banksia fraseri var crebra P4 16 4 115.3533 -29.8900206 Banksia fraseri var crebra P4 10 1 115.3591 -29.8804763 Banksia fraseri var crebra P4 12 6 115.359 -29.879158 Banksia fraseri var crebra P4 100 1 115.3589 -29.8784307 Banksia fraseri var crebra P4 9 2 115.3702 -29.8658457 Banksia fraseri var crebra P4 10 1 115.3702 -29.8678824 Banksia fraseri var crebra P4 10 1 115.3702 -29.8682253 Banksia fraseri var crebra P4 10 1 115.37 -29.8762725 Banksia fraseri var crebra P4 10 1 115.3726 -29.8794343 Banksia fraseri var crebra P4 16 4 115.3633 -29.8374867 Banksia fraseri var crebra P4 10 1 115.3666 -29.818079 Banksia fraseri var crebra P4 9 3 115.3662 -29.8177203 Banksia fraseri var crebra P4 10 1 115.3589 -29.853858 Banksia fraseri var crebra P4 10 1 115.363 -29.8528925 Banksia fraseri var crebra P4 25 5 115.3685 -29.8528807 Banksia fraseri var crebra P4 16 5 115.3704 -29.850996 Banksia fraseri var crebra P4 25 4 115.3704 -29.8504448 Banksia fraseri var crebra P4 12 3 115.3705 -29.8438015 Banksia fraseri var crebra P4 10 1 115.3849 -29.8764373 Banksia fraseri var crebra P4 9 4 115.3849 -29.8852179 Banksia fraseri var crebra P4 25 8 115.3848 -29.8969016 Banksia fraseri var crebra P4 100 2 115.3603 -29.8685231 Banksia fraseri var crebra P4 100 2 115.3603 -29.8738899 Banksia fraseri var crebra P4 100 6 115.3602 -29.8791835 Banksia fraseri var crebra P4 100 2 115.3601 -29.8804906 Banksia fraseri var crebra P4 100 3 115.3626 -29.8809592 Banksia fraseri var crebra P4 100 5 115.3626 -29.8768957 Banksia fraseri var crebra P4 100 1 115.3626 -29.8752895 Banksia fraseri var crebra P4 100 1 115.3628 -29.8663526 Banksia fraseri var crebra P4 100 1 115.3629 -29.856271 Banksia fraseri var crebra P4 200 8 115.38 -29.8745246 Banksia fraseri var crebra P4 200 15 115.3798 -29.8894971 Banksia fraseri var crebra P4 100 1 115.3797 -29.8922062 Banksia fraseri var crebra P4 1000 2 115.3823 -29.8965289 Banksia fraseri var crebra P4 300 18 115.3829 -29.8554309 Banksia fraseri var crebra P4 200 9 115.3732 -29.84212 Banksia fraseri var crebra P4 100 1 115.3802 -29.8696658 Banksia fraseri var. crebra P3 100 10 -29.8952 115.3854757 Beaufortia bicolor P3 100 2 -30.0463 115.3673965 Beaufortia bicolor P3 100 1 -30.043 115.3673831 Beaufortia bicolor P3 100 40 -30.0409 115.3710298 Beaufortia bicolor P3 100 20 -30.0336 115.3746335 Beaufortia bicolor P3 100 10 -30.0462 115.3782798 Beaufortia bicolor P3 100 40 -30.0435 115.3782748 Beaufortia bicolor P3 100 30 -30.0431 115.3783198 Beaufortia bicolor P3 100 60 -30.0423 115.3782833 Beaufortia bicolor P3 100 70 -30.0414 115.3782757 Beaufortia bicolor P3 100 70 -30.0397 115.3782875 Beaufortia bicolor P3 100 15 -30.0381 115.3782652 Beaufortia bicolor P3 100 7 -30.0357 115.3783139 Beaufortia bicolor P3 100 8 -30.034 115.3783134

Taxa Cons Cat Area of population (m2) Abundance Latitude Longitude Beaufortia bicolor P3 100 10 -30.0322 115.3783243 Beaufortia bicolor P3 100 12 -30.0308 115.3782858 Beaufortia bicolor P3 100 20 -30.0303 115.3782938 Beaufortia bicolor P3 100 30 -30.0283 115.3782686 Beaufortia bicolor P3 100 60 -30.028 115.3782709 Beaufortia bicolor P3 100 80 -30.0369 115.3819212 Beaufortia bicolor P3 100 60 -30.0379 115.3818937 Beaufortia bicolor P3 100 30 -30.0425 115.3819059 Beaufortia bicolor P3 100 1 -30.0454 115.3746921 Beaufortia bicolor P3 100 4 -30.0466 115.3674313 Beaufortia bicolor P3 100 5 -30.0425 115.3674132 Beaufortia bicolor P3 100 6 -30.0362 115.3674304 Beaufortia bicolor P3 100 50 -30.0269 115.3674334 Beaufortia bicolor P3 100 6 -30.0267 115.3710616 Beaufortia bicolor P3 100 15 -30.0272 115.3710608 Calytrix chrysantha P4 100 3 -30.0426 115.3964776 Calytrix chrysantha P4 100 20 -30.0414 115.3964587 Calytrix chrysantha P4 100 1 -30.0409 115.396467 Calytrix chrysantha P4 100 10 -30.0408 115.39648 Calytrix chrysantha P4 100 20 -30.0406 115.3964757 Calytrix chrysantha P4 100 20 -30.0403 115.3965002 Calytrix chrysantha P4 100 25 -30.0403 115.3964586 Calytrix chrysantha P4 100 5 -30.039 115.3964969 Calytrix chrysantha P4 100 3 -30.0389 115.3964981 Calytrix chrysantha P4 100 10 -30.0388 115.3964611 Calytrix chrysantha P4 100 10 -30.0387 115.3964772 Calytrix chrysantha P4 100 10 -30.0386 115.396473 Calytrix chrysantha P4 100 15 -30.0385 115.3964621 Calytrix chrysantha P4 100 20 -30.0383 115.3964962 Calytrix chrysantha P4 100 30 -30.0382 115.3964831 Calytrix chrysantha P4 100 25 -30.0381 115.3964567 Calytrix chrysantha P4 100 50 -30.0379 115.3964956 Calytrix chrysantha P4 100 50 -30.0377 115.3964892 Calytrix chrysantha P4 100 20 -30.0375 115.3964737 Calytrix chrysantha P4 100 25 -30.037 115.3964801 Calytrix chrysantha P4 100 50 -30.0367 115.3964764 Calytrix chrysantha P4 100 20 -30.0365 115.396491 Calytrix chrysantha P4 100 2 -30.0349 115.3964652 Calytrix chrysantha P4 100 5 -30.0346 115.3964973 Calytrix chrysantha P4 100 2 -30.0299 115.3964893 Calytrix chrysantha P4 100 2 -30.0281 115.3964953 Calytrix chrysantha P4 100 1 -30.0271 115.3964968 Calytrix chrysantha P4 100 10 -30.027 115.3963142 Calytrix chrysantha P4 100 2 -30.027 115.396116 Calytrix chrysantha P4 100 3 -30.027 115.3958344 Calytrix chrysantha P4 100 3 -30.027 115.395547 Calytrix chrysantha P4 100 15 -30.027 115.3949899 Calytrix chrysantha P4 100 5 -30.027 115.3947113 Calytrix chrysantha P4 100 5 -30.0291 115.3927943 Calytrix chrysantha P4 100 10 -30.0296 115.3927828 Calytrix chrysantha P4 100 10 -30.0303 115.3928061 Calytrix chrysantha P4 100 2 -30.0343 115.389232 Calytrix chrysantha P4 100 5 -30.0343 115.3892298 Calytrix chrysantha P4 100 5 -30.0342 115.3892401 Calytrix chrysantha P4 100 2 -30.031 115.394207 Calytrix chrysantha P4 100 3 -30.031 115.3938339 Calytrix chrysantha P4 100 5 -30.031 115.3937009 Calytrix chrysantha P4 100 15 -30.031 115.3935527 Calytrix chrysantha P4 100 10 -30.031 115.3924763

Taxa Cons Cat Area of population (m2) Abundance Latitude Longitude Calytrix chrysantha P4 100 2 -30.031 115.3922035 Calytrix chrysantha P4 100 15 -30.0311 115.3921037 Calytrix chrysantha P4 100 10 -30.031 115.3918979 Calytrix chrysantha P4 100 15 -30.031 115.3917899 Calytrix chrysantha P4 100 10 -30.031 115.3915381 Calytrix chrysantha P4 100 5 -30.031 115.3912299 Calytrix chrysantha P4 100 1 -30.0311 115.3897622 Calytrix chrysantha P4 100 1 -30.031 115.3896193 Calytrix chrysantha P4 100 15 -30.0392 115.3737599 Calytrix chrysantha P4 100 25 -30.0392 115.3970576 Calytrix chrysantha P4 100 6 -30.0392 115.3976465 Calytrix chrysantha P4 100 8 -30.0392 115.3979611 Calytrix chrysantha P4 100 1 -29.8547 115.3782146 Calytrix chrysantha P4 100 4 -29.8767 115.3528952 Calytrix chrysantha P4 100 10 -29.8766 115.3528554 Calytrix chrysantha P4 100 5 -29.8734 115.3528919 Calytrix chrysantha P4 100 5 -29.8731 115.3528999 Calytrix chrysantha P4 100 12 -29.873 115.3528852 Calytrix chrysantha P4 100 3 -29.873 115.3529181 Calytrix chrysantha P4 100 9 -29.8729 115.3528862 Calytrix chrysantha P4 100 3 -29.8727 115.3529083 Calytrix chrysantha P4 100 4 -29.8727 115.3528931 Calytrix chrysantha P4 100 3 -29.8724 115.3529114 Calytrix chrysantha P4 100 6 -29.8712 115.352879 Calytrix chrysantha P4 100 4 -29.8703 115.3529015 Calytrix chrysantha P4 100 6 -29.8701 115.3528949 Calytrix chrysantha P4 100 1 -29.8699 115.3528747 Calytrix chrysantha P4 100 2 -29.8696 115.3528723 Calytrix chrysantha P4 100 2 -29.8695 115.3528792 Calytrix chrysantha P4 100 3 -29.8672 115.3565205 Calytrix chrysantha P4 100 5 -29.8686 115.3565185 Calytrix chrysantha P4 100 5 -29.8687 115.3565197 Calytrix chrysantha P4 100 4 -29.869 115.3565002 Calytrix chrysantha P4 100 3 -29.87 115.3565099 Calytrix chrysantha P4 100 15 -29.8702 115.3564977 Calytrix chrysantha P4 100 11 -29.8703 115.356506 Calytrix chrysantha P4 100 4 -29.8707 115.3565055 Calytrix chrysantha P4 100 6 -29.8712 115.3565222 Calytrix chrysantha P4 100 12 -29.8713 115.3565154 Calytrix chrysantha P4 100 8 -29.8716 115.3564827 Calytrix chrysantha P4 100 6 -29.8719 115.3565132 Calytrix chrysantha P4 100 10 -29.872 115.3564816 Calytrix chrysantha P4 100 6 -29.8722 115.3564953 Calytrix chrysantha P4 100 2 -29.8722 115.3565016 Calytrix chrysantha P4 100 3 -29.8727 115.3565124 Calytrix chrysantha P4 100 8 -29.8729 115.3565145 Calytrix chrysantha P4 100 2 -29.8729 115.3564996 Calytrix chrysantha P4 100 2 -29.8734 115.3565164 Calytrix chrysantha P4 100 15 -29.8741 115.3564968 Calytrix chrysantha P4 100 5 -29.8743 115.3565174 Calytrix chrysantha P4 100 9 -29.8744 115.3565078 Calytrix chrysantha P4 100 8 -29.8745 115.3564945 Calytrix chrysantha P4 100 18 -29.8747 115.3565053 Calytrix chrysantha P4 100 16 -29.8748 115.3564992 Calytrix chrysantha P4 100 1 -29.876 115.3564963 Calytrix chrysantha P4 100 6 -29.8791 115.356491 Calytrix chrysantha P4 100 8 -29.8792 115.3565018 Calytrix chrysantha P4 100 3 -29.8796 115.3564931 Calytrix chrysantha P4 100 8 -29.88 115.3564937

Taxa Cons Cat Area of population (m2) Abundance Latitude Longitude Calytrix chrysantha P4 100 12 -29.8803 115.3564825 Calytrix chrysantha P4 100 6 -29.8804 115.356515 Calytrix chrysantha P4 100 2 -29.8805 115.3564977 Calytrix chrysantha P4 100 1 -29.8808 115.3564867 Calytrix chrysantha P4 100 9 -29.8808 115.3564923 Calytrix chrysantha P4 100 8 -29.881 115.3564842 Calytrix chrysantha P4 100 5 -29.8811 115.3564993 Calytrix chrysantha P4 100 11 -29.8813 115.356484 Calytrix chrysantha P4 100 2 -29.8815 115.3564913 Calytrix chrysantha P4 100 5 -29.8825 115.356485 Calytrix chrysantha P4 100 5 -29.8648 115.3746317 Calytrix chrysantha P4 100 3 -29.9127 115.3927719 Calytrix chrysantha P4 100 5 -29.9126 115.3927823 Calytrix chrysantha P4 100 8 -29.9125 115.3927491 Calytrix chrysantha P4 100 7 -29.9122 115.3927554 Calytrix chrysantha P4 100 2 -29.9121 115.3927677 Calytrix chrysantha P4 100 5 -29.912 115.3927635 Calytrix chrysantha P4 100 2 -29.9136 115.3963763 Calytrix chrysantha P4 100 8 -29.9137 115.3963883 Calytrix chrysantha P4 100 5 -29.9143 115.3963986 Calytrix chrysantha P4 100 5 -29.9145 115.3963934 Calytrix chrysantha P4 100 10 -29.9146 115.3963941 Calytrix chrysantha P4 100 5 -29.915 115.3963878 Calytrix chrysantha P4 100 2 -29.9151 115.3963784 Calytrix chrysantha P4 100 15 -29.9152 115.3963852 Calytrix chrysantha P4 100 10 -29.9153 115.3963799 Calytrix chrysantha P4 100 10 -29.9155 115.3964024 Calytrix chrysantha P4 100 5 -29.9156 115.3963931 Calytrix chrysantha P4 100 10 -29.9157 115.3963826 Calytrix chrysantha P4 100 20 -29.916 115.3963699 Calytrix chrysantha P4 100 15 -29.9161 115.3963818 Calytrix chrysantha P4 100 5 -29.9162 115.3963894 Calytrix chrysantha P4 100 50 -29.9204 115.3528951 Calytrix chrysantha P4 100 50 -29.9202 115.3528921 Calytrix chrysantha P4 100 50 -29.9201 115.3528921 Calytrix chrysantha P4 100 10 -29.9191 115.3529115 Calytrix chrysantha P4 100 20 -29.918 115.3528869 Calytrix chrysantha P4 100 30 -29.918 115.3529048 Calytrix chrysantha P4 100 40 -29.9179 115.3529086 Calytrix chrysantha P4 100 50 -29.9178 115.3529016 Calytrix chrysantha P4 100 50 -29.9176 115.3528961 Calytrix chrysantha P4 100 50 -29.9175 115.3528953 Calytrix chrysantha P4 100 50 -29.9174 115.3529138 Calytrix chrysantha P4 100 8 -29.9171 115.3528977 Calytrix chrysantha P4 100 1 -29.9151 115.356532 Calytrix chrysantha P4 100 2 -29.9157 115.3565015 Calytrix chrysantha P4 100 1 -29.9162 115.3564929 Calytrix chrysantha P4 100 3 -29.969 115.3710302 Calytrix chrysantha P4 100 2 -30.03 115.3819466 Calytrix chrysantha P4 100 10 -30.0362 115.3819011 Calytrix chrysantha P4 100 3 -29.8823 115.374636 Calytrix chrysantha P4 100 10 -29.8808 115.3745912 Calytrix chrysantha P4 100 30 -29.8779 115.3746604 Calytrix chrysantha P4 100 50 -29.8771 115.3746363 Calytrix chrysantha P4 100 30 -29.8751 115.3746259 Calytrix chrysantha P4 100 20 -29.8741 115.3746363 Calytrix chrysantha P4 100 60 -29.8732 115.374623 Calytrix chrysantha P4 100 40 -29.8711 115.3782694 Calytrix chrysantha P4 100 40 -29.8797 115.3782571

Taxa Cons Cat Area of population (m2) Abundance Latitude Longitude Calytrix chrysantha P4 100 1 -29.8981 115.385545 Calytrix chrysantha P4 100 10 -29.8964 115.3855366 Calytrix chrysantha P4 100 6 -29.8765 115.3854561 Calytrix chrysantha P4 100 6 -29.8757 115.3855299 Calytrix chrysantha P4 100 30 -29.8753 115.3854952 Calytrix chrysantha P4 100 20 -29.873 115.3854749 Calytrix chrysantha P4 100 15 -29.8632 115.3854793 Calytrix chrysantha P4 100 5 -29.8642 115.3854818 Calytrix chrysantha P4 100 50 -29.8686 115.3818409 Calytrix chrysantha P4 100 10 -29.867 115.3818738 Calytrix chrysantha P4 100 5 -29.9089 115.3601521 Calytrix chrysantha P4 100 30 -29.9053 115.3601341 Calytrix chrysantha P4 100 6 -29.9109 115.3637556 Calytrix chrysantha P4 100 30 -29.9115 115.363751 Calytrix chrysantha P4 100 15 -29.9125 115.3637483 Calytrix chrysantha P4 100 1 -29.9413 115.3746968 Calytrix chrysantha P4 100 3 -29.9378 115.374621 Calytrix chrysantha P4 100 1 -29.9387 115.378258 Calytrix chrysantha P4 100 1 -30.0423 115.396434 Calytrix chrysantha P4 100 1 -30.0422 115.3964181 Calytrix chrysantha P4 100 12 -30.041 115.3964347 Calytrix chrysantha P4 100 10 -30.0407 115.3964304 Calytrix chrysantha P4 100 2 -30.0406 115.3964188 Calytrix chrysantha P4 100 3 -30.0402 115.3964363 Calytrix chrysantha P4 100 3 -30.0394 115.3964559 Calytrix chrysantha P4 100 1 -30.039 115.3964725 Calytrix chrysantha P4 100 3 -30.0389 115.3964409 Calytrix chrysantha P4 100 3 -30.0389 115.3964448 Calytrix chrysantha P4 100 5 -30.0385 115.3964256 Calytrix chrysantha P4 100 10 -30.0382 115.3964275 Calytrix chrysantha P4 100 3 -30.0365 115.3964313 Calytrix chrysantha P4 100 2 -30.0291 115.3964255 Calytrix chrysantha P4 100 2 -30.0282 115.3964255 Calytrix chrysantha P4 100 15 -30.0272 115.396424 Calytrix chrysantha P4 100 10 -30.027 115.396441 Calytrix chrysantha P4 100 4 -30.027 115.3961239 Calytrix chrysantha P4 100 2 -30.027 115.3948862 Calytrix chrysantha P4 100 1 -30.028 115.3928616 Calytrix chrysantha P4 100 6 -30.0286 115.3928273 Calytrix chrysantha P4 100 5 -30.0301 115.3928581 Calytrix chrysantha P4 100 4 -30.0424 115.3928803 Calytrix chrysantha P4 100 3 -30.0429 115.3928734 Calytrix chrysantha P4 100 10 -30.0344 115.3891859 Calytrix chrysantha P4 100 1 -30.0353 115.3855898 Calytrix chrysantha P4 100 1 -30.0311 115.3938258 Calytrix chrysantha P4 100 6 -30.0311 115.3935331 Calytrix chrysantha P4 100 5 -30.0311 115.392708 Calytrix chrysantha P4 100 5 -30.0311 115.3925325 Calytrix chrysantha P4 100 5 -30.0311 115.3924329 Calytrix chrysantha P4 100 7 -30.0311 115.3922461 Calytrix chrysantha P4 100 5 -30.0311 115.3921509 Calytrix chrysantha P4 100 5 -30.0311 115.3919126 Calytrix chrysantha P4 100 4 -30.0311 115.3915198 Calytrix chrysantha P4 100 6 -30.0311 115.3912831 Calytrix chrysantha P4 100 5 -30.0311 115.389931 Calytrix chrysantha P4 100 1 -30.0311 115.38747 Calytrix chrysantha P4 100 10 -30.0392 115.3782384 Calytrix chrysantha P4 100 4 -29.8748 115.3601098 Calytrix chrysantha P4 100 10 -29.8673 115.3637421

Taxa Cons Cat Area of population (m2) Abundance Latitude Longitude Calytrix chrysantha P4 100 10 -29.8726 115.3637607 Calytrix chrysantha P4 100 15 -30.0436 115.3783585 Calytrix chrysantha P4 100 5 -29.8771 115.3673497 Calytrix chrysantha P4 100 7 -29.8803 115.381863 Calytrix chrysantha P4 100 20 -29.8778 115.3818853 Calytrix chrysantha P4 100 5 -29.8763 115.3819089 Calytrix chrysantha P4 100 40 -29.8753 115.3818563 Calytrix chrysantha P4 100 100 -29.8753 115.3818563 Calytrix chrysantha P4 100 25 -29.9047 115.3710107 Calytrix chrysantha P4 100 1 -29.9013 115.3674037 Calytrix chrysantha P4 100 100 -29.902 115.3673787 Calytrix chrysantha P4 100 1 -29.9072 115.3637152 Calytrix chrysantha P4 100 100 -29.9059 115.3637497 Calytrix chrysantha P4 100 50 -29.9027 115.3637454 Calytrix chrysantha P4 100 5 -29.9233 115.3674204 Calytrix eneabbensis P4 100 1 -30.0362 115.3819011 Calytrix eneabbensis P4 100 4 -29.894 115.3746596 Calytrix eneabbensis P4 100 5 -29.8741 115.3746363 Calytrix eneabbensis P4 100 6 -29.8832 115.3782721 Calytrix eneabbensis P4 100 20 -29.887 115.3782538 Calytrix eneabbensis P4 100 1 -30.0297 115.3710558 Calytrix eneabbensis P4 100 5 -29.8889 115.3674076 Calytrix eneabbensis P4 100 5 -29.875 115.367413 Calytrix eneabbensis P4 100 4 -29.8729 115.3673892 Calytrix eneabbensis P4 100 5 -29.8719 115.367391 Calytrix eneabbensis P4 100 10 -29.8727 115.3709678 Calytrix eneabbensis P4 100 2 -29.8928 115.3818808 Calytrix eneabbensis P4 100 3 -29.8753 115.3818563 Calytrix eneabbensis P4 100 2 115.3544 -29.8174649 Calytrix eneabbensis P4 100 1 115.3544 -29.8221947 Calytrix eneabbensis P4 100 1 115.357 -29.8164365 Calytrix eneabbensis P4 100 2 115.3588 -29.817446 Calytrix eneabbensis P4 100 3 115.3588 -29.818964 Calytrix eneabbensis P4 100 2 115.3589 -29.8304328 Calytrix eneabbensis P4 100 1 115.3588 -29.8362356 Calytrix eneabbensis P4 100 3 115.3589 -29.8384983 Conostephium ?magnum P4 100 10 -30.0314 115.3892034 Desmocladus ?elongatus P4 100 1 -29.9662 115.3673963 Desmocladus ?elongatus P4 100 1 -29.97 115.3674162 Desmocladus ?elongatus P4 100 1 -29.97 115.367422 Desmocladus ?elongatus P4 100 1 -29.9732 115.3674493 Desmocladus ?elongatus P4 100 8 -29.9733 115.3674025 Desmocladus ?elongatus P4 100 1 -29.9733 115.3673732 Desmocladus elongatus P4 100 2 -29.9752 115.3746532 Desmocladus elongatus P4 100 1 -29.9738 115.3710499 Desmocladus elongatus P4 100 1 -29.9728 115.3710369 Desmocladus elongatus P4 100 2 -29.972 115.3710109 Desmocladus elongatus P4 100 4 -29.9206 115.3456433 Desmocladus elongatus P4 100 2 -29.9115 115.3492778 Desmocladus elongatus P4 100 1 -29.9118 115.3492739 Desmocladus elongatus P4 100 4 -29.9127 115.3492745 Desmocladus elongatus P4 100 3 -29.9162 115.3492841 Desmocladus elongatus P4 100 4 -29.9191 115.349304 Desmocladus elongatus P4 100 1 -29.9197 115.3492763 Desmocladus elongatus P4 100 1 -29.9208 115.3492957 Desmocladus elongatus P4 100 3 -29.9277 115.3492955 Desmocladus elongatus P4 100 1 -29.9353 115.3492904 Grevillea amplexans subsp. adpressa P1 100 1 -29.9408 115.3746506 Grevillea amplexans subsp. adpressa P1 100 3 -29.9404 115.3746965

Taxa Cons Cat Area of population (m2) Abundance Latitude Longitude Hemiandra aff. Eneabba (H. Demarz 3687) other 100 3 -29.8931 115.3528897 Hemiandra aff. Eneabba (H. Demarz 3687) other 100 1 -29.8995 115.3673794 Hemiandra aff. Eneabba (H. Demarz 3687) other 100 1 -29.9 115.367362 Hemiandra aff. Eneabba (H. Demarz 3687) other 100 1 -29.9008 115.3709698 Hemiandra aff. Eneabba (H. Demarz 3687) other 100 1 -29.9013 115.3674037 Hemiandra aff. Eneabba (H. Demarz 3687) other 100 1 -29.9036 115.3673847 Hemiandra aff. Eneabba (H. Demarz 3687) other 100 1 -29.9029 115.3637468 Hemiandra aff. sp. Jurien (B.J. Conn & M.E. other 100 1 -30.0397 115.3928039 Tozer BJC 3885) Hemiandra aff. sp. Jurien (B.J. Conn & M.E. other 100 1 -30.0416 115.389248 Tozer BJC 3885) Hemiandra aff. sp. Jurien (B.J. Conn & M.E. other 100 1 -29.9708 115.3710311 Tozer BJC 3885) Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8817 115.3564985 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 2 -29.8819 115.3565113 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8903 115.3565011 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 2 -29.8908 115.3565144 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 2 -29.8937 115.3565034 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8946 115.3565351 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8954 115.3564974 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9024 115.3528922 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8966 115.3565222 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8668 115.3746493 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 2 -29.9151 115.3528719 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9101 115.3528898 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.91 115.35288 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.909 115.352896 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9099 115.3564679 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9073 115.3565029 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9092 115.3565368 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9099 115.3565036 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9103 115.3565207 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9128 115.3565105 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9132 115.3565057 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 2 -29.9133 115.3565282 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 2 -29.9194 115.3565181 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8963 115.3746406 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8795 115.374647 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8742 115.3782781 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 5 -29.8746 115.3782626 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8754 115.3782556 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8945 115.3854948 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 2 -29.8936 115.3855045 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8883 115.3854949 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8583 115.385513 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8592 115.381863 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9201 115.3601831 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 3 -29.9199 115.3601025 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9166 115.3601528 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9163 115.3601354 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9161 115.3601535 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9159 115.3601204 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 2 -29.9115 115.3601166 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 2 -29.9114 115.3601472 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9108 115.3601647 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9106 115.3601508 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9106 115.360141 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9104 115.36014 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9209 115.3637927

Taxa Cons Cat Area of population (m2) Abundance Latitude Longitude Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8948 115.3601403 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8983 115.363737 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9012 115.3601407 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8949 115.389111 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8948 115.38911 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8913 115.3891076 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8898 115.3891231 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8891 115.389124 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8886 115.3891143 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8883 115.3891186 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8883 115.3890793 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8879 115.3890922 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8865 115.3890938 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8849 115.3890974 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8839 115.3891133 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8836 115.3891007 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8833 115.389086 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8831 115.3890852 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.883 115.3891223 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8816 115.3890891 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8792 115.3891017 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8734 115.3891181 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8733 115.3890741 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9091 115.3456577 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9086 115.3456347 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9208 115.34931 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.921 115.3493109 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9212 115.3492849 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.9225 115.3492926 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8508 115.3854982 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8947 115.3710061 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8752 115.3818504 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8554 115.3890853 Hemiandra aff. sp. Kalbarri (D. Bellairs 1505) other 100 1 -29.8557 115.3891092 Hemiandra sp. Eneabba (H. Demarz 3687) P3 10 1 115.378 -29.857533 Hemiandra sp. Eneabba (H. Demarz 3687) P3 10 1 115.3779 -29.8568171 Hemiandra sp. Eneabba (H. Demarz 3687) P3 10 1 115.3759 -29.8287059 Hemiandra sp. Eneabba (H. Demarz 3687) P3 10 1 115.3732 -29.8401829 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3708 -29.8263284 Hemiandra sp. Eneabba (H. Demarz 3687) P3 10 1 115.3884 -29.8221407 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3805 -29.8536525 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3802 -29.8545952 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 2 115.3803 -29.8612979 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.38 -29.8824116 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3823 -29.8982486 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3826 -29.8754619 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.383 -29.8521314 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3544 -29.8197101 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3544 -29.8242655 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3543 -29.8259675 Hemiandra sp. Eneabba (H. Demarz 3687) P3 200 10 115.3541 -29.8285354 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.354 -29.8336698 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 2 115.354 -29.8346127 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 3 115.354 -29.8364587 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 2 115.354 -29.8388741 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3574 -29.8420453 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3573 -29.8405372 Hemiandra sp. Eneabba (H. Demarz 3687) P3 300 2 115.3574 -29.8394377 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3573 -29.8327744

Taxa Cons Cat Area of population (m2) Abundance Latitude Longitude Hemiandra sp. Eneabba (H. Demarz 3687) P3 200 7 115.3573 -29.8315322 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 4 115.3571 -29.8241994 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.357 -29.8218505 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 2 115.3569 -29.8145003 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3588 -29.815098 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 2 115.3588 -29.826671 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 2 115.3589 -29.8311976 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3588 -29.8405635 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3731 -29.8467783 Hemiandra sp. Eneabba (H. Demarz 3687) P3 200 2 115.3756 -29.8444523 Hemiandra sp. Eneabba (H. Demarz 3687) P3 200 2 115.3757 -29.8419215 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 3 115.3781 -29.8414975 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 5 115.3782 -29.8432112 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3781 -29.8443589 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3781 -29.8461987 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3805 -29.848873 Hemiandra sp. Eneabba (H. Demarz 3687) P3 300 5 115.3806 -29.8454999 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 3 115.3829 -29.8505467 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.383 -29.8513469 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3882 -29.8406411 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3882 -29.8419197 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3597 -29.9106034 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3598 -29.9011591 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3598 -29.898716 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3599 -29.8970832 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3629 -29.8558739 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3704 -29.8555792 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3703 -29.8618291 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3698 -29.8830124 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3724 -29.8892437 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3725 -29.8845494 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.353 -29.9026038 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3609 -29.8375452 Hemiandra sp. Eneabba (H. Demarz 3687) P3 9 3 115.361 -29.8331962 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3635 -29.8236254 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3635 -29.8261178 Hemiandra sp. Eneabba (H. Demarz 3687) P3 1 2 115.3658 -29.8385577 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3659 -29.8378086 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3659 -29.830198 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.366 -29.8279166 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.366 -29.8274831 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.366 -29.8268127 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3661 -29.821952 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3662 -29.8142304 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3539 -29.8466933 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3589 -29.8496422 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.359 -29.8444821 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3608 -29.8461326 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3633 -29.8424241 Hemiandra sp. Eneabba (H. Demarz 3687) P3 4 2 115.3633 -29.843635 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3632 -29.8459638 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3632 -29.8467597 Hemiandra sp. Eneabba (H. Demarz 3687) P3 4 2 115.3631 -29.8514199 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3656 -29.8507428 Hemiandra sp. Eneabba (H. Demarz 3687) P3 6 5 115.3656 -29.8504574 Hemiandra sp. Eneabba (H. Demarz 3687) P3 16 5 115.3657 -29.8446468 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3681 -29.8456825 Hemiandra sp. Eneabba (H. Demarz 3687) P3 25 6 115.3681 -29.8462024 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3681 -29.8484156

Taxa Cons Cat Area of population (m2) Abundance Latitude Longitude Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3681 -29.8513022 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3681 -29.8515709 Hemiandra sp. Eneabba (H. Demarz 3687) P3 4 5 115.3705 -29.8470186 Hemiandra sp. Eneabba (H. Demarz 3687) P3 4 3 115.3706 -29.8455493 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3706 -29.8415122 Hemiandra sp. Eneabba (H. Demarz 3687) P3 2 3 115.3722 -29.9035054 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3747 -29.9028189 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3747 -29.8988458 Hemiandra sp. Eneabba (H. Demarz 3687) P3 2 3 115.3854 -29.8533462 Hemiandra sp. Eneabba (H. Demarz 3687) P3 100 1 115.3831 -29.8421753 Hensmania stoniella P3 100 1 -29.969 115.3674199 Jacksonia anthoclada P3 100 2 -29.8918 115.3529279 Jacksonia anthoclada P3 100 3 -29.9373 115.3528919 Jacksonia anthoclada P3 100 1 -29.9371 115.3528894 Jacksonia anthoclada P3 100 2 -29.9371 115.3529062 Jacksonia anthoclada P3 100 15 -29.9062 115.3565081 Jacksonia anthoclada P3 100 2 -29.9063 115.3565323 Jacksonia anthoclada P3 100 1 -29.9667 115.3710426 Jacksonia anthoclada P3 100 40 -29.9058 115.3601179 Jacksonia anthoclada P3 100 10 -29.9056 115.3601625 Jacksonia anthoclada P3 100 10 -29.9055 115.360155 Jacksonia anthoclada P3 100 4 -29.9754 115.3637553 Jacksonia anthoclada P3 100 1 -29.9754 115.3638039 Jacksonia anthoclada P3 100 1 -29.9752 115.363775 Jacksonia anthoclada P3 100 1 -29.9752 115.3637577 Jacksonia anthoclada P3 100 1 -29.9752 115.3637761 Jacksonia anthoclada P3 100 1 -29.9751 115.3637607 Jacksonia anthoclada P3 100 1 -29.975 115.3637913 Jacksonia anthoclada P3 100 1 -29.975 115.363796 Jacksonia anthoclada P3 100 1 -29.8978 115.3818782 Jacksonia anthoclada P3 100 20 -29.8777 115.3818536 Jacksonia anthoclada P3 100 20 -29.9235 115.3674023 Persoonia filiformis P2 100 1 -29.9042 115.3529041 Persoonia filiformis P2 100 1 -29.9236 115.360165 Persoonia filiformis P2 100 2 -29.937 115.3746817 Persoonia filiformis P2 100 1 -29.8903 115.3637559 Persoonia filiformis P2 100 1 -29.901 115.360142 Persoonia rudis P3 100 1 -29.8843 115.3565153 Persoonia rudis P3 100 1 -29.9109 115.3492653 Phlebocarya pilosissima subsp. pilosissima P3 100 1 -29.9724 115.3746681 Phlebocarya pilosissima subsp. pilosissima P3 100 3 -29.9747 115.3710245 Phlebocarya pilosissima subsp. pilosissima P3 100 1 -30.0355 115.3783076 Phlebocarya pilosissima subsp. pilosissima P3 100 8 -29.8618 115.3818788 Phlebocarya pilosissima subsp. pilosissima P3 100 3 -29.8613 115.3818579 Phlebocarya pilosissima subsp. pilosissima P3 100 1 -29.8608 115.3818695 Phlebocarya pilosissima subsp. pilosissima P3 100 1 -29.8606 115.3818695 Phlebocarya pilosissima subsp. pilosissima P3 100 1 -29.86 115.381849 Phlebocarya pilosissima subsp. pilosissima P3 100 5 -29.8599 115.3818667 Phlebocarya pilosissima subsp. pilosissima P3 100 2 -29.8597 115.3818653 Phlebocarya pilosissima subsp. pilosissima P3 100 3 -29.8596 115.3818587 Phlebocarya pilosissima subsp. pilosissima P3 100 1 -29.9186 115.3601334 Phlebocarya pilosissima subsp. pilosissima P3 100 3 -29.9167 115.3601388 Stylidium ?hymenocraspedum P3 100 2 -30.0311 115.3889305 Stylidium ?hymenocraspedum P3 100 1 -30.0296 115.3891606 Stylidium ?hymenocraspedum P3 100 1 -29.8896 115.3637664 Synaphea ?endothrix P3 100 2 -29.9143 115.3964001 Synaphea ?endothrix P3 100 1 -29.9152 115.3963941 Synaphea ?endothrix P3 100 1 -29.9262 115.3601105 Verticordia aurea P4 100 2 -29.9081 115.3565023

Taxa Cons Cat Area of population (m2) Abundance Latitude Longitude Verticordia aurea P4 100 11 -29.9179 115.356508 Verticordia aurea P4 100 2 -29.9196 115.3492686 Verticordia aurea P4 100 5 -29.9219 115.3493121 Verticordia aurea P4 100 5 -29.8575 115.3891178 Verticordia fragrans P3 100 3 115.3885 -29.8186432 Verticordia insignis subsp. eomagis P3 100 1 -30.0443 115.3964662 Verticordia luteola var. rosea P1 10 2 115.3676 -29.8654563 Verticordia luteola var. rosea P1 10 3 115.3679 -29.866333 Verticordia rutilastra P3 100 1 -30.0449 115.3965022 Verticordia rutilastra P3 100 1 -30.0453 115.396435 Verticordia rutilastra P3 100 1 -30.0269 115.396478

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Reviewer Approved for Issue Rev No. Author Name Name Signature Date A T Sleigh L Taylor L Taylor 14/04/2021