20111124 1328 report ND MDQA - EPA WA | EPA Western Australia · 2021. 1. 4. · Sinosteel Midwest Corporaton Weld Range Haul Road Short Range Endemic Invertebrate Survey November

NOVEMBER 2011

SINOSTEEL MIDWEST CORPORATION

WELD RANGE HAUL ROAD

SHORT RANGE ENDEMIC SURVEY

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SINOSTEEL MIDWEST CORPORATION

WELD RANGE HAUL ROAD

SHORT RANGE ENDEMIC INVERTEBRATE SURVEY

Sinosteel Midwest Corporaton

Weld Range Haul Road

Short Range Endemic Invertebrate Survey

November 2011

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Document Status

Approved for Issue Rev Author Reviewer/s Date

Name Distributed To Date

A L. Quinn

1 N. Dight M. Davis 4/11/11 M. Davis W. Ennor 4/11/11

2 N. Dight M. Davis 22/11/1 M. Davis W. Ennor 24/11/11

ecologia Environment (2011). Reproduction of this report in whole or in part by electronic, mechanical or chemical means including photocopying, recording or by any information storage and retrieval system, in any language, is strictly prohibited without the express approval of Sinosteel Midwest Corporation and/or ecologia Environment.

Restrictions on Use

This report has been prepared specifically for Sinosteel Midwest Corporation. Neither the report nor its contents may be referred to or quoted in any statement, study, report, application, prospectus, loan, or other agreement document, without the express approval of Sinosteel Midwest Corporation and/or ecologia Environment.

ecologia Environment

1025 Wellington Street

WEST PERTH WA 6005

Phone: 08 9322 1944

Fax: 08 9322 1599

Email: [email protected]




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TABLE OF CONTENTS

EXECUTIVE SUMMARY....................................................................................................................VI

1 INTRODUCTION ................................................................................................................ 1

1.1 PROJECT OVERVIEW..................................................................................................................1

1.2 LEGISLATIVE FRAMEWORK .......................................................................................................3

1.3 SURVEY OBJECTIVES..................................................................................................................3

1.4 SHORT RANGE ENDEMIC FAUNA: A REVIEW ............................................................................4

2 BIOPHYSICAL ENVIRONMENT............................................................................................ 9

2.1 CLIMATE ....................................................................................................................................9

2.2 BIOGEOGRAPHY ..................................................................................................................... 10

2.3 VEGETATION .......................................................................................................................... 10

2.4 LAND SYSTEMS....................................................................................................................... 13

3 METHODS ....................................................................................................................... 17

3.1 LITERATURE REVIEW AND DATABASE SEARCHES .................................................................. 17

3.2 SURVEY TIMING ..................................................................................................................... 17

3.3 SITE SELECTION ...................................................................................................................... 17

3.4 SAMPLING METHODS............................................................................................................. 20

3.5 SRE STATUS ............................................................................................................................ 22

3.6 DATA ANALYSIS ...................................................................................................................... 22

4 RESULTS.......................................................................................................................... 23

4.1 DATABASE AND LITERATURE REVIEW.................................................................................... 23

4.2 SURVEY RESULTS .................................................................................................................... 24

4.3 SPECIMENS COLLECTED ......................................................................................................... 29

4.4 SURVEY ADEQUACY................................................................................................................ 35

4.5 SURVEY LIMITATIONS............................................................................................................. 36

5 DISCUSSION.................................................................................................................... 37

6 CONCLUSIONS ................................................................................................................ 41




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7 STUDY TEAM................................................................................................................... 43

8 REFERENCES.................................................................................................................... 45

TABLES

Table 2.1 – Climate Summary of Meekatharra (1950‐2011)....................................................................9

Table 2.2 – Recorded Rainfall at Meektharra Preceeding Survey ............................................................9

Table 2.3 – Vegetation Assoiations of the Project Area........................................................................ 11

Table 2.4 – Land Systems of the Project Area ....................................................................................... 14

Table 3.1 – Refferenced ecologia Invertebrate Surveys........................................................................ 17

Table 3.2 – Summary of Survey Effort................................................................................................... 18

Table 3.3 – Taxonomic Experts used to Identify Potential SRE Taxa Found During the Survey. ........... 21

Table 3.4 – ecologia Staff Involved with Survey.................................................................................... 22

Table 4.1 – DEC Naturemap Database Results of Rare, Threatened, and Conservation significant Invertebrate Species Likely to occur in the Mid West and Wheatbelt ............................. 23

Table 4.2 – Summary of Specimens Collected....................................................................................... 27

Table 4.4 – Mean estimates of total species richness of the SRE assemblage based on 100 randomisations ................................................................................................................. 36

Table 5.1 – Summary of SRE Specimens Collected and Significance of Impact..................................... 39

FIGURES

Figure 1.1 – Location of the Project Area. ................................................................................................2

Figure 2.1 – Western Murchison Subregions and Surrounds (Based On IBRA Version 6.1 Thackway and Cresswell 1995)................................................................................................................. 10

Figure 2.2 – Vegetation Associations of the Project Area ..................................................................... 12

Figure 2.3 – Land Sytems of the Project Area ....................................................................................... 16

Figure 3.1 – Location of Survey Sites..................................................................................................... 19

Figure 3.2 – Example fo Wet Pitfall Traps ............................................................................................. 20

Figure 3.3 – Examples of the Leaf Litter Reducer and Tullgren Funnels ............................................... 21

Figure 4.1 – Abundance Histogram of Collected Species ...................................................................... 25

Figure 4.2 – Species Accumulation Curve.............................................................................................. 35




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APPENDICES

Appendix A Site Descriptions ............................................................................................................... 48

Appendix B Database and Literature Results Table ............................................................................. 64




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ACRONYMS

List all acronyms used in the report here. Format alphabetically as follows:

DEC Department of Environment and Conservation

EPA Environmental Protection Authority

EPBC Environment Protection and Biodiversity Conservation Act 1950

SRE Short Range Endemic

WAM Western Australian Museum

SMC Sinosteel Midwest Corporation




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EXECUTIVE SUMMARY

Sinosteel Midwest Corporation (SMC) is seeking approvals for the developments supporting their proposed Weld Range Mining Operation in the Midwest region of Western Australia. SMC intends to build a haul road approximately 20 km in length as part of the infrastructure developments at Weld Range, which is located approximately 90 km west of Meekatharra. ecologia Environment was commissioned to undertake a baseline survey for Short Range Endemic (SRE) invertebrate fauna within the proposed haul road as part of the environmental approvals process.

This assessment involved a search of the DEC database and, as many SRE species are not formally recognised under Commonwealth and state legislation due to limited knowledge of the species, searches were also undertaken of the Western Australian Museum (WAM) database and previous ecologia surveys nearby. The likelihood of invertebrate records to be considered SREs was determined by WAM taxonomists based on the current knowledge of the distribution and biology of each species.

The survey was completed between February and March 2011 utilising wet pitfall traps, foraging and leaf litter collected as recommended by the EPA’s Guidance Statement No. 20. Twenty nine sites were selected primarily in isolated, island‐like habitats, while other habitat types were included secondarily.

More than 500 specimens were collected during the survey. These individuals represented eight orders, 16 familles and 44 species of invertebrates (Table 4.2). Of these, one species was considered to be a SRE, two were likely SREs, 22 were potential SREs and three were undetermined. Under the precautionary principle, potential and undetermined SREs should be considered as SREs.

The single confirmed SRE species was the snail Pleuroxia ?bethana and two likely SREs isopods Pseudodiploexochus 'sp. 1' and Pseudodiploexochus 'sp. 2'. The 22 potential SRE species included six mygalomorph spiders (from genera Cethegus, Euoplos, Kwonkan and Aname), nine pseudoscorpions (Synphyronus ‘sp. PSE010’ and eight species of Beierolpium), five scorpions (Isometroides sp., Urodacus sp., Urodacus ‘weld range 3’, Urodacus ‘weld range 4’ and Urodacus ‘weld range 5’), one centipede (Family Mecistocephalidae) and one undescribed genus of isopod. Species of undetermined SREs were two pseudoscorpions (genera Austrohorus and Euryolpium) and one snail (genus Succinea).

The main conclusions of the survey were:

• A total of 47 conservation significant species were found during the database searches of the regional area;

• The survey methods were consistent with the EPA Guidance Statement 20 to sample for SRE fauna;

• Species estimators found the survey was sufficient at 67 %, however it is likely that some SRE species inhabiting the survey area have not been collected in the survey;

• A total of 44 species were collected, of which 26 species were considered to represent SRE and/or potential SRE species;

• The known distributions of Aname ‘MYG228’, Aname ‘MYG229’, Kwonkan ‘MYG230’, Austrohorus sp., Euryolpium sp., Isometroides sp., Urodacus sp., Urodacus 'weld range 5', Urodacus 'weld range 4', Urodacus 'weld range 3', Psuedodiploexochus ‘sp. 1’,




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Psuedodiploexochus ‘sp. 2’, Pleuroxia ?bethana, Succinea sp. and the isopod ‘genus nov. sp. nov.’ will be impacted by the Project, however, the impact is expected to be low as the habitat is widespread and it is expected that these species are present outside the Project area;

• The distribution of Cethegus sp., Euoplos sp., Aname sp., Synsphyronus ‘PSE010’, Meicistocephalidae and all Beierolpium species, will be impacted by the Project, however, the impact is expected to be negligible as regional records exists and the species are known outside the Project area; and,

• None of the habitats in which the potential SRE species were located are unique to the proposed impact areas and they extend beyond the limits of the mapped area. Thus, on the scale of impact ranging from high ‐ moderate – low ‐ negligible, the impact from the Project development on the potential SRE species is expected to be low to negligible.




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1 INTRODUCTION

1.1 PROJECT OVERVIEW

Sinosteel Midwest Corporation (SMC) is seeking approvals for the developments supporting their proposed Weld Range Mining Operation in the Midwest region of Western Australia. SMC intends to build a haul road approximately 20 km in length with a total area of approximately 15 km² as part of the infrastructure developments at Weld Range, which is located approximately 90 km west of Meekatharra (Figure 1.1).

!(

!(

!(

Cue

Mt Magnet

Meekatharra

Coordinate SystemName: GDA 1994 MGA Zone 50Projection: Transverse MercatorDatum: GDA 1994

Figure: 1.1Project ID: 1328 Drawn: NDDate: 02/11/2011Location ofthe Project AreaA4

K0 10 20

Kilometres1:1,000,000Absolute Scale -

LegendHaul Road and Infrastructure

Unique Map ID: ND061




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1.2 LEGISLATIVE FRAMEWORK

Federal and State legislation applicable to the conservation of native fauna include, but are not limited to, the Environment Protection and Biodiversity Conservation Act 1999, the Wildlife Conservation Act 1950, and the Environmental Protection Act 1986. Section 4a of the Environmental Protection Act 1986 requires that developments take into account the following principles applicable to native fauna:

• The Precautionary Principle

Where there are threats of serious or irreversible damage, a lack of full scientific certainty should not be used as a reason for postponing measures to prevent environmental degradation.

• The Principles of Intergenerational Equity

The present generation should ensure that the health, diversity and productivity of the environment is maintained or enhanced for the benefit of future generations.

• The Principle of the Conservation of Biological Diversity and Ecological Integrity

Conservation of biological diversity and ecological integrity should be a fundamental consideration.

This document includes background information on the Project, a literature review of the SRE fauna of Midwest subregion; particularly in reference to the habitats and environments of the Project. The conservation significance of fauna in Western Australia is also outlined.

The document was constructed with a view to satisfy the requirements of:

• the EPA Guidance Statement No. 20: Sampling of Short‐range Endemic Invertebrate Fauna for Environmental Impact Assessment in Western Australia (EPA 2009);

• the EPA Guidance Statement No. 56: Terrestrial Fauna Surveys for Environmental Impact Assessment in Western Australia (EPA 2004).

Some better‐known SRE species have been listed as threatened or endangered under State or Commonwealth legislation in the Wildlife Conservation Act 1950 and/or Environment Protection and Biodiversity Conservation Act 1999, but the majority have not. Often the lack of knowledge about these species precludes their consideration for listing as threatened or endangered. Listing under legislation should therefore not be the only conservation consideration in environmental impact assessment.

The State is committed to the principles and objectives for the protection of biodiversity as outlined in The National Strategy for the Conservation of Australia's Biological Diversity (Commonwealth Government 1996). The EPA expects that environmental impact assessment will consider impacts on conservation of SRE species (EPA 2004).

1.3 SURVEY OBJECTIVES

The EPA’s objectives with regards to fauna management are to:

• maintain the abundance, species diversity and geographical distribution of terrestrial invertebrate fauna; and,

• protect Specially Protected (Threatened) fauna, consistent with the provisions of the Wildlife Conservation Act 1950 (WC Act).




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Hence, the primary objective of this study was to provide sufficient information for the EPA to assess the impact of the Project on the invertebrate fauna of the area, thereby informing assessment against these objectives.

Specifically, the objectives were to undertake a survey that satisfies the requirements documented in EPA’s Guidance Statement 20, thus providing:

• a review of background information (including literature and database searches);

• an inventory of invertebrate fauna species occurring in the Project area, incorporating recent published and unpublished records;

• an inventory of species of biological and conservation significance recorded or likely to occur within the Project area and surrounds;

• a description of the characteristics of the invertebrate fauna habitats occurring in the Project area;

• a description of the characteristics of SRE assemblages occurring in the Project area; and,

• a review of regional and biogeographical significance, including the conservation status of species recorded in the Project area.

1.4 SHORT RANGE ENDEMIC FAUNA: A REVIEW

The decline in biodiversity of terrestrial communities has already been observed both nationally and state‐wide (CALM 2004). There is also an increasing shift in environmental protection from species based conservation to biodiversity based conservation (Chessman 1995; Burbidge et al. 2000; McKenzie et al. 2000) and one of the important considerations involved in this is the presence of endemic species.

Endemism refers to the restriction of species to a particular area, whether it is at the continental, national or local level (Allen et al. 2002). This review focuses on epigean SREs, outlining the major paths to Short Range Endemism, the current knowledge of Short Range Endemism in Australia and the conservation significance of such species. It is important to note that the individual taxa and broader groups discussed are not an exhaustive list of all SREs. This is due to the fact that SREs are dominated by invertebrate species, which are historically understudied and in many cases lack formal descriptions. An extensive, reliable taxonomic evaluation of these species has begun only relatively recently and thus the availability of literature relevant to SREs is relatively scarce.

1.4.1 Processes Promoting Short‐Range Endemism

Short‐range endemism is influenced by numerous processes, which generally contribute to the isolation of a species. A number of factors, including the ability and opportunity to disperse, life history, physiology, habitat requirements, habitat availability, biotic and abiotic interactions, and historical conditions, influence not only the distribution of a taxon, but also the tendency for differentiation and speciation (Ponder and Colgan 2002).

Isolated populations of plants and animals tend to differentiate both morphologically and genetically as they are influenced by different selective pressures over time. Additionally, a combination of novel mutations and genetic drift promote the accumulation of genetic differences between isolated populations. Conversely, the maintenance of genetic similarity is promoted by a lack of isolation through migration between the populations, repeated mutation and balancing selection (Wright




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1943). The level of differentiation and speciation between populations is determined by the relative magnitude of these factors, with the extent of migration generally being the strongest determinant. Migration is hindered by the poor dispersal ability of the taxon as well as geographical barriers to impede dispersal. In summary, those taxa that exhibit short‐range endemism are generally characterised by poor dispersal, low growth rates, low fecundity and reliance on habitat types that are discontinuous (Harvey 2002).

The historical connections between habitats are also important in determining species distributions and often explain patterns that are otherwise inexplicable by current conditions. Many SREs are considered to be relictual taxa (remnants of species that have become extinct elsewhere) and are confined to certain habitats, and in some cases, single geographic areas (Main 1996). Relictual taxa include extremely old species that can be traced back to the Gondwanan periods (180‐65 million years ago) and have a very restrictive biology (Harvey 2002).

In Western Australia, relictual taxa generally occur in fragmented populations, from lineages reaching back to historically wetter periods. For example, during the Miocene period (from 25 million to 13 million years ago), the aridification of Australia resulted in the contraction of many areas of moist habitat and the fragmentation of populations of fauna occurring in these areas (Hill 1994). With the onset of progressively dryer and more seasonal climatic conditions since this time, suitable habitats have become increasingly fragmented. Relictual species now generally persist in habitats characterised by permanent moisture and shade, maintained by high rainfall and/or prevalence of fog. This may be induced by topography or coastal proximity, or areas associated with freshwater courses (e.g. swamps or swampy headwaters of river systems), caves or microhabitats associated with southern slopes of hills and ranges, rocky outcrops, deep litter beds or various combinations of these features (Main 1996; Main 1999). As a result, these habitats support only small, spatially isolated populations, which are further restricted by their low dispersal powers typical for all SRE species.

1.4.2 Taxonomic Groups Likely to Support Short‐Range Endemism

1.4.2.1 Arachnids (Phylum: Arthropoda, Sub Class: Arachnida)

Four orders of arachnids can exhibit short‐range endemism: Pseudoscorpiones (false scorpions), Scorpiones (true scorpions), Schizomida (short‐tailed whip spiders) and Araneae (i.e. Infraorder: Mygalomorphae or trap‐door spiders).

Many mygalomorph trap‐door spider species are vulnerable to disturbance and exhibit short‐range endemism due to their limited ability to disperse. These spiders also have extreme longevity and the long‐term persistence of females in a single burrow (Raven 1982). Mygalomorph spiders are largely considered ‘old world’ spiders and, as such, are generally adapted to past climatic regimes making them vulnerable to desiccation in arid environments. They use a variety of behavioural techniques to avoid desiccation, the most obvious of which is their burrow, which may reach up to 70 cm in depth (Main 1982). Mygalomorph groups are thus capable of surviving on the periphery of the great central desert region and minor habitats within the general arid regions of the continent. A few mygalomorph spider species are known from the Midwest region with representatives of the families Nemesiidae and Idiopidae known from nearby locations to the Project area.

Another member of the arachnid class, the Schizomida, is composed entirely of SREs, with most recorded from single localities (Harvey 2002). Forty‐six schizomid species have been described in northern Australia. Most are known to occur in the entrances to and inside caves, while the




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remainder occur in nearby habitats (Harvey 2002). No epigean schizomids are known from the Midwest region.

Scorpions and pseudoscorpions also exhibit high degrees of endemism (Koch 1981; Harvey 1996). Scorpions are popularly thought of as desert animals although they can be found in most of Australia’s climatic zones. Several SRE scorpions and pseudoscorpions are known from the Midwest region including species from the scorpion genera Lychas and Urodacus and the pseudoscorpion species Synsphyronus gracilis.

1.4.2.2 Isopods (subphylum: Crustacea, Class malacostraca)

There are currently around 10,215 described species of isopod classified into 11 suborders: however, little understanding of the taxonomy of Australian genera exists to date (Judd et al.; Brusca and Brusca 2003). Numerous species of terrestrial and subterranean isopods belonging to several different genera have been identified in Western Australia with several genera containing known and potential SREs including Pseudolaureola, Buddelundia, Cubaris and Platyarthridae (Judd 2009, 2010, 2011). SRE isopods have been collected from the Midwest, Pilbara and Kimberley regions of Western Australia (Judd et al. 2008), Judd 2011). Many species have Gondwanan affinities suggesting that relictual habitats originating from much wetter climate periods persist across the State (Main 1987). Due to a lack of taxonomic knowledge and paucity of data, the precise distributions of each species is unknown and more taxonomic work at species level is required before the status of individual populations can be ascertained.

1.4.2.3 Millipedes and Centipedes (Phylum Arthropoda, Class Myriapoda)

Despite millipedes being highly abundant in soil and leaf litter and highly diverse at the order level, they are inadequately studied and relatively little is known of their biogeography (Harvey 2002). SRE millipedes known to occur in the Midwest include species from the genus Antichiropus. All species from this genus are known to be short‐range endemics with the exception of two species Antichiropus variabilis and Antichiropus ‘PM1’, from the jarrah forests and northern Wheatbelt respectively. This genus extends from the Nullarbor Plain to the Pilbara region and has been collected close to the Project area.

Centipedes are not listed by Harvey (2002) as SRE species; however they have been shown to be endemic to small areas on the east coast (Edgecombe et al. 2002). Examination of the distributions of species featured in the CSIRO centipede webpage also reveals disjunct and isolated occurrences of many species. A number of genera have Pangaean and Gondwanan affinities (Edgecombe et al. 2002). In general, these animals have a relatively cryptic biology, preferring moist habitats in deep litter accumulations, under rocks and in rotting logs, and they have relatively poor dispersal abilities (Lewis 1981). This suggests that they are potential candidates for designation as SREs.

1.4.2.4 Molluscs (Phylum: Mollusca)

Numerous species of freshwater and terrestrial molluscs belonging to many genera have been identified in Australia, with most being SREs (Harvey 2002). Restricted ranges of the terrestrial molluscs of the drier northern and Western Australia were noted for a vast number of species (Solem 1997). Among these were seven endemic species of Rhagada from the Dampier Archipelago, five of which were found to occur sympatrically on one island. However, in a recent genetic study conducted on Rhagada (Johnson et al. 2004), allozyme analysis revealed little variation between taxa. Such a finding could indicate that there is merely high morphological diversity within one or a few




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species. It is also possible however, that there is a number of highly endemic species and that morphological diversity has taken place rapidly with little genetic change (Johnson et al. 2004).

Some species of the terrestrial snail genera Pleuroxia are known to be SREs. Species of this genus have been recorded within the Midwest region with some occurring in areas close to the Project area.

1.4.2.5 Worms (Phylum: Annelida & Onychophora)

The taxonomic status of the earthworm family, Megascolecidae, in Western Australia was revised by Jamieson in 1971. As a result of this study, it was concluded that most of the earthworm genera are made up almost entirely of SREs (Harvey 2002). This is also the case with the velvet worms (Onychophorans). Due to several taxonomic revisions that have been conducted (see references within Harvey, 2002a), the number of onychophoran species has expanded from six to over 70 species, and a number of species still remain undescribed (Harvey 2002). Very few of these species exceed ranges of 200 km2 and some are restricted to single localities and have high genetic differentiation, indicating very little mobility and dependence on their permanently moist habitats (Harvey 2002). No terrestrial SRE worms are known from the Midwest region.




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2 BIOPHYSICAL ENVIRONMENT

2.1 CLIMATE

The climate of the Project area is described as semi arid with a bimodal rainfall pattern which peaks in summer and winter. During the survey period (February 2011 – March 2011) a significant amount of rainfall occurred during both months (Table 2.2). The average annual rainfall, as recorded from historical data at Meekatharra Airport, is 236 mm falling over an average of 46 days, (Desmond et al. 2001), however a total of 168.8 mm fell during the 38 days of the survey period. The maximum temperatures peaked in February with a mean maximum temperature 36°C, while the mean maximum temperature for March was 34.3°C. Overnight minima peaked in February with a monthly mean of 23°C, while the mean minimum temperature for March was 21°C.

0

5

10

15

20

25

30

35

40

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

Rain

fall

(mm

)

0

5

10

15

20

25

30

35

40

45

Tem

p (°

)

Mean Rainfall Mean Max Temp Mean Min Temp

Table 2.1 – Climate Summary of Meekatharra (1950‐2011)

Table 2.2 – Recorded Rainfall at Meektharra Preceeding Survey

September 2010

October 2010

November 2010

December 2010

January 2011

February 2011

March 2011

Total Rainfall (mm)

24.6 0.2 5.2 111.4 26 169.6 29.2

Mean Rainfall (mm)

4.8 6.4 11.5 13.6 27.1 37.3 28.2




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2.2 BIOGEOGRAPHY

Weld Range lies in the Murchison Biogeographic Region, western sub region, which lies within the Eremaean Botanical Province of Western Australia (Figure 2.1). Geologically, the Weld Range Land System is located within the Murchison geological province, within the Yilgarn Craton. The System may be described as a series of rugged ranges and ridges of mainly Archaean metamorphosed sedimentary rocks supporting Acacia shrub lands (Curry et al. 1994). The 350 km2 area includes the Weld Range and Jack Hills systems.

Figure 2.1 – Western Murchison Subregions and Surrounds (Based On IBRA Version 6.1 Thackway and Cresswell 1995)

2.3 VEGETATION

The Project area lies within the Eremaean Botanical Province of the Western Australia (Thackway and Cresswell 1995). Six vegetation associations mapped by Shepherd (2001) occur within the survey area (Table 2.3, Figure 2.2). The survey area consists primarily of low woodland with mulga, Acacia aneura and A. ramulosa and shrubland. All vegetation associations are widespread outside of the Project area, less than 1% of all vegetation associations represented within the survey area.




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Table 2.3 – Vegetation Assoiations of the Project Area

Vegetation Association

Vegetation Description Survey Sites Total Area in WA

(km2) Area in Study Area (km2)

Total Vegetation Type Impacted (%)

18 Low woodland; mulga (Acacia aneura) F2, F6, F7, F8, F13, F16, P6,

P7, P8, P9, P10 247512 5.71

P13

P12

P11

P10

P09

P08

P07

P06P05P04P03P02

P01 F9

F8

F7F6

F5

F4

F3

F2

F1

F16

F15

F14

F13

F12 F11

F10

LegendForaging Sites

Wet Pitfall Trapping Sites

Haul Road and Infrastructure

Vegetation Associations18

39

182

202

204

2081

Coordinate SystemName: GDA 1994 MGA Zone 50Projection: Transverse MercatorDatum: GDA 1994 A4

Figure: 2.2 Project ID: 1328 Drawn: NDDate: 02/11/11

K0 2 4

Kilometres1:140,000Absolute Scale -


Vegetation Associations of the Project Area




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2.4 LAND SYSTEMS

Land systems are described using the biophysical characteristics of geology, landforms, vegetation and soils. Curry et al. (1994) undertook a regional inventory of the Murchison River catchment and surrounds to document the land systems present and their vegetation conditions. This inventory covered a total of 88,360 km², spanning from Meekatharra and Mount Magnet in the east, to the Greenough and Wooramel rivers in the west.

The Project area spans eight of these land systems (Table 2.4, Figure 2.3), of which the Kalli Land System represents a majority of the Project area (approximately 60%). The Kalli Land System is described as elevated, gently undulating red sandplains edged by stripped surfaces on laterite and granite; tall acacia shrublands and understorey of wanderrie grasses (and spinifex locally) replaced by more extensive areas of Bullimore land system. However, all land systems are represented by the Project area with less than 1% (Table 2.4).




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Table 2.4 – Land Systems of the Project Area

Land System Description Survey Sites Total Area in WA (km²) Area in the Project Area

(km²)

Total Land System Impacted (%)

Land type 1 ‐ Hills and ranges with acacia shrublands

Weld Land System

Rugged ranges and ridges of banded ironstone and quartzite, supporting acacia shrublands.

F1, F2, F3, F4, P9 372 1.30




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Land System Description Survey Sites Total Area in WA (km²) Area in the Project Area

(km²)

Total Land System Impacted (%)

Land type 36 ‐ Alluvial plains with halophytic shrublands

Mileura Land System

Saline and non‐saline calcreted river plains, with clayey flood plains interrupted by raised calcrete platforms supporting diverse and very variable tall shrublands, mixed halophytic shrublands and shrubby grasslands.

F7 2612 0.09

P13

P12

P11

P10

P09

P08

P07

P06P05P04P03P02

P01 F9

F8

F7F6

F5

F4

F3

F2

F1

F16

F15

F14

F13

F12 F11

F10LegendWet Pitfall Trapping Sites

Foraging Sites


Land Systems Jundee Land System

Kalli Land System

Mileura Land System

Sherwood Land System

Violet Land System

Weld Land System

Yanganoo Land System

Yarrameedie Land System


Figure: 2.3Project ID: 1328 Drawn: NDDate: 02/11/11

K0 2 4



Land Systems of the Project Area




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3 METHODS

3.1 LITERATURE REVIEW AND DATABASE SEARCHES

Ideally, a database search for SRE species would be undertaken of the Project area and surrounding local area. However, as knowledge of invertebrate diversity throughout the Midwest region is very limited, a regional approach was taken. Using the area 100 km from the Project area, taxa (Orders) known to contain SREs were searched within the Arachnid, Mollusc, Crustacean and Myriapod terrestrial invertebrate electronic databases of the Western Australian Museum (WAM). The ecologia database was also consulted for specimens collected from previous surveys within 50 km of the Project area.

Fauna species that have been formally recognised as rare, threatened, or as having high conservation value are protected under Commonwealth and State legislation. A DEC NatureMap database search was undertaken in order to determine if any species listed by EPBC Act or the WC Act have potential to occur in the Project area. In addition, five ecologia publications (Table 3.1) reporting on invertebrate fauna surveys conducted within the Midwest were consulted.

Table 3.1 – Refferenced ecologia Invertebrate Surveys

Survey Distance (km)

Sinosteel Midwest Corp. Ltd Jack Hills SRE Survey (ecologia 2009c) 110

Sinosteel Midwest Corp. Ltd Jack Hills Shield‐back spider Idiosoma nigrum Survey (ecologia 2009b); 110

Sinosteel Midwest Corp. Ltd Weld Range SRE Survey (ecologia 2008) 10

Sinosteel Midwest Corp. Ltd Weld Range Shield‐back spider Idiosoma nigrum Survey (ecologia 2009d) 10

Crosslands Resources, Jack Hills SRE Survey (ecologia 2009a) 110

3.2 SURVEY TIMING

Sufficient rainfall is required for optimal SRE sampling, therefore the optimal time for SRE sampling in the Midwest is November to April (EPA 2009). Fieldwork was completed between February and March 2011 and thus within the recommended period. The Project area received above average rainfall before and during the survey period. Although rainfall events are generally desirable for sampling, the volume of rainfall at the Project area was to the extent that it impaired the survey methodology.

3.3 SITE SELECTION

Survey site locations were selected primarily based on those habitats likely to support SRE invertebrates. Aerial photographs (Google Earth™) and a vegetation map of the Project Area was studied to determine the vegetation communities in which the SREs were likely to occur within the Project Area. Micro habitats likely to maintain higher moisture levels and ‘island’ habitats were targeted. Thirteen wet pitfall trap sites and 16 foraging only sites were selected along the length of the proposed Haul road (Table 3.2, Figure 3.1). These site locations were further refined following on‐site examination.




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Table 3.2 – Summary of Survey Effort

Site Zone East North Foraging (hrs) Leaf litter

Collection (m²) Wet Pitfall Traps

P01 50 564851 7029606 1 3 4

P02 50 566258 7030331 1 3 4

P03 50 567194 7030315 1 3 4

P04 50 569221 7029662 1 3 4

P05 50 571656 7029590 1 3 4

P06 50 573718 7029546 1 3 4

P07 50 570109 7028127 1 3 4

P08 50 575052 7029475 1 3 4

P09 50 579074 7028119 1 3 4

P10 50 569480 7032820 1 3 4

P11 50 569804 7033719 1 3 4

P12 50 575198 7036856 1 3 4

P13 50 574759 7037510 1 3 4

F01 50 581483 7027147 2 3 0

F02 50 579650 7025665 2 3 0

F03 50 579606 7026506 2 3 0

F04 50 577637 7028894 2 3 0

F05 50 553149 7018763 2 3 0

F06 50 555330 7018097 2 3 0

F07 50 557311 7017931 2 3 0

F08 50 561019 7019603 2 3 0

F09 50 568174 7029805 2 3 0

F10 50 562660 7026494 2 3 0

F11 50 571427 7034771 2 3 0

F12 50 569540 7034512 2 3 0

F13 50 562314 7021510 2 3 0

F14 50 562526 7024510 2 3 0

F15 50 563365 7027699 2 3 0

F16 50 571923 7028608 2 3 0

Total 45 87 52

P13

P12

P11

P10

P09

P08

P07

P06P05P04P03P02

P01 F9

F8

F7F6

F5

F4

F3

F2

F1

F16

F15

F14

F13

F12 F11

F10

LegendWet Pitfall Trapping Sites

Foraging Sites



Figure: 3.1 Project ID: 1328 Drawn: NDDate: 02/11/11

K0 2 4



Location of Survey Sites




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3.4 SAMPLING METHODS

The survey methods adopted by ecologia are aligned with the EPA’s Guidance Statement No. 20 (EPA 2009). The survey was undertaken using a variety of sampling techniques, both systematic and opportunistic. Systematic sampling refers to data methodically collected over a fixed time period in a discrete habitat type, using an equal or standardised sampling effort. The resulting information can be analysed statistically, facilitating comparisons between habitats. Opportunistic sampling includes data collected non‐systematically from both fixed sampling sites and as opportunistic records gathered during foraging sessions.

3.4.1 Wet Pitfall Trapping

At 13 sites, four wet pitfall traps (Figure 3.2) consisting of a PVC tube (25cm long) and containing 30% Ethylene Glycol and 5% Formaldehyde were dug into the ground so that the surface was flush with the ground level. A receptacle (containing 700 ml of pitfall trapping solution) and funnel (fitting flush to the inside of the pitfall trap) were deployed into each tube and a cover was fitted 3 cm above the tube with steel fittings to exclude medium sized vertebrates and rain, and to deter attention of larger vertebrates. Traps were left open for 38 days, after which period they were cleared.

Figure 3.2 – Example of Wet Pitfall Traps

3.4.2 Foraging

At least one person hour was spent foraging at all 29 sites. Opportunistic foraging involved physically searching through microhabitats for SRE invertebrates. The underside of rocks and logs were closely investigated for SREs, snail shells and trapdoor spiders were collected and documented where found.

3.4.3 Leaf Litter Collection

At each site, three quadrats (1 m2 each) of leaf litter were collected and placed separately into a leaf‐litter reducer (Figure 3.3). The contents from each collection was placed into a paper bag inside a zip‐lock bag and kept separate. A small amount of wet tissue paper was placed into each sample to keep humid. Samples were then transported back to Perth in a cool, dark container where they were placed on Tullgren funnels to extract specimens




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3.4.4 Laboratory sorting and specimen identification

Tullgren funnels were used to extract litter‐dwelling invertebrates from the collected leaf litter samples (Figure 3.3). The general principle of Tullgren funnels is that a sample of leaf litter is suspended above a vessel containing ethanol. Animals inhabiting the sample are forced downwards by the progressive drying of the sample and ultimately fall into the collecting vessel containing ethanol. Typically, drying is enhanced by placing an incandescent lamp or heat source above the sample.

After the leaf litter samples were processed on the Tullgren funnels, each sample was then examined for dead snail shells, or any other dead animals that were not collected during the Tullgren funnel extraction. Each sample was emptied into a tray and examined using a fluorescent light magnifier. Any dead animals were collected and immediately placed into ethanol. Samples were then sorted under a Stereo microscope into potential SRE groups and sent to the relevant taxonomic expert for further identification. A list of taxonomic specialists used for identification is shown in Table 3.3.

Figure 3.3 – Examples of the Leaf Litter Reducer and Tullgren Funnels

Table 3.3 – Taxonomic Experts used to Identify Potential SRE Taxa Found During the Survey.

Taxonomic Expert Institution Specialist Group

Corey Whisson Western Australian Museum Molluscs

Erich Volschenk Private consultant Scorpions

Mark Harvey Western Australian Museum Arachnids, Myriapods

Mieke Burger Western Australian Museum Arachnids, Myriapods

Shirley Slack‐Smith Western Australian Museum Molluscs

Simon Judd Private consultant Isopods

Volker Framenau Private Consultant Mygalomorph spiders




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3.4.5 Field Team

Field survey team members are listed in Table 3.4.

Table 3.4 – ecologia Staff Involved with Survey

Name Qualification Relevant Experience

Catherine Hall BSc (Hons) 3 years experience with invertebrate zoology

Nicholas Dight BSc 4 years experience with invertebrate surveys

Sean White BSc 3 years experience with invertebrate surveys

3.5 SRE STATUS

The likelihood of the invertebrate species to be considered a SRE or not a SRE was determined by expert taxonomists (Mark Harvey, Department of Terrestrial Invertebrates, WAM; Shirley Slack‐Smith and Corey Whisson, Department of Malacology; Erich Volschenk, Volker Framenau and Simon Judd, private consultants) based on the current knowledge of the distribution and biology of each species, as follows:

• no – not considered a SRE;

• confirmed – current knowledge confirms that this species is a SRE;

• likely – current knowledge suggests this species is probably a SRE, however, further research is required to confirm status;

• potential – current knowledge of this species or group is very limited, however, there is the potential for this species to represent a SRE. Further research is required to confirm status;

• unlikely ‐ current knowledge of this species or group is limited but sufficient to expect the species will have wider ranges; and,

• undetermined.

3.6 DATA ANALYSIS

3.6.1 Survey Adequacy

There are three general methods of estimating species richness from sample data: extrapolating species‐accumulation curves (SAC), fitting parametric models of relative abundance, and using non‐parametric estimators (Bunge and Fitzpatrick 1993; Colwell and Coddington 1994; Gaston 1996). In this report, the level of survey adequacy was estimated using the rarefaction of SACs as computed by Mao Tao estimator. In addition, the following species richness estimators: ACE, ICE, Chao‐1, Jacknife‐1, Jacknife‐2, Bootstrap and their 95% confidence limits were calculated. Finally, a Michaelis‐Menten enzyme kinetic curve was calculated and used as a stopping rule technique. To eliminate features caused by random or periodic temporal variation, the sample order was randomised 100 times. The estimators applied to the data set were performed using EstimateS (version 8, Colwell 2009).




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4 RESULTS

4.1 DATABASE AND LITERATURE REVIEW

The results of the WAM and ecologia database searches are presented in Appendix A. The search identified 29 SRE species considered SRE (two species), potential SRE (23 species) or undetermined (five species). These consisted of 11 mygalomorph spiders, seven pseudoscorpions, four scorpions, one snail, two millipedes, one centipede and four isopods. Ten genera identified from these results were recorded in the Project area.

The results of the DEC NatureMap search are provided in Table 4.1. A total of 19 species are listed by the EPBC Act, WC Act or DEC as being formally recognised as rare, threatened, or as having high conservation value in the Midwest and Wheatbelt regions of Western Australia. These species are protected under Commonwealth and State legislation. These species include four trapdoor spiders (mygalomorphs), one butterfly, two bees, six crickets, two snails and one scorpion fly. None of those listed species were recorded in the Project area.

Table 4.1 – DEC Naturemap Database Results of Rare, Threatened, and Conservation significant Invertebrate Species Likely to occur in the Mid West and Wheatbelt

Species EPBC Act WC Act DEC

Ogyris subterrestris petrina (butterfly) CR S1

Kwonkan eboracum (trapdoor spider) CR S1

Teyl sp. (trapdoor spider) CR S1

Neopasiphe simplicolor (bee) EN S1

Aganippe castellum (trapdoor spider) EN S1

Idiosoma nigrum(Shield‐back Trapdoor spider) VU S1

Psacadonotus seriatus (cricket) P1

Ixalodectes flectocerus (cricket) P1

Bothriembryon perobesus (snail) P1

Bothriembryon bradshawi (snail) P1

Phasmodes jeeba (cricket) P2

Austromerope poultoni (scorpionfly) P2

Austrosaga spinifer (cricket) P3

Hemisaga vepreculae (cricket) P3

Throscodectes xederoides (cricket) P3

Hylaeus globuliferus (bee) P3




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4.2 SURVEY RESULTS

A total of 526 specimens were collected during the survey. These individuals represented eight orders, 14 familles (minus scorpions pending identification) and 37 species of invertebrates (Table 4.2). Of these, one species was considered to be a SRE, two were likely SREs, 22 were potential SREs and three were undetermined. Under the precautionary principle, potential and undetermined SREs should be considered the same as confirmed SREs.

The single confirmed SRE species was the snail Pleuroxia ?bethana and two likely SREs isopods Pseudodiploexochus 'sp. 1' and Pseudodiploexochus 'sp. 2'. The 22 potential SRE species included six mygalomorph spiders (from genera Cethegus, Euoplos, Kwonkan and Aname), nine pseudoscorpions (Synphyronus ‘sp. PSE010’ and eight species of Beierolpium), five scorpions (Isometroides sp., Urodacus sp., Urodacus ‘weld range 3’, Urodacus ‘weld range 4’ and Urodacus ‘weld range 5’), one centipede (Family Mecistocephalidae) and one undescribed genus of isopod. Species of undetermined SREs were two pseudoscorpions (genera Austrohorus and Euryolpium) and one snail (genus Succinea).

The taxonomy, distribution and SRE status of these genera are discussed in the following sections.

As typical in SRE surveys, 25 species were recorded in low abundance, being represented only by singletons (one record each, 20 taxa) and / or doubletons (two records each, 5 taxa) (Figure 4.1). From those, nine species present potential SREs.




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0 50 100 150 200 250 300

Buddelundia 'sp.13'

Synsphyronus `sp. PSE010`

Pseudodiploexochus 'sp. 1'

'indet' `sp. 2 Yeel i rrie`

Beierolpium`sp. (juv. 7/2)`

Indolpium sp.

genus nov. sp. nov.

Beierolpium `sp. 8/4 smal l `

Pupoides paci fi cus

Euryolpium sp.

Nes idiochernes sp.

Austrohorus sp.

Oratemnus sp.

Pupoides bel tianus

Gastrocopta bannertonens is


Beierolpium `sp. 8/3`

Succinea sp.

Scolopendra mors itans

Pupoides eremicolus


Pleuroxia bethana

Kwonkan 'MYG230'

'indet' `sp. 1 Yeel i rrie`

Gaius sp.

Family Synxenidae

Family Mecis tocephal idae

Euoplos sp.

Cethegus sp.

Buddelundia 'sp.10'



Beierolpium `sp. 8/4 l ge`

Beierolpium `sp. 8/2`

Aname sp.

Aname 'MYG229'

Aname 'MYG228'

Figure 4.1 – Abundance Histogram of Collected Species




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Sinosteel Midwest CorporatonWeld Range Haul Road


Table 4.2 ‐ Summary of Specimens Collected Trapping Sites Forage Only SitesClass (Order) Family Taxa SRE P01 P02 P03 P04 P05 P06 P07 P08 P09 P10 P11 P12 P13 F01 F02 F03 F04 F05 F06 F07 F08 F09 F10 F11 F12 F13 F14 F15 F16

Arachnida (Mygalomorphae)

Dipluridae Cethegus sp. potential 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Idiopidae Euoplos sp. potential 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

Gaius sp. no 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Nemesiidae Aname sp. potential 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

Aname 'MYG228' potential 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Aname 'MYG229' potential 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Kwonkan 'MYG230' potential 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

Arachnida (Pseudoscorpiones)

Atemnidae Oratemnus sp. no 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0Chernetidae `sp. 1 Yeelirrie` unlikely 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

`sp. 2 Yeelirrie` unlikely 0 0 0 20 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Nesidiochernes sp. no 0 0 0 3 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

Garypidae Synsphyronus `sp. PSE010` potential 0 0 1 0 5 10 27 6 3 1 3 2 1 0 13 0 0 0 0 0 0 1 0 0 0 0 0 0 0Olpiidae Austrohorus sp. undetermined 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 2 0 0 0 0 0 0 0 0 0 0

Beierolpium `sp. (juv. 3/1)` potential 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Beierolpium `sp. (juv. 6/2)` potential 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Beierolpium `sp. (juv. 7/2)` potential 1 0 1 1 0 0 2 4 0 0 0 1 1 0 1 8 0 0 0 0 0 0 0 0 0 0 0 0 0Beierolpium `sp. (juv. 7/3)` potential 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0Beierolpium `sp. 8/2` potential 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Beierolpium `sp. 8/3` potential 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0Beierolpium `sp. 8/4 lge` potential 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Beierolpium `sp. 8/4 small` potential 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 3 0 0 0 0 0 0 0 0 0 0Euryolpium sp. undetermined 0 1 0 0 0 0 0 2 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Indolpium sp. unlikely 0 1 1 0 0 0 1 0 0 0 1 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

Arachnida (Scorpiones)

Buthidae Isometroides sp. indet. potential 0 0 0 0 0 0 1 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Lychas 'splendens' no 0 0 0 2 0 0 0 0 0 1 0 0 1 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 1

Urodacidae Urodacus sp. indet. potential 0 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Urodacus 'gibson 1' no 0 0 0 0 0 0 0 0 0 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Urodacus 'weld range 3' potential 0 1 0 0 1 0 4 0 0 0 0 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Urodacus 'weld range 4' potential 0 0 1 0 0 0 0 0 0 0 0 3 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Urodacus 'weld range 5' potential 0 0 1 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

Chilopoda (Geophilida)

Mecistocephalidae potential 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

Chilopoda (Scolopendrida)Scolopendridae Scolopendra morsitans no 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

Diplopoda (Polyxenida)

Synxenidae no 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

Malacostraca (Isopoda)

Armadillidae Buddelundia ' sp.10' no 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0Buddelundia 'sp.13' unlikely 1 0 2 266 0 0 1 0 0 2 2 5 1 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Pseudodiploexochus 'sp. 1' likely 9 2 0 12 4 0 0 0 0 0 0 10 9 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Pseudodiploexochus ' sp. 2' likely 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0genus nov. sp. nov. potential 5 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

Molluscs (Gastropoda)

Camaenidae Pleuroxia ?bethana yes 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0Pupillidae Gastrocopta bannertonensis no 0 0 0 0 0 0 0 0 2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

Pupoides beltianus no 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 2 0 0 0 0 0 0 0 0 0 0 0 0 0Pupoides eremicolus no 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0Pupoides pacificus no 1 0 0 0 0 2 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0

Succineidae Succinea sp. undetermined 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1 0 0 0 0 0 0 0 0 0 0 0 0 0 0

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4.3 SPECIMENS COLLECTED

4.3.1 Arachnida: Mygalomorphae

4.3.1.1 Family: Dipluridae

Cethegus sp.

A single specimen of the genus Cethegus was collected from site P12, an area of low Acacia ramulosa woodland on a floodplain. The specimen was a juvenile and therefore could not be identified to species as typically mature males are required. The known range of Cethegus exceeds the limit for a SRE, however it is possible that a species complex is found at Weld and Robinson Ranges and Jack Hills (Framenau 2011), therefore this specimen represents a potential SRE species.

4.3.1.2 Family: Idiopidae

Euoplos sp.

A single specimen of the genus Euoplos was collected from site P10, an area of low Acacia aneura woodland on a floodplain. The specimen was a female and thus could not be identified to species. Main (2000) restricted the range of Euoplos to the Tropic of Capricorn. Based on the current knowledge and known diversity of Euoplos, the specimen represents a potential SRE species (Framenau 2011)

Gaius sp.

A single specimen of the genus Gaius was collected from site P05, an area of open scrub with Acacia sclerosperma over saltbush and bluebush on a floodplain. The specimen was a juvenile and therefore could not be identified to species, however, the genus is well represented throughout Western Australia and most species have wide distributions (Framenau 2011), thus the specimen does not represent a SRE species.

4.3.1.3 Family: Nemesiidae

Aname sp.

A single specimen of the genus Aname was collected from site P01, an area of A. ramulosa and various scrub spp. on a floodplain. The specimen was juvenile and thus could not be identified to species. Aname regularly belongs to the most diverse mygalomorph genera in biological spider surveys (Durrant et al. 2010) and many appear to have restricted distributions (Framenau 2011). As such, this specimen represents a potential SRE species.

Aname 'MYG228'

A single specimen of Aname ‘MYG228’ was collected from P07, an area of low A. aneura woodland on a floodplain. This species was previously not known from the WAM mygalomorph species collection and thus represents a potential SRE species (Framenau 2011).




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Aname 'MYG229'

A single specimen of Aname ‘MYG229’ was collected from site P01, an area of A. ramulosa and various scrub spp. on a floodplain. This species was previously not known from the WAM mygalomorph species collection and thus represents a potential SRE species (Framenau 2011).

Kwonkan 'MYG230'

A single specimen of Kwonkan ‘MYG230’ was collected from site P01, an area of A. ramulosa and various scrub spp. on a floodplain. This species was previously not known from the WAM mygalomorph species collection and thus represents a potential SRE species (Framenau 2011).

4.3.2 Arachnida: Pseudoscorpiones

4.3.2.1 Family: Atemnidae

Oratemnus sp.

Two specimens of the genus Oratemnus were collected from site F02, an area of low A. aneura woodland on a foot slope which drains to a floodplain. The taxonomy of Oratemnus is uncertain, however based on current knowledge it Oratemnus is not considered to be a SRE (Burger and Harvey 2011) .

4.3.2.2 Family: Chernetidae

`sp. 1 Yeelirrie` and `sp. 2 Yeelirrie`

A single specimen of ‘sp. 1 Yeelirrie’ and 20 specimens of ‘sp. 2 Yeelirrie’ were collected from site P04, an area of A. ramulosa and various scrub spp. on a floodplain. These specimens are likely to belong to new genera as the taxonomic knowledge of Chernetids is limited, however, based on the distribution of other Chernetids these specimens are not considered to be SREs (Burger and Harvey 2011).

Nesidiochernes sp.

Three specimens of the genus Nesidiochernes were collected from site P04, an area of A. ramulosa and various scrub spp. on a floodplain. The genus is widely distributed throughout Australia and these specimens resemble a species that is widely distributed in Southern Australia and thus is not a SRE species (Burger and Harvey 2011).

4.3.2.3 Family: Garypidae

Synsphyronus `sp. PSE010`

A total of 73 specimens of Synphyronus ‘sp. PSE010’ were collected from sites P03, P05, P06, P07, P08, P09, P10, P11, P12, P13 and F02. These sites consisted primarily of low A. aneura woodland on a floodplain. Synsphyronus ‘sp. PSE010’ has been recorded elsewhere near Weld Range, however the extent does not exceed 50 km (Burger and Harvey 2011)and thus may represent a SRE.




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4.3.2.4 Family: Olpiidae

Austrohorus sp.

Three specimens of the genus Austrohorus were collected from sites F03 and F06, low A. aneura woodland on a foot slope and A. sclerosperma scrubland on a floodplain. These specimens appear to be similar to other specimens of the genus collected in Western Australia. However, based on current knowledge of the group the SRE status cannot be determined (Burger and Harvey 2011).

Beierolpium

A total of 32 specimens of the genus Beierolpium, were collected from 14 sites. These sites were located in areas of A. anueura and A. ramulosa woodland and scrublands consisting of Acacia quadrimarginea, A. ramulosa and mulga. Identified from this survey were eight species, Beierolpium`sp. (juv. 3/1)`, Beierolpium`sp. (juv. 6/2)`, Beierolpium`sp. (juv. 7/2)` , Beierolpium`sp. (juv. 7/3)`, Beierolpium `sp. 8/2`, Beierolpium `sp. 8/3`, Beierolpium `sp. 8/4 lge` and Beierolpium `sp. 8/4 small`. The taxonomy of Beierolpium has not been fully assessed and thus species are currently identified by the number of sensory hairs on the fixed and movable fingers. A full taxonomic revision is required to identify the SRE status of Beierolpium species and as such all species represent potential SRE species (Burger and Harvey 2011).

Euryolpium sp.

Four specimens of the genus Euryolpium were collected from sites P02, P08 and P10, areas of A. ramulosa and various scrub spp. and low A. aneura woodlands on a floodplain. Euryolpium are commonly found under bark and rocks throughout Australia, but are not often recorded as far south as these specimens (Burger and Harvey 2011). Based on current knowledge the SRE status of these specimens is undetermined.

Indolpium sp.

Five specimens of the genus Indolpium were collected from sites P02, P03, P07 and P11, areas of low A. aneura woodland and mulga and A. ramulosa scrub. These specimens resemble specimens collected elsewhere in Western Australia, which suggests the genus is widespread. Based on current knowledge, it is unlikely that these specimens represent a SRE species (Burger and Harvey 2011)

4.3.3 Arachnida: Scorpiones

4.3.3.1 Family: Buthidae

Isometroides sp. indet.

Two juvenile specimens of the genus Isometroides were collected from sites P7 and P13, areas of low woodland of A. aneura and A. ramulosa on floodplain. The taxonomy of Isometroides is poorly resolved and mature males are required for identification, thus identification beyond genus could not be completed. Due to a paucity of data, these specimens represent a potential SRE (Volschenk 2011).

Lychas 'splendens'

Six specimens of Lychas ‘splendens’ were collected from sites P4, P10, P13, F6 and F16, areas of woodland containing A. aneura and A. ramulosa as well as shrublands. Lychas is widespread across mainland Australia and many species have wide distributions, Lychas ‘splendons’ included. Therefore it is not a SRE species (Volschenk 2011).




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4.3.3.2 Family: Urodacidae

Urodacus sp. indet.

Two juvenile specimens of the genus Urodacus were collected from sites P5 and P6, open scrub with scattered mulga and A. sclerosperma and low A. aneura woodland. As mature males are required for identification thus identification beyond genus could not be completed. Urodacus is very diverse in Western Australia and contains both widespread and SRE species (Volschenk 2011). As such they represent a potential SRE species.

Urodacus 'gibson 1'

Two specimens of Urodacus ‘gibson 1’ were collected from site P10, low woodland of A. aneura. Urodacus is very diverse in Western Australia and contains both widespread and SRE species (Volschenk 2011). Urodacus ‘gibson 1’ has been recorded elsewhere in Western Australia and does not represent a SRE species.

Urodacus 'weld range 3'

Eight specimens of Urodacus ‘weld range 3’ were collected from sites P2, P5, P7, P12 and P13, open scrub and scrublands with scattered mulga and low woodland of A. aneura, A. ramulosa and A. sclerosperma. Urodacus is very diverse in Western Australia and contains both widespread and SRE species (Volschenk 2011). Urodacus ‘weld range 3’ is only known from these specimens at Weld Range and thus represents a potential SRE species.


Six specimens of Urodacus ‘weld range 4’ were collected from sites P3, P12 and P13, areas of A. ramulosa low woodland and shrubland. Urodacus is very diverse in Western Australia and contains both widespread and SRE species (Volschenk 2011). Urodacus ‘weld range 4’ is only known from these specimens at Weld Range and thus represents a potential SRE species.


Two specimens of Urodacus ‘weld range 5’ were collected from sites P3 and P12, areas of A. ramulosa low woodland and shrubland. Urodacus is very diverse in Western Australia and contains both widespread and SRE species (Volschenk 2011). Urodacus ‘weld range 5’ is only known from these specimens at Weld Range and thus represents a potential SRE species.

4.3.4 Chilopoda: Geophilida

4.3.4.1 Family: Mecistocephalidae

A single specimen of the family Mecistocephalidae was collected from site P10, an area of low A. aneura woodland on a floodplain. The taxonomy of Geophilida is poorly known and thus the genus of this specimen is unknown. It is possible that some geophilids are SRE species but a full taxonomic revision would be required (Burger and Harvey 2011). As such the specimen represents a potential SRE species.




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4.3.5 Chilopoda: Scolopendrida

4.3.5.1 Family: Scolopendridae

Scolopendra morsitans

A single specimen of Scolopendra morsitans was collected from site P02, an area of scrublands consisting of A. ramulosa and various species of scrub. The family Scolopendridae are widespread across Western Australia and S. morsitans is well represented in many areas, as such it does not represent a SRE species (Mieke Burger, Pers. Comm.).

4.3.6 Diplopoda (Polyxenida)

4.3.6.1 Family: Synxenidae

A single specimen of the family Synxenidae was collected from site P02, an area of scrublands consisting of A. ramulosa and various species of scrub. The family Synxenidae is known from several areas of Western Australia and does not contain SRE species, thus this specimen does not represent a SRE species (Mieke Burger, Pers. Comm.).

4.3.7 Malacostraca: Isopoda

4.3.7.1 Family: Armadillidae

Buddelundia 'sp.10'

A single specimen of Buddelundia 'sp.10' was collected from site F02, an area of low A. aneura woodland on a footslope which drains to a floodplain. Buddelundia 'sp.10' is a large species and one of the most common arid zone forms of the genus. There are slight variations among its distribution but it is widespread and thus not a SRE species (Judd 2011).

Buddelundia 'sp.13'

A total of 281 speicmens of Buddelundia 'sp.13’ were collected from sites P01, P03, P04, P07, P10, P11, P12, P13 and F01, these sites were in areas of A. anueura and A. ramulosa woodland and scrublands consisting of Acacia quadrimarginea, A. ramulosa and mulga. Buddelundia 'sp.13’ is a common species and has been collected from the PIlbara as well as the Midwest but there are slight differences between those found in the Midwest and the Pilbara (Judd 2011). It is unlikely that this species represents a SRE.


A total of 46 specimens of Pseudodiploexochus 'sp. 1' were collected from P01, P02, P04, P05, P12 and P13, areas of low A. ramulosa woodland, A. ramulosa and various scrubland and open scrub with A. sclerosperma over saltbush and bluebush. Pseudodiploexochus 'sp. 1' is a previously undescribed species as this genus is more commonly collected in the high rainfall areas of the south west (Judd 2011). Pseudodiploexochus 'sp. 1' is likely to represent a SRE species.




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A single specimen of Pseudodiploexochus 'sp. 2 was collected from site P03, an area of A. ramulosa and various scrublands on a floodplain. There were marked differences between P. 'sp. 1' and P. 'sp. 2' which suggests they are different species. Pseudodiploexochus is more commonly associated with high rainfall areas and thus it is highly likely to represent a SRE species (Judd 2011).

genus nov. sp. nov.

Five specimens of an undescribed species were collected from site P01, an area of A. ramulosa and various scrublands on a floodplain. These specimens represent a new genus beside Buddelundia and Barrowdillo and a previously unknown species as well (Judd 2011). As such, these specimens represent a potential SRE species.

4.3.8 Molluscs: Gastropoda

4.3.8.1 Family: Camaenidae

Pleuroxia ?bethana

A single specimen most closely resembling Pleuroxia bethana was collected from site P07, an area of low A. aneura woodland on a floodplain. Due to differences in shell morphology, this specimen is not confidently placed as P. bethana (Whisson 2011). Based

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20111124 1328 report ND MDQA - EPA WA | EPA Western Australia · 2021. 1. 4. · Sinosteel Midwest Corporaton Weld Range Haul Road Short Range Endemic Invertebrate Survey November