Boundary Hill South Project Environmental Impact Statement Volume 5 – Appendices February 2014 Boundary Hill South Project P2

Terrestrial Fauna Assessment

NOTE:

At the time of preparation of this technical assessment, the Project site included a larger footprint of 1,069 hectares. In June 2013, a decision was made to reduce the size of the Project site by removing a portion of the Mining Lease Application (MLA) area. This portion of the site, otherwise known as the Timber Reserve area, has been removed from the Project MLA and will not be subject to mining activity as part of the Project. This amendment to the MLA boundary reduces the size of the Project site from 1,069 hectares to 630 hectares. As such, the terrestrial fauna assessment has been undertaken within a broader survey area and included the Timber Reserve area. Whilst the terrestrial fauna survey was undertaken over the broader study area to include the originally proposed MLA, the impact assessment contained in Chapter 12A Terrestrial Ecology considers the revised Project area of 630 hectares.

Boundary Hill South Environmental Impact Statement

Boundary Hill South Anglo Coal (Callide Management) Pty Ltd 01-Nov-2012 Doc No. 60238883

Terrestrial Fauna Technical Report

AECOM Boundary Hill South Terrestrial Fauna Technical Report

Terrestrial Fauna Technical Report

Client: Anglo Coal (Callide Management) Pty Ltd

ABN: 75 009 666 200

Prepared by

AECOM Australia Pty Ltd 21 Stokes Street, PO Box 5423, Townsville QLD 4810, Australia T +61 7 4729 5500 F +61 7 4729 5599 www.aecom.com ABN 20 093 846 925

01-Nov-2012

Job No.: 60238883

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\\autsv1fp001\Jobs\MMPL\60238883\6. Draft Docs\6.1 Reports\Rev 02 Issue\Appendices\Appendix P2 - Terrestrial Fauna.docx Revision 01 – 01-Nov-2012 Prepared for – Anglo Coal (Callide Management) Pty Ltd – ABN: 75 009 666 200 AECOM Boundary Hill South Terrestrial Fauna Technical Report

Quality Information

Document Terrestrial Fauna Technical Report

Ref 60238883

Date 01-Nov-2012

Prepared by Annemarie van Doorn

Reviewed by Joss Bentley

Revision History

Authorised Revision Revision Details Date Name/Position Signature

1 23-Oct-2012 Draft for Review Joss Bentley

A 9-Nov-2012 Final Copy Rouven Lau Associate Director - Environment 01 25-Oct-2013 Final Andrew Walsh Project Manager

Table of Contents Executive Summary i 1.0 Introduction 2 1.1 Scope of Works 2 1.2 Project Site 2 1.3 Commonwealth Legislation 5 1.4 Queensland Legislation 5 1.5 Ecological Offsets 8 2.0 Methodology 11 2.1 Taxonomic Nomenclature 11 2.2 Determination of Significance Level for Fauna 11 2.3 Fauna Desktop Assessment 11 2.4 Fauna Field Survey 11 2.4.1 Detailed Survey Sites 11 2.4.2 Secondary Survey Sites 14 2.4.3 Fauna Habitat Assessments 14 2.4.4 Incidental Observations 15 2.4.5 Survey Locations 15 2.4.6 Survey Timing 15 2.4.7 Analyses 15 2.4.8 Threatened Species 15 2.5 Assumptions and Limitations 16 3.0 Existing Ecological Environment 18 3.1 Available Habitat Types 18 3.2 Essential Habitat 24 3.3 Environmentally Sensitive Areas 24 3.4 Bioregional Corridors and Habitat Connectivity 24 3.5 Species Diversity 30 3.6 Edge of Range Species 30 3.7 Threatened Fauna 30 3.8 Migratory Fauna 43 3.9 Breeding Sites 48 3.10 Culturally Significant Fauna 48 3.11 Introduced Pest Species 50 4.0 Conclusions and Recommendations 52 5.0 References 53 Appendix A Desktop Searches A Appendix B Fauna Habitat Assessments B Appendix C Terrestrial Fauna Recorded during Field Surveys C Appendix D Fauna Analyses Results D

Executive Summary AECOM was commissioned by Anglo Coal (Callide Management) Pty Ltd to determine the terrestrial fauna values for the Boundary Hill South Lease Extension (BHSLE) project. The EPBC referral for the BHSLE project (the Project) was lodged on 16 March 2012 as Commonwealth database searches indicate that the project may impact on some matters of national environmental significance. This technical report will guide the fauna component of the Environmental Impact Statement (EIS) fauna and flora chapter measuring potential impacts and instating adequate mitigation measures to reduce the environmental impact of the Project on the existing fauna assemblage with particular emphasis on Endangered, Vulnerable, and Near Threatened (EVNT) species. Four regional ecosystems (RE’s) are mapped by the Department of Environment and Heritage Protection (DEHP) in the Study Area, all of which have a Vegetation Management Act 1992 status of Least Concern. However, RE 11.3.25 (Eucalyptus tereticornis or E. camaldulensis woodland fringing drainage lines) has ‘Of Concern’ biodiversity status. Two RE’s restricted in distribution in the Project area that may support a high number of EVNT species include RE 11.3.25 (blue gum Eucalyptus tereticornis along creeks) and RE 11.10.13 (brown bloodwood Corymbia trachyphloia and ironbark Eucalyptus suffulgens on upper sandstone slopes). In addition, large connected areas of woodland, such as RE 11.9.9 and 11.10.1 also provide habitat for a diversity of terrestrial fauna species. Disturbances recorded in the Project site included weeds, introduced pests, erosion, fire and grazing. All sites had some form of disturbance with weeds and introduced pest species being present throughout the Project site. The effects of a hot fire was evident at all sites located east of the power line easement and may have impacted the diversity of terrestrial fauna recorded during surveys. No essential fauna habitat was recorded within the Project site. The project is affected by a Category C Environmentally Sensitive Area (ESA) which consists of the Callide Timber Reserve. As a Category C ESA, the Callide Timber Reserve falls under the Forestry Act 1959. Within the Project site, remnant vegetation is mapped as medium State ecosystem diversity, with the exception of one small area of high diversity located in the far south west section. Larger areas of high biodiversity are located to the east of the Project boundary. There are no regional corridors mapped, however, the boundary of the mapped State biodiversity corridor is located in the north east of the Project site. Field surveys recorded a total of 107 fauna species, comprising 68 bird species, 3 amphibians, 10 reptiles and 26 mammals with five additional mammal species being possibly present. Of these, three EVNT species were recorded: - Black-chinned honeyeater Melithreptus gularis Near Threatened under the NC Act. - Squatter pigeon Geophaps scripta scripta, Vulnerable under the EPBC Act and the NC Act; - Little pied bat Chalinolobus picatus Near Threatened under the NC Act. In addition to the species recorded, the field survey also recovered a scat that could possibly be attributed to a northern quoll (Dasyurus hallucatus). The northern quoll, listed as ‘Endangered’ under the EPBC Act is assumed to be present within the Project sit as it is within the mapped distribution, suitable habitat is present, and it has recently been recorded in close vicinity. Although not recorded during surveys, multiple threatened Brigalow Belt reptiles are highly likely to occur in the Project site as suitable habitat is present based on distribution maps and fauna habitat assessments. Suitable habitat for the koala Phascolarctus cinereus (Vulnerable, EPBC ACT) was also found to be present in the Project site. One migratory species, rainbow bee-eater Merops ornatus, was recorded during the survey and additional species are either possible or likely to occur. The echidna, Tachyglossus aculeatus, is a culturally significant species found to be widespread during surveys. Six introduced pest species, not including domestic animals, were recorded during field surveys, of which five are considered as a key threatening process. Pest species were found throughout the Project site with European foxes Vulpes vulpes and cane toads Bufo marinus being the most widely distributed.

1.0 Introduction Anglo Coal (Callide Management) Pty Ltd operates the Callide Mine, which is located in the Callide Basin of Central Queensland, approximately 20 km northeast of the rural town of Biloela and 85 km south west of the port of Gladstone (Figure 1). Callide Mine consists of four existing pits: Dunn Creek; The Hut; Trap Gully; and the Boundary Hill pit, which is located 20 km to the north of Dunn Creek operations. Coal production from the Callide Mine is currently 10 million tonnes per annum and the majority of the coal is used for domestic power generation in the Queensland market. The existing Boundary Hill operation has a limited life span with resources expected to be exhausted by 2014. The successful approval and construction of the Boundary Hill South Lease Extension (BHSLE) project on Mining Lease Application (MLA) 80186, before 2014, will allow the mine to continue to provide resources that support long term secured contracts with the Callide and Gladstone Power Stations. An EPBC referral for the BHSLE project was lodged on 16 March 2012 as Commonwealth database searches indicate that the project may impact on some matters of national environmental significance. A controlled action decision was made with the project proceeding under a bilateral agreement with the Qld government, to be assessed as a voluntary EIS under the Environment Protection Act 1994. This report presents the terrestrial fauna values for the BHSLE (the Project).

1.1 Scope of Works The scope of the terrestrial fauna assessment is to determine the characteristics of the existing fauna assemblage within the proposed expansion area, through desktop and field surveys. Specifically, the assessment considers: - Available fauna habitat, including movement corridors and existing barriers; - Species diversity; - A list of recorded and likely to occur fauna species recognised as threatened under State and Commonwealth legislation. - Identification of potential habitat for threatened species; - Migratory fauna; - Species that are at their distributional limit; - Culturally significant species; - Breeding and nesting sites; - Introduced pest species; and - Recommendations for management of issues particularly related to fauna.

1.2 Project Site The Project is located immediately to the south of the existing Boundary Hill operation, within the Banana Shire Council local government area (Figure 2). The Boundary Hill operation is located over Mining Leases (ML) 5655 and 6994. The Project site is located on MLA 80186.The proposed 2007 MLA area overlaps the proposed 2011 MLA area and together make up for about 1,691 ha (the Project site). The mine lease area is surrounded by agricultural land including grazing, improved pasture and cropping land. Several properties around Callide are pastoral properties as well as one timber reserve. The lowland has mostly been cleared for agriculture with most vegetated areas confined to more rugged land within Callide’s north. The Project site lies in the Brigalow Belt South Bioregion (Interim Biogeographic Regionalisation for Australia, IBRA 2005). There are no areas designated as National Park located within the footprint of the Project site. To the north east of the BHSLE there is an existing Timber Reserve (Callide Timber Reserve TR170 on plan FTY1843).

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T Image © ESRI T StreetPro © 2010 Pitney Bowes Software Pty Ltd E N Roads, Rivers - © 2010 PSMA Australia Pty Ltd R U Service Layer Credits: Source: Esri, DigitalGlobe, GeoEye, i-cubed, B USDA, USGS, AEX, Getmapping, Aerogrid, IGN, IGP, swisstopo, and the AECOM does not warrant the accuracy or completeness of information displayed in this map and any person using it does so at their own risk. AECOM shall bear no responsibility or liability for any errors, faults, defects, or omissions in the information. BOUNDARY HILL SOUTH LEASE EXPANSION (BHSLE) Mount Morgan Ranges Bio-geographical Subregions Detailed Project Site

Figure 2

Mount Morgan Ranges Bio-geographical Subregions Callide Creek Downs Bio-geographical Subregions

Legend

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M l i Image supplied by Callide Mine (date unknown). a K StreetPro © 2010 Pitney Bowes Software Pty Ltd ll in Roads, Rivers - © 2010 PSMA Australia Pty Ltd s e Sub-bioregions - DERM 2012 o d i n l s l a AECOM does not warrant the accuracy or completeness of information displayed in this R C map and any person using it does so at their own risk. AECOM shall bear no responsibility d or liability for any errors, faults, defects, or omissions in the information. AECOM Boundary Hill South 5 Terrestrial Fauna Technical Report

1.3 Commonwealth Legislation Environment Protection and Biodiversity Conservation Act 1999 During the last few decades, changes to the landscape and habitat of native wildlife as a result of human activity have put many species of plants and animals at risk. The Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act) is administered by the Department of Sustainability, Environment, Water, Population and Communities (SEWPAC) and together with its regulations is the Australian Government's central piece of environmental legislation. The EPBC Act provides the legal framework to protect and manage nationally and internationally important flora, fauna, ecological communities and heritage places, which is defined in the Act as Matters of National Environmental Significance (MNES). The eight matters of MNES to which the EPBC Act applies are: - World heritage sites; - National heritage places; - Wetlands of international importance (often called ‘Ramsar’ wetlands after the international treaty under which such wetlands are listed); - Nationally threatened species and ecological communities; - Migratory species listed under international treaties such as the Australian agreements with Japan (JAMBA) and China (CAMBA), Republic of Korea (ROKAMBA) and the Bonn Convention; - Commonwealth marine areas; - Nuclear actions; and - Great Barrier Reef Marine Park. Specifically, the EPBC Act aims to conserve Australia’s biodiversity and protect biodiversity internationally by: - Controlling the international movement of wildlife, - Providing a streamlined environmental assessment and approvals process for matters of national environmental significance; - Protecting world and national heritage; and - Promoting ecologically sustainable development. The EPBC Act protects Australia's native species and ecological communities by: - Listing of species and ecological communities as threatened, - Development of conservation advice and recovery plans for listed species and ecological communities; - Development of a register of critical habitat; - Recognition of key threatening processes; and - Where appropriate, reducing the impacts of these processes through threat abatement plans. Under the EPBC Act, an action will require approval from the Federal Environment Minister if the action will have or is likely to have a significant impact on a matter of national environmental significance. SEWPAC define a significant impact as an impact which is important, notable, or of consequence, having regard to its context or intensity. Whether or not an action is likely to have a significant impact depends upon the sensitivity, value, and quality of the environment which is impacted, and upon the intensity, duration, magnitude and geographic extent of the impacts.

1.4 Queensland Legislation Vegetation Management Framework The Vegetation Management Framework is administered by the Department of Environment and Heritage Protection (EHP) and regulates vegetation management on freehold and State land. The policy incorporates

several pieces of legislation, State policy, regional vegetation management codes, an offsets policy, a regrowth vegetation code as well as specific policies relating to material change of use and reconfiguration of lots. Specifically the framework operates under: - The Sustainable Planning Act 2009 (SPA) which regulates what activities are considered assessable development; - The Vegetation Management Act 1999 (VMA) which regulates the clearing of native vegetation in Queensland. The Act sets down the rules and regulations that guide what clearing can be done, and how it must be done to meet the requirements of the law. It regulates clearing of remnant on freehold land, and of remnant and some non-remnant vegetation on State tenures; - The Land Act 1994 (LA), which governs vegetation management on leasehold and other State land; - Regional Vegetation Management Plans. The State policy administers vegetation clearing to: - Protect remnant “endangered” and “of concern” regional ecosystems and areas of essential habitat; - Maintain the integrity and stability of landscapes including riparian and wetland areas; and - Manage vegetation where it is the most appropriate method to protect land from degradation. The VMA classifies regional ecosystems based on their extent across the bioregion (VMA status). In addition, specific criteria assess the condition of the regional ecosystem and used for planning and management applications (Biodiversity status). Native vegetation clearance (operational works ) that is considered assessable development is defined by Schedule 3 of the SP Regulations unless the clearing is mentioned in schedule 24 in relation to an activity or matter in part 1; or for particular land mentioned in part 2. Under part 1, Schedule 24 clearing of vegetation for a mining activity is not assessable. Nature Conservation Act 1992 The Nature Conservation Act 1992 (NC Act) is administered by the Department of Environment and Heritage Protection, for the conservation of nature. The Act is based on principles to conserve biological diversity, ecologically sustainable use of wildlife, ecologically sustainable development and international criteria developed by the World Conservation Union (International Union for the Conservation of Nature and Natural Resources) for establishing and managing protected areas. The NC Act protects wildlife habitat and regulates the taking and use of wildlife. 'Wildlife' means any taxon or species of an animal, plant, protista, or virus. The Act provides further protection for a range of rare and threatened species listed under the Nature Conservation Wildlife Regulations, which are considered to be Endangered, Vulnerable or Near Threatened. Table 1 outlines the meaning of each declaration category.

Table 1 Nature Conservation Act 1992 status and declaration categories Wildlife Declaration Status Category Endangered (a) there have not been thorough searches conducted for the wildlife and the wildlife has not been seen in the wild over a period that is appropriate for the life cycle or form of the wildlife; or (b) the habitat or distribution of the wildlife has been reduced to an extent that the wildlife may be in danger of extinction; or (c) the population size of the wildlife has declined, or is likely to decline, to an extent that the wildlife may be in danger of extinction; or (d) the survival of the wildlife in the wild is unlikely if a threatening process continues. Vulnerable (a) the population size or distribution of the wildlife has declined, or is likely to decline, to an extent that the wildlife may become endangered because of a threatening process; or (b) the population size of the wildlife has been seriously depleted and the protection of the wildlife is not secured; or (c) the population of the wildlife is—

Wildlife Declaration Status Category (i) low or localised; and (ii) dependent on habitat that has been, or is likely to be, adversely affected, in terms of quantity or quality, by a threatening process. Near Threatened (1) A regulation may prescribe native wildlife as near threatened wildlife if - (a) the population size or distribution of the wildlife is small and may become smaller; or (b) the population size of the wildlife has declined, or is likely to decline, at a rate higher than the usual rate for population changes for the wildlife; or (c) the survival of the wildlife in the wild is affected to an extent that the wildlife is in danger of becoming vulnerable. (2) Native wildlife may be prescribed as near threatened wildlife even if the wildlife is the subject of a threatening process.

Removing or relocating wildlife, including tampering with a breeding place is also controlled under the NC Act: The Act protects all native birds, reptiles, mammals and amphibians, along with a limited range of invertebrates (some butterflies, spiders and scorpions), freshwater fish and the grey nurse shark. If wildlife within a project area needs to be removed or relocated then an application for a damage mitigation permit is required. Interference with an animal breeding place used by a protected animal to incubate or rear the animal’s offspring requires the approval of the EHP Chief Executive which is achieved by way of a species management program submitted by the applicant. Critical habitat is defined under the Nature Conservation Act 1992 as: ‘habitat that is essential for the conservation of a viable population of protected wildlife or community of native wildlife, whether or not special management considerations and protection are required, and A critical habitat may include an area of land that is considered essential for the conservation of protected wildlife, even though the area is not presently occupied by the wildlife.” Habitat can be declared critical under a conservation plan for a protected species or an interim conservation order can be declared for a critical habitat by the CEO under the NCA. Further, under section 97 of the Act it is an offence to take, use, keep or interfere with native wildlife in an area identified under a conservation plan as, or including, a critical habitat or an area of major interest unless authorized or permitted to do so. Provision under the NCA is also made in relation to forest reserves. Part 4A of the Act States: “(1) The purpose of this part is to assist the dedication of areas within State forests, timber reserves, Land Act reserves or unallocated State land as protected areas. (2) The purpose is achieved primarily by providing for forest reserve dedications as an interim measure to assist the dedication of the areas as protected areas. (3) It is Parliament’s intention that, subject to any revocation under this part, each area of land dedicated as a forest reserve will become a protected area as soon as practicable after its dedication.” Land Protection (Pest and Stock Route Management) Act 2002 The Land Protection (Pest and Stock Route Management) Act 2002 (LP Act) is the primary legislation in Queensland for the management of flora and fauna pest species. The purpose of the Act and the regulation is to provide pest management for land and stock route network management in Queensland. This is achieved by: - Establishing principles of pest management for land; - Providing for pest management planning; - Declaring animals and plants to be pests; - Restricting the introduction, keeping or sale of declared pests; - Preventing the spread of declared pests in the State; and - Building and maintaining fences to prevent declared pests animals from moving from a part of the State to another part.

The Act requires all land owners and managers to undertake management of pest species that are present on their land. The principles of pest management for land are as follows: - Integration; - Public awareness; - Commitment; - Consultation and partnership; - Planning; - Prevention; - Best practice; and - Improvement.

Table 2 Pest management requirements

Class Status Control action required

1 Not commonly present or established in Queensland, and has Landowners and/or managers the potential to cause an adverse economic, environmental or should take reasonable steps to social impact in Queensland or another State keep their land free of Class 1 pests 2 Established in Queensland, and has, or could have a serious Landowners and/or managers adverse economic, environmental or social impact in should take reasonable steps to Queensland or another State keep their land free of Class 2 pests 3 Established in Queensland, and has, or could have an adverse Landowners and/or managers may economic, environmental or social impact in Queensland or be required to take steps to control another State a Class 3 pest if it threatens an environmentally significant area

1.5 Ecological Offsets Federal Policy In October 2012, SEWPAC released the environmental offsets policy under the EPBC Act. The policy focuses on the use of offsets under Part 9 (Approval of Actions) of the EPBC Act and primarily relates to terrestrial impacts and offsets, although some aspects of the approach are also relevant to the marine environment. The policy does not promote the use of offsets to justify environmental harm, but rather to counterbalance the impacts that remain after avoidance and mitigation issues have been exhausted and there are still ‘residual impacts’. The Environmental Offsets Policy will be applied to ‘controlled actions’ only after SEWPAC is satisfied that all other mitigation measures have been exhausted and where the residual impact is likely to have a significant impact on the relevant MNES. There are several offset requirements, as listed below. The offset must: 1. deliver an overall conservation outcome that improves or maintains the viability of the aspect of the environment that is protected by national environment law and affected by the proposed development; 2. be efficient, effective, transparent, proportionate, scientifically robust and reasonable; 3. be built around direct offsets but may include indirect offsets; 4. be of a size and scale proportionate to the impacts being offset; 5. be in proportion to the level of statutory protection that applies to the affected species or community; 6. effectively manage the risks of the offset not succeeding; and 7. have transparent governance arrangements including being able to be readily measured, monitored, audited and enforced. Queensland Government Environmental Offsets Policy The Queensland Government Environmental Offsets Policy (2008) provides an integrated, consistent and transparent framework for applying environmental offsets in Queensland. Environmental offsets are used to

replace the value of environmental features lost during development. However, offsets should only be considered after all environmental impacts have been avoided and minimised and if all other government environmental standards have been met. Under the framework provided by the Queensland Government Environmental Offsets Policy there are several other policies that are specific to particular issues, such as removal of marine habitat, koala habitat, regional ecosystems or State significant biodiversity values. Specific-issue offset policies under the Queensland Government Environmental Offsets Policy are: - Policy for Vegetation Management Offsets, version 3 (September 2011) - Marine Fish Habitat — Mitigation and Compensation for Works or Activities Causing Marine Fish Habitat Loss, 2002, Department of Primary Industries and Fisheries - Offsets for Net Gain of Koala Habitat in South East Queensland Policy, DERM 2010. The Biodiversity Offset Policy (version 1, 2011) describes offset requirements for impacts to a range of State significant biodiversity values, including: - EVNT species listed under the NC Act; - Wetlands (as defined in VM Act and SPP4/11 Protecting wetlands of high ecological significance in Great Barrier Reef catchments) - Watercourses (as defined in the VM Act); - Endangered and Of Concern REs (including grassland REs); - High Value Regrowth (HVR) of Endangered and Of Concern REs; - Threshold and critically limited REs; - Essential habitat and essential regrowth habitat; and - Connectivity (defined as remnant or regrowth areas that are within 500 m of a State significant biodiversity value and that provide important connectivity or are at least 5 ha in size). Essential habitat is defined as habitat where EVNT species are known to occur and is mapped by the State. Under the Biodiversity Offset policy, Level 1 mining activities (Chapter 5 activities) trigger the imposition of environmental offset conditions under section 201 and 305 on an environment authority (mining lease) and environmental authority (mining activities). Environmentally Sensitive Areas under the Environmental Protection Regulation 2008 Sections 25 and 26 of the Environment Protection Regulation define category A and B environmentally sensitive areas. A category A environmentally sensitive area (which are those where mining activities are excluded) include; national park (including scientific) Aboriginal land, Torres Strait islander land, Cape York Peninsula Aboriginal land and recovery; a conservation park; a forest reserve; the wet tropics area under the Wet Tropics World Heritage Protection and Management Act 1993; the Great Barrier Reef Region under the Great Barrier Reef Marine Park Act 1975; and a marine park under the Marine Parks Act 2004, other than a part of the park that is a general use zone under that Act. A category B environmentally sensitive area includes: “(a) any of the following areas under the Nature Conservation Act 1992— (i) a coordinated conservation area; (ii) a wilderness area; (iii) a World Heritage management area; (iv) an international agreement area; (v) an area of critical habitat or major interest identified under a conservation plan; (vi) an area subject to an interim conservation order; (b) an area subject to the following conventions to which Australia is a signatory— (i) the ‘Convention on the Conservation of Migratory Species of Wild Animals’ (Bonn, 23 June 1979);

(ii) the ‘Convention on Wetlands of International Importance, especially as Waterfowl Habitat’ (Ramsar, Iran, 2 February 1971); (iii) the ‘Convention Concerning the Protection of the World Cultural and Natural Heritage’ (Paris, 23 November 1972); (c) a zone of a marine park under the Marine Parks Act 2004; (d) an area to the seaward side of the highest astronomical tide; (e) the following under the Queensland Heritage Act 1992— (i) a place of cultural heritage significance; (ii) a registered place; (f) an area recorded in the Aboriginal Cultural Heritage Register established under the Aboriginal Cultural Heritage Act 2003, section 46, other than the area known as the ‘Stanbroke Pastoral Development Holding’, leased under the Land Act 1994 by lease number PH 13/5398; (g) a feature protection area, State forest park or scientific area under the Forestry Act 1959; (h) a declared fish habitat area under the Fisheries Act 1994; (i) a place in which a marine plant under the Fisheries Act 1994 is situated; (j) an endangered regional ecosystem identified in the database known as the ‘Regional ecosystem description database’ kept by the department.” Standard mining and exploration activities are excluded from within 1 km of these areas, but non-standard mining activities, such as the Project, may occur within these areas after an appropriate level of assessment (e.g. an EIS).

2.0 Methodology

2.1 Taxonomic Nomenclature Taxonomic nomenclature within this report follows the CSIRO List of Australian Vertebrates (Clayton et al., 2007), with the exception of bats, which follow Churchill (2008).

2.2 Determination of Significance Level for Fauna Endangered, Vulnerable and Near Threatened (EVNT) fauna species are those listed as: - Critically Endangered, Endangered or Vulnerable under the Commonwealth Environment Protection and Biodiversity Conservation Act 1999 (EPBC Act). - Endangered, Vulnerable or Near Threatened under the Queensland Nature Conservation Act 1992 (NC Act). All other species are considered to be of Least Concern.

2.3 Fauna Desktop Assessment The desktop assessment included a review of the following data sets: - Areas of conservation significance, species and ecological communities identified in SEWPAC Protected Matters Searches of the Study site. An initial search was undertaken in March 2012 with a subsequent search in September 2012. The searches encompassed 25 km and 100 km radium from the centre point of the proposed expansion area. - Queensland Herbarium RE mapping (version 6.1) for a buffer extending 5 km around the proposed expansion area (the study area), to identify the vegetation communities mapped at a scale of 1:100,000 as occurring in the study area. This mapping also provided mapping of essential habitats. An examination of aerial photography was used in conjunction with the existing vegetation mapping. This review provided an appreciation of the vegetation types within the wider study area and the Project’s proximity to sensitive areas. - Species data from the DEHP WildNet databases. An initial search was undertaken in March 2012 with a subsequent search in September 2012. The searches encompassed 25 km and 100 km radium from the centre point of the proposed expansion area. - Species data from the Queensland Museum was sourced in August 2012. Reviews focused on fauna species within 25 km and 100 km buffer areas from the central point of the expansion area. - Environmentally Sensitive Area (ESA) mapping by DEHP to identify sensitive environmental values in the study area, including significant wetlands, Endangered and Of Concern REs and protected areas. - Biodiversity Planning Assessment (BPA) mapping by DERM (2008) to identify significant wildlife corridors and areas of State, regional or local biodiversity significance. - Wetland mapping by DERM (2009) to determine the classification, extent and significance of wetlands within the Project site.

2.4 Fauna Field Survey 2.4.1 Detailed Survey Sites Five detailed survey sites were established to sample representative fauna. Sites were located in areas where the probability of finding EVNT species was estimated to be the highest. Survey locations aimed to sample the representative regional ecosystems located within the Project site. A hot fire had occurred less than 12 month prior to the survey and multiple sites were affected. Research suggests that fauna diversity may be impacted by a hot fire, particularly for diurnal reptiles (e.g. Legge et al., 2008). Table 3 illustrates the representative RE for each fauna survey site and whether the site was affected by fire.

Table 3 Representative regional ecosystems (RE’s) at study sites, their coverage in the Project site and the impact of fire

Site ID Representative RE % of Project Affected by recent site fire (< 12 months)

Detailed Site 1 11.10.1, Lemon-scented gum Corymbia 27.7 Yes citriodora and ironbark Eucalyptus crebra on coarse-grained soils Detailed Site 2 11.9.9, Ironbark Eucalyptus crebra, grey 22.4 No bloodwood Corymbia clarksoniana and peppermint Eucalyptus exerta on red soils Detailed Site 3 11.3.25, Blue gum Eucalyptus tereticornis 0.8 No along creeks Detailed Site 4 11.9.9, Ironbark Eucalyptus crebra, grey 22.4 Yes bloodwood Corymbia clarksoniana and peppermint Eucalyptus exerta on red soils Detailed Site 5 11.10.1, Lemon-scented gum Corymbia 27.7 Yes citriodora and ironbark Eucalyptus crebra on coarse-grained soils Secondary Site 1 11.10.13, Brown bloodwood Corymbia 0.5 Yes trachyphloia and ironbark Eucalyptus suffulgens on sandstone upper slopes Secondary Site 2 11.9.9 regrowth, on edge with cleared 12.6 No pasture

Table 4 Survey effort at detailed survey sites

Method Effort per site Target taxa

Box traps – Elliott ‘A’ 20 traps, 4 nights 1 Small mammals

Box trap – Elliott ‘B’ 5 traps, 4 nights 1 Medium mammals and reptiles

Wire cage trap 5 traps, 4 nights 1 Medium mammals

Pitfall traps 6 x 20L buckets, 30m drift fence,4 Reptiles, amphibians, small days, 4 nights 1 mammals Funnels 2 with 30m drift fence, 4 days, 4 Reptiles and amphibians nights Hair tubes 10, 5 on tree trunks, 5 on the Mammals ground, 4 days, 4 nights Acoustic bat detector 1, 4 nights Microbats

Diurnal active search 30 mins, 3 days (2 people). Total Reptiles, amphibians search effort 3 person-hours Spotlighting and nocturnal active 20-45 minutes on minimum 2 nights Nocturnal birds, mammals, reptiles, search (2 people). Minimum total search amphibians effort 2 person-hours. Cameras 4, 4 days, 4 nights Mammals, medium to large reptiles

Diurnal bird survey 20 mins, 4 mornings. Total search Birds effort 1.3 person-hours 1 During the survey in April 2012, pitfalls were only open for three nights due to time constraints.

Bird Survey Methods Diurnal bird surveys were undertaken using the 20 minute two hectare search area recommended by the Atlas of Australian Birds. Surveys were undertaken on four mornings, and were completed within four hours of dawn. Records were based both on direct observation and species-specific vocalisations. Nocturnal bird records were based on observations or vocalisations heard during spotlighting. Information recorded included species and where possible number. Spotlighting involved active searches over a minimum of two nights with a minimum search effort of two person hours. During the first field trip in April, due to mine safety work time limits, spotlighting could only take place on two nights. On these occasions survey time was increased to 45 minutes per person over two nights. During the September surveys detailed sites were surveyed over three nights. One observer used a hand held 100W spotlight, the other a high intensity LED head torch. In addition to formal surveys, incidental observations of birds while undertaking other activities (e.g. checking traps, driving) were also made, noting species and number of individuals. Reptile Survey Methods A variety of survey methods are generally required to adequately survey reptiles, with survey outcomes strongly influenced by weather conditions (SEWPAC, 2011c). Techniques used included pitfall trapping, funnel traps and active diurnal and nocturnal searching on foot, focusing on likely reptile habitats and refuges. Twenty litre buckets were used for pitfall traps, with six evenly spaced along a 30m fence consisting of 30cm high damp course. A funnel trap was placed at either end of the drift fence. A shallow layer of earth and litter was placed in the base of each bucket, along with a section of PVC tube to provide shelter for captured animals, a damp cloth to provide moisture and a small float to ensure captured animals didn’t drown if heavy rainfall occurred. Funnel and pitfall traps were left open both during the day and at night, and were open for three days and four nights. Timed diurnal searches were undertaken in the late afternoon, when conditions were warm and reptiles were likely to be active. Searches targeted a variety of substrates, but particular attention was paid to likely basking and refuge sites, including rock surfaces/outcrops, fallen logs and timber, decorticating and fallen bark and litter. Searches were undertaken by two observers on four days, for a period of 30 minutes. Nocturnal searches occurred in the early evening, when temperatures were higher and reptiles more likely to be active. For geckos and nocturnal snakes, tree trunks and decorticating bark were targeted, as were riparian areas, standing water pools where frogs were calling and likely to attract frog-eating snakes. Spotlighting methods for reptiles was the same as those for birds detailed above. Information recorded included species, number, and where possible sex and breeding condition. Amphibian Survey Methods Survey methods for amphibians were the same as those used for reptiles, the only differences being the substrates/habitats targeted during active searches. Specifically, for frogs, moist habitats such as creeks, wetlands and standing pools of water were targeted, or any areas where frogs were heard calling. Mammal Survey Methods Ground-dwelling mammals were surveyed using a variety of box and cage traps, as well as pitfall traps, hair tubes, cameras and active nocturnal searches. Small mammals were targeted with small (Type A) Elliott aluminium box traps. Twenty traps were set out in a square, with five traps along each side, each separated by 20m. A large Elliott trap (Type B) was placed at each corner of the square, also 20m from the adjoining traps, and one within the square. A wire cage trap was placed in the centre of each side of the square (20m from adjoining traps), and in the middle of the square (hence the length of each side of the square was 140m). In total 20 small Elliott traps, five large Elliott traps and five wire cage traps were used. Traps were baited with a combination of peanut butter, rolled oats and sardines. Litter was placed inside traps as nesting material, and the wire cage traps were covered with hessian. Traps were opened in the late afternoon, and checked early each morning, before being closed for the day. Traps were freshly baited each afternoon, and were set for four nights. Pitfall trapping methods are described in the section on reptile survey methods above. Ten hairtubes were placed within each trapping site, five on tree trunks and five on the ground. Hairtubes were baited with peanut butter and rolled oats and left in place throughout the survey (three days, four nights). Four movement triggered infrared cameras were placed at each site. Cameras were mounted to a tree, and focussed on a bait station. Bait stations consisted of buried chicken necks (which were wired in to prevent them

being easily removed), and a tea-egg filled with a ball of rolled oats and peanut butter, very shallowly buried, also wired in to prevent it being removed. Cameras were operational from the time they were deployed until the site was closed (three days, four nights). Survey techniques for flying foxes were the same as those used for nocturnal birds. Microbats were surveyed using acoustic bat detectors, in this case SM2 or SM2BAT+ SongMeters (Wildlife Acoustics). One bat detector was deployed at each site, for a period of four nights, and placed in a likely flyway or close to water features such as creeks, pools or dams. For non-flying, captured mammals, information recorded included species, number, sex and breeding condition. Only species identity (or in some cases genus or family) information can be determined from hairtubes and acoustic bat detectors. 2.4.2 Secondary Survey Sites During the late dry season survey two secondary sites were also established to ensure all representative regional ecosystems were included. The survey effort at the two secondary sites is outlined below. Secondary Site 1 was surveyed over four days and four nights with two movement triggered infrared cameras and one Songmeter2 acoustic bat recorder. In addition, one timed bird survey, one diurnal reptile search and two night time spotlight surveys were also conducted. Two spotlight surveys were performed at this site as it was considered suitable habitat for potential Brigalow Belt reptiles. Secondary Site 2 was surveyed over four days and four nights with two movement triggered infrared cameras. In addition one early morning bird survey and one diurnal reptile search was conducted at this site. 2.4.3 Fauna Habitat Assessments Detailed Habitat Assessments Detailed habitat assessments were completed at all five detailed survey sites. In addition, fauna habitat assessments were undertaken at six additional sites. Assessments comprised a mixture of both qualitative and quantitative data on: - landscape description and landform - aspect, elevation, slope and relief class - geology, soil colour and texture - vegetation community/RE, dominant species for each strata and general vegetation description - canopy height - projected cover, percent cover and dominant species for each strata and a variety of ground cover components, including; litter, rocky substrates, cryptogamic crust and bare ground - tree size classes and bark types - percent of trees supporting climbing vines, dieback and mistletoe - abundance of different size classes of logs - abundance, size class and decay stage of dead trees - abundance of hollows of different size classes - weed species abundance and distribution - abundance of termite mounds - fire history - disturbance type and extent - erosion type and extent - connectivity - land use

- animal signs (nests, shelters, diggings, scats, tracks, burrows, tree scratches and feeding scars, any other sign). Where animal signs were observed, the likely species identity was recorded, and in the case of scats or hairs, samples taken for identification. 2.4.4 Incidental Observations Any species recorded opportunistically, that is outside of the formal survey times, within the study area were recorded as incidental observations. 2.4.5 Survey Locations Five detailed fauna sites, two secondary fauna sites and 11 habitat assessment sites were established during the course of this study (Figure 3). Site selection was based on RE mapping (used as an indicator of habitat type), aerial photography and the results of searches of the EPBC and Queensland Museum databases. Limited access, primarily due to mine restrictions on haulage roads, limited the access to some areas within the project which influenced the location of survey sites. 2.4.6 Survey Timing Surveys were undertaken during the early dry season and late dry seasons. Early Dry Season The early dry season survey was conducted April 17 through 21, 2012. The weather was warm with mild nights and only one day with recorded rain (1.4 mm). The average daily low temperature was 12.4°C, and the average maximum daily temperature was 30.7°C. Late Dry Season The late dry season survey was undertaken September 6 through 10, 2012. Mornings were cool and days were mild with no recorded rainfall. The days of September 9 and 10 were exceedingly windy. The average low temperature during the field survey was 6.9°C, and the average maximum daily temperature was 27°C. 2.4.7 Analyses All scats and hair samples collected during the field survey were sent to Barbara Triggs of ‘Dead Finish’ for analyses. Acoustic bat recordings were analysed by Greg Ford of ‘Balance Environmental’. 2.4.8 Threatened Species A number of threatened species records or habitats were identified in the study area in the EPBC and Queensland Museum searches. Of these, referral guidelines containing specific survey guidelines have been developed for northern quolls Dasyurus hallucatus (SEWPAC, 2011b) and threatened Brigalow Belt reptiles (SEWAC, 2011c). Critical habitat for the northern quoll has been defined in the northern quoll referral guidelines (DSEWPC, 2011c) as any habitat within the modelled distribution of the northern quoll where denning and shelter habitat occurs, and may take three forms: - Rocky habitat such as ranges, escarpments, mesas, gorges, breakaways, boulder fields, major drainage lines or treed creek lines - Structurally diverse woodland or forest areas containing large diameter trees, termite mounds or hollow logs. - Off shore islands where the northern quoll is known to exist (DSEWPC, 2011c). Under the northern quoll referral guidelines options are to either undertake extensive survey work in accordance with the Guidelines, or assume that the quoll is present. Given that much of the Project site is modelled as habitat in which the northern quoll is known or likely to occur (SEWPAC, 2011b), there are recent records in close vicinity of the Project site, rather than undertake extensive surveys, it has been assumed that the northern quoll is present within suitable habitat in the Project site. Survey guidelines for the threatened Brigalow Belt reptiles (SEWPAC, 2011c) recommend that surveys should be undertaken from late September through to late March, when weather conditions are warm, not too dry and maximum temperatures exceed 25°C on most survey days. They also recommend the use of multiple techniques for each species, that each technique is used for a minimum of three nights, and that if target species are not detected, at least one replicate survey be undertaken. Surveys were undertaken slightly outside of the recommended period with lower than optimal night time temperatures, however maximum daily temperatures did

exceed 25°C on all days during both surveys considered suitable for detecting reptiles. As it was a late wet season, during the April surveys, there was still standing water in creeks that were surveyed and sites were found to have good green vegetative cover providing potential habitat for amphibian species. These conditions could also potentially result in higher insect abundance providing prey for birds, reptiles and amphibians. Survey techniques did not strictly meet comprehensive guidelines for a small area of the Projects site (< 2% of remnant and regrowth vegetation), due to the lack of replication of two RE’s present. On the basis of these surveys, the presence/absence of threatened Brigalow Belt reptiles in two RES’; 11.3.25 (Eucalyptus tereticornis or E. camaldulensis woodland fringing drainage lines) and 11.10.13 (Eucalyptus spp. and/or Corymbia spp. open forest on scarps and sandstone tablelands) could not be confidently assessed. However, RE 11.3.25 only accounts for 0.8% of the area in the Project site and RE 11.10.13 only 0.5%. Replication was achieved in the two dominant RE’s present on site; RE 11.10.1 and RE 11.9.9 which together account for approximately 50% of the total area in the Project site and 97% of remnant vegetation.

2.5 Assumptions and Limitations It is recognised that information gained from database searches and included in the desktop components of this assessment has caveats attached to it regarding the robustness or completeness of the information. Queensland Museum and Wildlife Online data are based on specimens actually recorded as present in the given locations. The absence of any specimen records for a particular species from an area does not imply that that species does not occur in that area. Data from the SEWPAC’s EPBC Protected Matters Search website are based on a combination of actual records, primarily from State Government databases, combined with modelled distributions of species according to their ecological characteristics. Species and communities identified by this search may occur in the search area, but require further investigation to confirm their presence. Every attempt was made to locate fauna survey sites, particularly detailed sites, within substantial patches of remnant vegetation, and away from the remnant edge, to maximise the probability of detecting rare and cryptic species. Nevertheless restrictions on access to many areas within the mine lease limited the extent to which this could be achieved, and in a number of cases sites were located either within small patches or at the remnant edge, where access could be achieved. Field surveys were limited to the early dry season and late dry season and were not conducted during the wet season when species such as amphibians would have been more readily detected. Dry season surveys were undertaken outside the recommended survey period for threatened Brigalow Belt reptiles. Hence the probability of detecting threatened Brigalow Belt reptiles was reduced. To address this situation, greater emphasis has been placed on habitat assessment, and the identification of suitable habitat for these species. It should be recognised that the surveys undertaken as part of this assessment represent a sample of the Project site’s fauna and should not be considered comprehensive, particularly given the level of site access. For the desktop analysis, it was assumed that species records within 25 km of the Project were highly relevant and those further than 25 km were of limited relevance as many of the EVNT species outside of the 25 km radius were marine species that would not be found in the study area. However, to adhere to the terms of reference (TOR) a full list of species can be found in Appendix A. In addition, EVNT species within the 100 km radius were cross-checked with their distribution and habitat associations to ensure their distribution fell outside of the Project site.

Survey Sites

Figure 3

Legend *#(! Highway )" Local Road

Project Site Site Coordinates

)" Detailed Site 1 (April)

)" Detailed Site 2 (April)

*# )" Detailed Site 3 (March)

)" Detailed Site 4 (March)

)" )" Detailed Site 5 (March)

(! Secondary Site 1 (March) )" (! Secondary Site 2 (March) *# *# Habitat Assessment 1

*# Habitat Assessment 2

(! *# *# Habitat Assessment 3

*# # Habitat Assessment 4 *# )" * *# Habitat Assessment 5

)" *# Habitat Assessment 6

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b l M i Site Locations - AECOM 2012 a K Image - Callide 2012 l li StreetPro © 2010 Pitney Bowes Software Pty Ltd. n e s d Roads, Rivers - © 2010 PSMA Australia Pty Ltd. o i l n l s a AECOM does not warrant the accuracy or completeness of information displayed in this R C map and any person using it does so at their own risk. AECOM shall bear no responsibility d or liability for any errors, faults, defects, or omissions in the information. AECOM Boundary Hill South 18 Terrestrial Fauna Technical Report

3.0 Existing Ecological Environment

3.1 Available Habitat Types Four regional ecosystems (RE’s) are mapped by DEHP in the Project site, all of which have a VMA status of Least Concern (Figure 4, Table 5). However, RE 11.3.25 (Eucalyptus tereticornis or E. camaldulensis woodland fringing drainage lines) has ‘Of Concern’ biodiversity status. Flora surveys conducted by AECOM as part of the broader survey were consistent with the RE’s reported by DEHP, however their distribution in the Project site was found to differ (Figure 5). Eucalypt and bloodwood woodland comprise a large area of the remnant habitat in the Project site. On the eastern side of the Project site, woodland forms a large connected area, dissected only by the primary haul road from the current Boundary Hill mine pit. Continuous tracts of woodland provide important habitat for many species, for example, during field surveys two species of arboreal mammals (squirrel glider Petaurus norfolcensis and greater glider Petauroides volans) were recorded during spotlighting and both of these species were recorded in the eastern area of the project site in continuous woodland. Although woodland also exists in the south western area of the Project site this area does not connect to any other large tracts of woodland. The area in the south west corner of the Project site is mapped by DEHP as regrowth vegetation, however, AECOM mapping has shown the vegetation to be remnant. Habitats along creeks (e.g. RE 11.3.25) are generally regarded as areas of high biodiversity and although this habitat only a covers a small area of the Project site, may provide important habitat for some species. For example, these areas may provide important habitat for the northern quoll in the Project site (AECOM, 2012). In the southern lower area of the Project site, vegetation consists primarily of cleared habitat with scattered trees. This area covers approximately 300 ha (29%) of the Project site. Incidental observations indicate that this habitat is used by grassland species such as eastern grey kangaroo (Macropus giganteus), Australian bustard (Ardeotis australis), crested pigeon (Ocyphaps lophotes), and Australian pipit (Anthus australis). Table 6 below provides a description of fauna habitat features found in the mapped regional ecosystems and pasture (cleared) habitat and their condition in the Project site. The RE’s found on the Project site provide suitable habitat for multiple EVNT species. Table 7 in Section 3.7 provides a description of potential EVNT fauna species and their known habitat associations. Potential species associated with RE’s are listed in Table 8. Two RE’s restricted in distribution that may support a high number of EVNT species include RE 11.3.25 and RE 11.10.13 (see description in Table 5 below). In addition, large connected areas of woodland, such as RE 11.9.9 (Eucalyptus crebra woodland on fine-grained sedimentary rocks) and 11.10.1 (Corymbia citriodora open forest on coarse-grained sedimentary rocks) also provide habitat for a diversity of terrestrial fauna species. Appendix B provides habitat descriptions, resources for fauna (e.g. hollows, logs), and disturbances for all survey sites as well as fauna habitat assessment sites. Mapping illustrates the presence of two Level 1 stream orders within the Project site (Figure 6). Three of the detailed study sites are located in the vicinity of the streams as riparian habitat was considered to have a potentially higher biodiversity values.

Table 5 Regional Ecosystems (and their description) located in the Project site based on DEHP’s RE mapping and their corresponding VMA and Biodiversity status VMA Biodiversity RE Description Long Description status Status 11.3.25 Least Of concern Eucalyptus tereticornis Eucalyptus camaldulensis or E. tereticornis open-forest to woodland. Other tree species such as concern or E. camaldulensis Casuarina cunninghamiana, E. coolabah, Melaleuca bracteata, Melaleuca viminalis, Livistona spp. (in woodland fringing north), Melaleuca spp. and Angophora floribunda are commonly present and may be locally drainage lines dominant. An open to sparse, tall shrub layer is frequently present dominated by species including Acacia salicina, A. Stenophylla or Lysiphyllum carronii. Low shrubs are present, but rarely form a conspicuous layer. The ground layer is open to sparse and dominated by perennial grasses, sedges or forbs such as Imperata cylindrica, Bothriochloa bladhii, B. ewartiana, Chrysopogon fallax, Cyperus dactylotes, C. difformis, C. exaltatus, C. gracilis, C. iria, C. rigidellus, C. victoriensis, Dichanthium sericeum, Leptochloa digitata, Lomandra longifolia or Panicum spp. Occurs on fringing levees and banks of major rivers and drainage lines of alluvial plains throughout the region. Soils are very deep, alluvial, grey and brown cracking clays with or without some texture contrast. 11.9.9 Least No concern at Eucalyptus crebra Eucalyptus crebra grassy woodland. Eucalyptus moluccana sometimes conspicuous on lower slopes. concern present woodland on fine- Occurs on Cainozoic to Proterozoic consolidated, fine-grained sediments grained sedimentary rocks 11.10.1 Least No concern at Corymbia citriodora open Corymbia citriodora predominates and forms a distinct but discontinuous open-forest (to woodland) concern present forest on coarse-grained canopy (20-30m high). On rocky slopes, Eucalyptus crebra and C. hendersonii may be scattered sedimentary rocks throughout the canopy. On flats and footslopes, scattered E. crebra, C. clarksoniana and C. tessellaris may occur. Corymbia trachyphloia and E. cloeziana often occur on crests and plateaus while E. apothalassica and E. longirostrata sometimes occur in moister microhabitats. Scattered tall to low shrubs, such as Acacia leiocalyx, Acacia spp., Bursaria spinosa, Persoonia falcata, Alphitonia excelsa, Petalostigma pubescens and Xanthorrhoea johnsonii are usually present and sometimes form a conspicuous layer. The ground layer varies from sparse to moderately dense (depending on the rockiness) and is dominated by perennial grasses. Occurs on hills and ranges, particularly on colluvial lower slopes, formed from medium to coarse-grained sediments (usually sandstone). 11.10.13 Least No concern at Eucalyptus spp. and/or Open-forest (to woodland) with a range of canopy species including Eucalyptus cloeziana, concern present Corymbia spp. open E. melanoleuca, E. sphaerocarpa, Corymbia bunites, C. hendersonii, C. trachyphloia, E. suffulgens, forest on scarps and C. leichhardtii, C. citriodora, E. baileyana. Occurs on sandstone scarps and tablelands with shallow sandstone tablelands soils formed from medium to course-grained sediments.

Table 6 Fauna habitat features found in the mapped regional ecosystems and pasture (cleared) habitat and their condition in the Project site. VMA Biodiversity Condition of regional ecosystem in RE Description Fauna habitat features status Status the Study site 11.3.25 Least Of concern Eucalyptus Large eucalypt species with hollows provide nesting/denning Evidence of light to moderate grazing, concern tereticornis or E. opportunities or many species (e.g. owls & raptors). Availability of erosion along creek banks. Pest camaldulensis water in pools attracting many species. Dense vegetation along species such as European fox (Vulpes woodland fringing creek beds can act as a movement corridor for species such as the vulpes), rabbit (Oryctolagus cuniculus drainage lines northern quoll. Caves located along the creek (detailed sites 1 & 3) and cats (Felis catus). Dense could provide cover, roosting, denning sites for many species (e.g. concentration of cane toads (Bufo quoll, bats) marinus) in water holes. Noisy miners (Manorina melanocephala) abundant. 11.9.9 Least No concern Eucalyptus crebra Continuous eucalypt woodland provides habitat for a diverse array Evidence of hot fire east of the power concern at present woodland on fine- of species. Dense leaf litter and logs can provide for reptiles and line easement. Light to moderate grained small mammals and larger tree provide foraging opportunities for cattle grazing. Pest species include sedimentary rocks birds and arboreal mammals. Ironbark can provide cover for many pigs, rabbits, dingo/dog (Canis lupus reptile species that seek cover under the bark. sp.). Noisy miners abundant. 11.10.1 Least No concern Corymbia citriodora Continuous eucalypt woodland provides habitat for a diverse array Evidence of hot fire east of the power concern at present open forest on of species. Dense leaf litter and logs can provide for reptiles and line easement. Light to moderate coarse-grained small mammals and larger tree provide foraging opportunities for cattle grazing. Pest species include sedimentary rocks birds and arboreal mammals. Stags provide habitat for bats and pigs (Sus scrofa), dingo/dog. Noisy hollow nesting birds such as owls. miners abundant. 11.10.13 Least No concern Eucalyptus spp. With a dense midstorey level, this habitat provides cover for many Recently burned in NE corner. concern at present and/or Corymbia species such as geckos and skinks. Rocky outcrops and Evidence of light grazing (cattle spp. open forest on associated crevices and overhangs provide roosting opportunity for tracks). Evidence of pest species such scarps and bats, shelter sites for small mammals, and reptiles. In unburnt as the European fox. Very few weeds. sandstone areas, dense leaf litter can provide cover for numerous reptile tablelands species. Non-remnant Extensive grasslands suitable for open grassland species. Open with little canopy cover, pasture Foraging opportunities for raptors, bustards, granivorous birds, introduced grasses, pest species such snakes, and macropods. Nesting habitat for avian species with as foxes, dingo/dog and cats. long grasses available for cover.

\\autsv1fp001\Jobs\MMPL\60238883\6. Draft Docs\6.1 Reports\Rev 02 Issue\Appendices\Appendix P2 - Terrestrial Fauna.docx Revision 01 – 01-Nov-2012 Prepared for – Anglo Coal (Callide Management) Pty Ltd – ABN: 75 009 666 200 BOUNDARY HILL SOUTH LEASE EXPANSION 11.11.5a/11.11.15 (BHSLE)

11.9.4a DERM's Regional Ecosystem

Figure 4 11.10.13/11.10.13/11.10.4

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Highway 11.10.1 11.10.8/11.10.1 Local Road

# Regrowth Watercourse 11.10.8/11.10.1 11.10.1 Project Site 11.10.8/11.10.1 11.9.4a/11.9.5/11.9.1 )" 11.10.1/11.10.1 Essential Habitat 11.9.9 11.9.13/11.10.1 11.9.9 11.9.9/11.9.9 PMVA Category X Area 11.9.9/11.9.9 11.9.13/11.10.1 Regional Ecosystem " 11.10.1/11.10.1 11.10.1/11.9.13 ) Remnant Vegetation Containing # Endangered Regional Ecosystem 11.9.9 11.9.9 11.10.8/11.10.1 Remnant Vegetation Containing of Concern Regional Ecosystem 11.9.13/11.10.1 ! # 11.10.8/11.10.1 Remnant Vegetation that is a # Least Concern Regional Ecosystem 11.9.13/11.10.1 # )" High Value Regrowth 11.9.9 Containing Of Concern Regional Ecosystems 11.10.1 )" Is a Least Concern Regional Ecosystem non-rem

11.9.9 11.10.1

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b l M i Regional Ecosystem - © 2012 The State of Queensland. a K Image supplied by Callide Mine (date unknown). l li StreetPro © 2010 Pitney Bowes Software Pty Ltd. n e s d 11.10.1/11.10.1 Roads, Rivers - © 2010 PSMA Australia Pty Ltd. o i l n l s a AECOM does not warrant the accuracy or completeness of information displayed in this R C map and any person using it does so at their own risk. AECOM shall bear no responsibility d 11.10.1/11.10.1 or liability for any errors, faults, defects, or omissions in the information. BOUNDARY HILL SOUTH LEASE EXPANSION (BHSLE)

AECOM's Regional Ecosystem

Figure 5

! Regrowth # 11-10-1 11-10-13 Legend

)" )" Detailed Site Survey 11-10-1 11-9-9 ! Secondary Site Survey

Regrowth # Habitat Assessment Survey 11-9-9 11-3-25 Highway

# 11-10-1 Local Road

11-10-1 Project Site Regional Ecosystems Regrowth )" 11-10-1 11-10-1

11-10-13

)" 11-3-25 # 11-9-9 11-10-1 Regrowth Regrowth 11-9-9 Regrowth 11-10-1 11-9-9 ! # 11-9-9 Regrowth 11-9-9 11-9-9 # # )" non-remnant 11-9-9 non-remnant 11-9-9 )" Of Concern Regional Ecosystems

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b l M i Regional Ecosystem - © 2012 Vegetation Management Science a K Image supplied by Callide Mine (date unknown). l li StreetPro © 2010 Pitney Bowes Software Pty Ltd. n e s d Roads, Rivers - © 2010 PSMA Australia Pty Ltd. o i l n l s a AECOM does not warrant the accuracy or completeness of information displayed in this R C map and any person using it does so at their own risk. AECOM shall bear no responsibility d or liability for any errors, faults, defects, or omissions in the information. ELL CRE 4 B E 2 1 K 5 1 E K BOUNDARY HILL SOUTH 1 CRE 1 1 K 5 BAC LEASE EXPANSION 5 (BHSLE) 2

2 2 1 1 2 1 2 Watercourse Mapping 1 C LL RE BE E 1 K 4 2 2 Figure 6

1 2

1 1 1

2 1 1 1

1 Legend

)" Detailed Site Survey 1 #! 1 ! Secondary Site Survey

)" 3 # Habitat Assessment Survey 1 2 1 1 Highway 1 2 Local Road 1 # 1 1 )"1 Project Site Watercources with Stream Order 2 1 1 )" 1 Stream Order 1 # 1 2 Stream Order 2 ! # 2 # 3 Stream Order 3 1 # )" 1 )" 4 Stream Order 4 1 5 Stream Order 5

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L K StreetPro © 2010 Pitney Bowes Software Pty Ltd. ) Roads, Rivers - © 2010 PSMA Australia Pty Ltd. e id ll 1 a C AECOM does not warrant the accuracy or completeness of information displayed in this 1 1 2 map and any person using it does so at their own risk. AECOM shall bear no responsibility or liability for any errors, faults, defects, or omissions in the information. AECOM Boundary Hill South 24 Terrestrial Fauna Technical Report

3.2 Essential Habitat No essential habitat for fauna species is mapped by the State within the Project site. An area of mapped essential habitat in the north eastern boundary of the Project represents a threatened flora species.

3.3 Environmentally Sensitive Areas DEHP defines an environmentally sensitive area (ESA) as a location, however large or small, that has environmental values that contribute to maintaining biological diversity and integrity, has intrinsic or attributed scientific, historical, or cultural heritage value, or is important in providing amenity, harmony or sense of community. Environmentally sensitive areas are divided into three categories detailed below. Category A areas that have significant ecological values include national parks, marine parks, conservation parks, forest reserves, the Wet Tropics World Heritage Area and the Great Barrier Reef region. Category B areas include regional ecosystems (REs) with an Endangered biodiversity status (BD status), Ramsar wetlands, State forest parks, wilderness areas, areas seaward of the highest astronomical tide, fish habitat areas and areas containing marine plants. Category C areas typically include REs with an Of Concern biodiversity status, essential habitat, referable wetlands, nature refuges, State forests, timber reserves, declared water catchment areas, koala habitat areas and resources reserves. For the purposes of ESAs, the biodiversity status of the RE is considered, not the status under the Vegetation Management Act 1999. The Project site is affected by a Category C ESA and consists of the Callide Timber Reserve (Figure 7). As a Category C ESA, the Callide Timber Reserve falls under the Forestry Act 1959. Non-standard mining activities (the Project) may occur within these areas after an appropriate level of assessment (e.g. an EIS).

3.4 Bioregional Corridors and Habitat Connectivity The Department of Environment and Resource Management (now EHP) has conducted comprehensive biodiversity planning assessment (BPA) for bioregions within Queensland using the biodiversity assessment and mapping methodology (BAMM, EPA 2002). This methodology provides a consistent approach for assessing biodiversity values at the landscape scale in Queensland. It ranks areas of remnant vegetation into State, regional and local biodiversity significance, using a range of ecological criteria including size, rarity, diversity, fragmentation, habitat condition, resilience, threats, habitat for EVNT species and ecosystem processes. A key output of the BPA is identification and mapping of terrestrial and riparian corridors throughout Queensland. The most recent BPA for the Brigalow Belt Bioregion is version 1.3 (EPA 2008). The BPA classifies corridors into State and regional significance based on criteria including its size and connectivity of vegetation tracts, proximity to major watercourses and presence of EVNT species (DERM 2008). Within the Project, remnant vegetation is mapped as medium State ecosystem diversity, with the exception of one small area of high diversity located in the far south west section (Figure 8a). Larger areas of high biodiversity are located adjacent to the Project. There are no regional corridors mapped, however, the boundary of a mapped State biodiversity corridor is located in the north east of the project site (Figure 8b). The eastern portion of the Project site adjoins an extensive area of State Forest that extends south and connects with Kroombit Tops National Park. Areas of ecological significance (AES) mapped at a State level show high and general AES areas within the Project boundary (Figure 9). Areas of high AES include Callide Timber Reserve and riparian habitat in addition to remnant vegetation. In terms of bioregional corridors based on referable wetlands, the only mapped referable wetland is located north of the Project along Bell Creek (Figure 10).

Environmentally Sensitive Area (ESA)

Figure 7

Legend

)" Detailed Site Survey

! Secondary Site Survey

# # Habitat Assessment Survey

Highway

)" Local Road

Callide Timber Reserve Project Site Catagory B )" Endangered Regional Ecosystem # (Biodiversity Status) Catagory C ! # Timber Reserves # # )" )"

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11.9.4a State Ecosystem Diversity Map

Figure 8a

11.10.13/11.10.13/11.10.4

11.10.13/11.10.13/11.10.4 #! 12.5.1

12.5.1 )" 11.10.8/11.10.1 11.10.1/11.10.1 11.10.1/11.9.13 11.10.1 11.10.1 Legend

)" Detailed Site Survey

11.9.9/11.9.9 11.10.8/11.10.1 ! Secondary Site Survey # # Habitat Assessment Survey 11.10.8/11.10.1 Highway 11.10.1 11.10.1/11.10.1 Local Road 11.10.8/11.10.1 11.9.4a/11.9.5/11.9.1 )" Project Site 11.9.9 11.9.9 11.10.1/11.10.1 11.10.1/11.10.1 State Ecosystem Diversity 11.9.9/11.9.9 11.9.9/11.9.9 11.10.1 11.10.1/11.9.13 11.9.13/11.10.1 )" State Ecosystem Diversity Rating - Low # 11.10.1/11.10.1 State Ecosystem Diversity Rating - Medium 11.9.9 11.10.8/11.10.1 11.9.13/11.10.1 State Ecosystem Diversity Rating - High ! # 11.10.8/11.10.1 # State Ecosystem Diversity Rating - Very High 11.9.13/11.10.1 # )" 11.9.9 )" 11.9.9

11.10.1

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11.10.1 Metres

d R PROJECT ID 60238883 11.9.9 11.9.9

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b l M i BAMM- © 2012 The State of Queensland. a K 11.9.9 Image supplied by Callide Mine (date unknown). l li StreetPro © 2010 Pitney Bowes Software Pty Ltd. n e s 11.10.1/11.10.1 d Roads, Rivers - © 2010 PSMA Australia Pty Ltd. o i l n l s a AECOM does not warrant the accuracy or completeness of information displayed in this R C 11.10.1/11.10.1 map and any person using it does so at their own risk. AECOM shall bear no responsibility d 11.10.1/11.10.1 11.10.1/11.10.1 11.10.13/11.10.13/11.10.4 or liability for any errors, faults, defects, or omissions in the information. BOUNDARY HILL SOUTH LEASE EXPANSION (BHSLE)

Biodiversity Assessment and Mapping Methodology (BAMM)

Figure 8b

#! Legend

)" )" Detailed Site Survey

! Secondary Site Survey

# Habitat Assessment Survey

Highway # Local Road Project Site

Biodiversity Significance

)" State Habitat for EVR taxa

State

)" Regional

# Local or Other Values

Non Bioregion Ecosystem

! # Biodiversity Significance # Criteria J: Corridors # )" Regional

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b l M i Biodiversity Significance- © 2012 The State of Queensland. a K Image supplied by Callide Mine (date unknown). l li StreetPro © 2010 Pitney Bowes Software Pty Ltd. n e s d Roads, Rivers - © 2010 PSMA Australia Pty Ltd. o i l n l s a AECOM does not warrant the accuracy or completeness of information displayed in this R C map and any person using it does so at their own risk. AECOM shall bear no responsibility d or liability for any errors, faults, defects, or omissions in the information. BOUNDARY HILL SOUTH LEASE EXPANSION (BHSLE)

Areas of Ecological Significance

Figure 9

Legend

)" Detailed Site Survey # ! Secondary Site Survey

# Habitat Assessment Survey )" Highway Local Road

Project Site )" # General Ecological Siginificance High Ecological Significance ! # # # )" )"

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b l M i Ecological Significance - © 2012 The State of Queensland. a K Image supplied by Callide Mine (date unknown). l li StreetPro © 2010 Pitney Bowes Software Pty Ltd. n e s d Roads, Rivers - © 2010 PSMA Australia Pty Ltd. o i l n l s a AECOM does not warrant the accuracy or completeness of information displayed in this R C map and any person using it does so at their own risk. AECOM shall bear no responsibility d or liability for any errors, faults, defects, or omissions in the information. ELL CRE B E K K CREE BACK BOUNDARY HILL SOUTH B EL LEASE EXPANSION L CR EK E (BHSLE)

Referable Wetland

Figure 10

#! )" Legend )" Detailed Site Survey

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# # Habitat Assessment Survey )" Highway Local Road )" # Project Site # Wetland Management Area Wetland # ! # )" Wetland Management Area Trigger Area )"

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L a d k I e D n Metres E b O a A C h KY REE C EK K R R E d PROJECT ID 60238883 (O L LAST MODIFIED CFS 5-Oct-2012 D d C R H FILE NAME 60238883_ENV_035 A ie N rn N u Wetlands - © 2012 The State of Queensland. E b il Image - ESRI 2012

L K ) StreetPro © 2010 Pitney Bowes Software Pty Ltd. e id Roads, Rivers - © 2010 PSMA Australia Pty Ltd. ll a C AECOM does not warrant the accuracy or completeness of information displayed in this map and any person using it does so at their own risk. AECOM shall bear no responsibility or liability for any errors, faults, defects, or omissions in the information. AECOM Boundary Hill South 30 Terrestrial Fauna Technical Report

3.5 Species Diversity Desktop searches at the broader regional level (100 km buffer, Appendix A) revealed the presence of 898 species, representing 528 birds, 142 mammals, 189 reptiles and 39 amphibians. Examination of data restricted to the area within 25 km of the Project, revealed records for 395 species, representing 261 species of birds, 48 mammals, 64 reptiles, and 16 amphibians. Difference in the number of taxa between 100 km and 25 km buffers recorded are largely due to the reduced geographic area and lower diversity of habitat represented in the Museum data. Both the WildNet and Museum databases contained a number of marine species such as humpback whales Megaptera novaeangliae and sea snakes Aipysurus sp.. Over both field surveys, a total of 107 species were recorded, of these 68 were bird species, 3 amphibians, 10 reptiles and 26 mammals (Appendix A). An additional five mammal species were possibly present, echolocation calls which could not be reliability identified suggested an additional three microbat species while scats identified the possible presence of two additional mammal species (Appendix D). Based on database records, the current surveys appear to have sampled birds and mammals reasonably however amphibians and reptiles appear to have been under sampled. This may be attributable to the lack survey effort during the height of the wet season (which provides optimal amphibian and reptile survey conditions) and the influence of a recent hot fire that affected habitat east of the power line easement where three of our survey sites were located. Although water was as still present at the two detailed sites surveyed at the beginning of the dry season they consisted of small isolated pools. In addition, without surveys being conducted at the height of the wet season and without any large bodies of water being present the number of wetland birds such as ducks, herons and egrets would also have been low.

3.6 Edge of Range Species No edge of range species were recorded during the field surveys.

3.7 Threatened Fauna Desktop analysis revealed 70 (33 birds, 16 mammals, 18 reptiles and 2 amphibians) EVNT fauna species could potentially occur within the broader region (100 km buffer, see Appendix A). However, some of these species (e.g. dugong Dugong dugon, humpback whale Megaptera novaeangliae, water mouse Xeromys myoides) are marine and/or coastal in distribution and are therefore not relevant to the Project. Analysis within a more relevant 25 km buffer of the Project site identified the potential presence of 31 (14 birds, 9 mammals, and 7 reptiles) EVNT fauna species. An assessment of the likelihood of EVNT species, based on the 25 km buffer, occurring within the Project site was undertaken based on their habitat preferences and distributions. Twenty one species are considered to be either likely or possible to occur within the project site. The likelihood of particular EVNT species occurring in the Project site is presented in Table 7 below. Habitat located in the project site and potential EVNT species that may occur in them is outlined in Table 8. Field surveys confirmed the presence of three threatened species: - Black-chinned honeyeater Melithreptus gularis Near Threatened under the NC Act. - Squatter pigeon Geophaps scripta scripta, Vulnerable under the EPBC Act and the NC Act; - Little pied bat Chalinolobus picatus Near Threatened under the NC Act. The location of the recorded threatened species in the Project site is illustrated in Figure 11. The black-chinned honeyeater (6 individuals) was located at Site 2 during the April survey, the habitat at this site was dominated by ironbark (E. crebra), grey bloodwood (C. clarksoniana) and peppermint (E. exerta) representing RE 11.9.9. Detailed habitat assessment of the site can be found in Appendix B. Large tracts of connected dry eucalypt woodland provides suitable habitat within the Project site. Two squatter pigeons were recorded on Inverness Road, an unsealed road running between the Argoon Kilburnie Road and the haul road from the Boundary Hill mine. Additional suitable habitat is found in the Project site, for example, along the power easement where open grassy areas and other unsealed roads that run though the

Project site used to access various paddocks. Permanent water sources (cattle drinking troughs) provide a year round water supply for this species. The little pied bat was recorded from two locations, Site 3 and 5. The little pied bat is known to roost in both trees and caves although they have been found to roost in abandoned mines and buildings as well. Site 3 and 5 consist of riparian habitat and E. crebra / C. citriodora woodland respectively. Suitable roosting trees are available at both sites. Numerous small caves and rocky overhangs were located along a creek line that runs from east to west in the Project site east of Site 1 (Figure 10). Numerous scats were located within the small caves, predominantly echidna scats, however one scat was determined to potentially be northern quoll. Suitable habitat for this species occurs along this creek line and also potentially in the far north eastern section of the Project site near Secondary Site 1 that consists of rocky outcrops. However, the majority of the rocky outcrops in this area fall outside of the Project site. In addition to the species recorded, the field survey also recovered a scat in a small cave adjacent to Detailed Site 1 (less than one kilometre east of the Project site) that could possibly be attributed to a northern quoll (Dasyurus hallucatus). It should be noted that visually, quoll scats are fairly distinctive and can usually be differentiated from fox or cat scats with a reasonable degree of confidence (Triggs, 2012). The scat was sent for analysis of hair structures by Barabara Triggs of Dead Finish Pty Ltd, however analysis could not positively confirm the scat as quoll as grooming hairs were not present in the sample. On 17 May 2012, a northern quoll was captured at the Callide Power Station by staff (the animal was photographed and taken to a vet for identification, before being released (J. Dunlop pers. comm. 28/04/12)). Callide Power Station staff reported having seen a quoll a number of weeks earlier, as well as regularly observing scats. While the capture site is approximately 12 kilometres from the Project site, it is part of the large block of remnant vegetation adjoining the eastern boundary of the Project site, and is connected to the two creeks running east-west through the Project site. It was in one of these creeks that the putative quoll scat was found. The Project site is also within the northern quoll’s modelled distribution (DSEWPC, 2011c). The site appears to fall on the edge of the ‘known / likely to occur’ and ‘may occur’ areas of the distribution, however the boundaries for these areas are considered indicative only and are not drawn at a scale considered appropriate for local use (DSEWPC, 2011c). The area mapped as ‘known / likely to occur runs south-east from the Project site. It should be noted that another substantial area of remnant vegetation mapped as ‘known / likely to occur’ is found to the north of the Project site, and is the northern extension of the same patch of remnant vegetation adjoining the eastern boundary of the Project site. Habitat suitable for the northern quoll occurs across roughly half of the Project site, approximately 200 hectares of which is considered to be of medium to high suitability (AECOM, 2012c). On this basis it is considered appropriate to assume that the northern quoll occurs on site. Although they were not recorded during this survey, suitable habitat for numerous Brigalow Belt reptiles exists within the Project site (see Table 5 for species habitat associations). The far north east corner consists of brown bloodwood (C. trachyphloia) and ironbark (E. suffulgens) woodland on sandstone upper slopes (RE 11.10.13, Figure 11), where the rocky area would provide suitable habitat for species such as the common death adder (Acanthophis antarcticus), collared delma (Delma torquate), and brigalow scaly foot (Paradelma orientalis). The koala (listed as ‘Vulnerable’ under the EPBC Act) is another species that was not recorded during surveys but may be present within the Project site. Targeted surveys for koalas undertaken as part of this EIS did not confirm the presence of the koala within the Project site. Previous survey at Callide Mine confirmed the presence of the koala adjacent to the Southern operations, south-east of the Project site (Land Reclamation Services, 1998). Field survey identified available koala habitat, including woodland with mature eucalypts (Corymbia citriodora and Eucalyptus crebra), predominantly to the east and north-east of the Project site. There is also potential suitable habitat located in the south-west corner of the Project site but this area is fairly isolated from other suitable habitat unlike the woodland to the east of the Project site. There are no previous records of koala occurring in the Project site; however this species has previously been found near Callide Mine’s Southern operations and Callide Timber Reserve (Melzer & Kindness, 2012; Land Reclamation Services, 1998). Table 7 correlates potential threatened species and REs found in the survey area.

Table 7 Likelihood of endangered, vulnerable and near threatened (EVNT) species occurring in the Project site

Status (EPBC Species Distribution Habitat Requirements Habitat within study area Likelihood Act, NC Act) Birds

Accipiter -, NT Found in coastal and sub-coastal Closed forest, tall wet forest, taller woodland, Within the mapped distribution Possible novaehollandiae areas from northern Australia down timbered watercourses and riparian forest and some suitable riparian and Grey goshawk the eastern coast through to and disturbed areas. Tends to utilize lowland woodland areas. Tasmania. riparian forest during winter. Calyptorhynchus -, V In Queensland this species occurs Found in habitat dominated by she-oaks Within the mapped distribution Unlikely lathami from Gympie and Chinchilla south to Allocasuarina sp.. In SE Queensland it also but no suitable habitat (she- Glossy black- the New South Wales border. inhabits brigalow woodlands and coastal oak) recorded in the Project cockatoo woodlands. site. Ephippiorhynchus -, NT Restricted mainly to coastal and near- Inhabits wetlands, such as floodplains of Within the mapped distribution Possible asiaticus coastal areas of northern and eastern rivers with large shallow swamps and pools, but only smaller habitat area Black-necked Australia. and deeper permanent bodies of water. suitable during the wet season, stork Occasionally individuals will stray into open particularly creeks and one grass, woodland areas or flooded paddocks small ephemeral wetland area in search of food. located in the eastern area of the Project site. Erythrotriorchis V, E A very sparse and discontinuous Red goshawks occupy a range of habitats, Within the mapped distribution Possible radiatus distribution over a wide area - from often at ecotones, including coastal and sub- but the primary habitat is not Red goshawk the Kimberley in Western Australia coastal tall open forest, tropical savannahs present in the Project site. across northern Australia, and down crossed by wooded or forested Possibly in riparian corridors. the east coast of Queensland to watercourses, woodlands, the edges of northern New South Wales. It is rainforest and gallery forests along estimated there are 100 - 200 watercourses, and wetlands that include breeding pairs in Queensland. Melaleuca and Casuarina species. Geophaps scripta V, V The squatter pigeon (southern) Open grassy woodland on sandy soils Within the mapped distribution, Confirmed scripta occurs on the inland slopes of the interspersed with low gravely ridges, in habitat present and confirmed Squatter pigeon Great Dividing Range. The proximity to permanent water. Common on during surveys. Open grassy (southern) distribution extends from the pastoral lands. areas, cleared areas and

Status (EPBC Species Distribution Habitat Requirements Habitat within study area Likelihood Act, NC Act) Burdekin-Lynd divide in central regrowth areas near water Queensland, west to Charleville and sources, dirt tracks and the Longreach, east to the coast from power line easement found in Proserpine to Port Curtis, and south the Project site. to scattered sites in south-eastern Queensland. Lophoictinia isura -, NT This species is found throughout Found in eucalypt forest, heathlands, tropical Within the mapped distribution Likely Square-tailed kite Australia but rarely found more than and subtropical rainforest, and woodlands and suitable habitat (woodlands 250 km from the coast. where passerines, their primary prey, are and riparian corridors) is abundant. present in the Project site. Melithreptus -, NT Found on mainland Australia from the Upper levels of open eucalypt forests and Within the mapped distribution Confirmed gularis Gulf Country of Queensland south to woodlands dominated by box and ironbark and suitable habitat found Black-chinned Cloncurry and is widespread in eucalypts. It is often found along waterways, within the Project site (e.g. honeyeater central and eastern Queensland. especially in arid and semi-arid areas and in E. crebra). northern Australia. Neochmia E, E The star finch (eastern) occurs in This species has been recorded from damp Within the mapped distribution Unlikely ruficauda central Queensland and its population grasslands, sedgelands or grassy woodlands and previously known from the ruficauda is extremely limited. This taxon is near permanent water or areas of regular Rockhampton area. However, Star finch (eastern extinct in New South Wales. The inundation. primary habitat absent and no and southern) most recent records occur in an area recent records of this species. from near Wowan, north to Bowen, west to beyond Winton. Neophema -, NT Found from Cooloola NP and Found in open grassy woodlands coastal Current distribution is outside of Unlikely pulchella Gayndah south to north and eastern heaths, forested hills, pastures and the Project site. Turquoise parrot Victoria. No longer found north of roadsides. Maryborough. Nettapus -,NT Although once found from north Found in freshwater lakes, lagoons, swamps Within the mapped distribution Possible coromandelianus Queensland to the Hunter River in and dams, particularly those vegetated with but only a small area suitable Cotton pygmy- NSW, the cotton pygmy-goose is now waterlilies and other floating and submerged during the dry season in the goose only a rare visitor to NSW. aquatic vegetation. The cotton pygmy-goose form of a dam.

Status (EPBC Species Distribution Habitat Requirements Habitat within study area Likelihood Act, NC Act) Uncommon in Queensland. uses standing dead trees with hollows close to water for roosting and breeding. Poephila cincta E, E This species’ range previously The southern subspecies of the black- Within the broader mapped Possible cincta extended from the Atherton throated finch typically occurs in grassy open distribution and previously Black-throated Tablelands in north Queensland to woodlands and forests dominated by found in the Rockhampton finch the northern Tableland and north- Eucalyptus, Corymbia and Melaleuca, often region. Suitable habitat exists west slope regions of northern New along or near watercourses and occasionally within the Project site. Last South Wales. The species is currently in tussock grasslands or freshwater wetlands recorded in the region in the known from two strongholds in the late 1980’s. Townsville region and from scattered locations throughout central Queensland. Rostratula V, V The Australian painted snipe has a The Australian painted snipe is usually found Within the mapped distribution Possible australis scattered distribution in Australia, in shallow inland wetlands, either freshwater however only a small area of Australian painted primarily occurring along the east or brackish, that are either permanently or habitat for this species is snipe coast from north Queensland to the temporarily filled. located within the Project site. Eyre Peninsula in South Australia, and including the majority of New South Wales and Victoria. Most common in Murray Darling Basin. Tadorna radjah -, NT In Queensland, scarce south of Cape Radjah shelducks occupy terrestrial Within the mapped distribution Unlikely Radjah shelduck York Peninsula and no longer present wetlands, estuaries and the littoral zone of but suitable habitat would only south of Maryborough. monsoonal regions. It nests in tree hollows in be present in a small area the wet season, forming flocks near the during the wet season. coast during the dry season. Turnix V This species has a patchy distribution Restricted to rainforests and forests, mostly Distribution is within the Unlikely melanogaster in SE Queensland south to NE New in areas with 770-1200mm rainfall per mapped distribution but vine Black-breasted South Wales. Fourteen known annum. They prefer drier low closed forests, thicket habitat occurs outside of button-quail populations are known in Queensland particularly semi-evergreen vine thicket, low the Project site. with the two main populations microphyll vine forest and araucarian

Status (EPBC Species Distribution Habitat Requirements Habitat within study area Likelihood Act, NC Act) occurring in Yarraman and the Great notophyll vine forest. They may also be Sandy region. found in low, dense acacia thickets and, in littoral areas, in vegetation behind sand dunes. Mammals

Chalinolobus V, V In Queensland this species occurs in Roosts in caves (near their entrances), Within the mapped distribution Possible dwyeri areas with extensive cliffs and caves crevices in cliffs, old mine workings and in but only a small area of suitable Large-eared pied in the central Queensland sandstone the disused, bottle-shaped mud nests of the roosting habitat exists in the bat belt (Blackdown Tableland inland to fairy martin Hirundo ariel, frequenting low to north eastern section of the Carnarvon National Park) south to mid-elevation dry open forest and woodland Project site and along the Wollongong in New South Wales. close to these features. Found in well- Creek near Site 1. timbered areas containing gullies. Chalinolobus -, NT Coastal and south-eastern In the central and western Darling Downs Suitable habitat exists over a Confirmed picatus Queensland from the Greenvale area of Queensland it has been recorded large area of the Project site Little pied bat region (north of Ingham) to the from Callitris/Allocasuarina dominated such as dry open woodland Maryborough-Childers-Miriam Vale forests with scattered eucalypt emergents with suitable roosting trees area, extending across south-western such as E. dealbata and E. fibrosa. In the (large eucalypts with hollows), Queensland, western New South more arid parts of its range it has been within the known range. Wales and far north-eastern South recorded from mulga Acacia aneura Australia. Roosts in caves, mines and woodlands, from patches of Eucalyptus tree hollows largiflorens woodlands (New South Wales) and riverine E. camaldulensis dominated communities. Dasyurus E, - Reduced to four major geographical Northern quolls do not have highly specific Within the mapped distribution Likely hallucatus centres in Qld: Drummond Range, habitat requirements. They occur in a variety and suitable habitat exists for Northern quoll central Queensland; wet tropics of habitats across their range, including open this species. Open woodland northern Queensland; northern Cape forest and woodland. Daytime den sites with shelter sites such as RE York Peninsula. provide important shelter. Shelter sites are 11.10.13, riparian habitat with also non-specific; rocky outcrops, tree caves such as RE 11.3.25 and hollows, hollow logs, termite mounds, riparian corridors. Known to

Status (EPBC Species Distribution Habitat Requirements Habitat within study area Likelihood Act, NC Act) goanna burrows and human dwellings. occur adjacent to the Project site. Dasyurus E, V The southern subspecies is now This species inhabits vine-forest, rainforest Small area of suitable habitat Unlikely maculatus primarily confined to the Granite Belt and wet and dry sclerophyll forests with a but this species is now only maculatus and Border Ranges, although it still preference for areas that provide suitable known to occur south of the Spotted-tailed occurs in low numbers from Gympie shelter sites such as boulder piles. Project site. quoll south to the New South Wales border. Hipposideros E, V Confined primarily to northern Found in tropical rainforest, monsoon forest, A population in proximity to the Possible semoni Queensland from Townsville north to wet sclerophyll forest and open savannah Project site. The primary Semon’s leaf- Cooktown. A population is also woodland. Daytime roost sites include tree habitat for this species does not nosed bat recorded from Kroombit Tops near hollows, deserted buildings in rainforest, occur in the Project site. Gladstone road culverts and shallow caves amongst However, it is also known to granite boulders or in fissures. occur in eucalypt woodland which is present in the Study site (e.g. E. citriodora, E. crebra, and Corymbia sp.). Nyctophilus V, V Overall, the distribution of the south Inhabits a variety of vegetation types, The Project site is within the Likely corbeni eastern form coincides approximately including mallee, bulloke Allocasuarina distribution for the species. South-eastern with the Murray Darling Basin with the leuhmanni and eucalypt dominated There is available habitat: open long-eared bat Pilliga Scrub region being the distinct communities (including E. crebra). Requires woodland to woodland stronghold for this species. In hollows for roosting. (E. citriodora, E. crebra, and Queensland, the south-eastern long- Corymbia sp.) eared bat is mainly recorded in the Brigalow Belt South Bioregion, extending eastwards to the Bunya Mountains National Park. Petrogale V, V This species occurs from Yarraman in Found in many habitat types, including A very small area of suitable Unlikely penicillata Queensland south to eastern Victoria. rainforest and open eucalypt forest, where habitat is found in the far north Brush-tailed rock- It is patchily distributed throughout its the key habitat component is rock faces with eastern portion of the Project

Status (EPBC Species Distribution Habitat Requirements Habitat within study area Likelihood Act, NC Act) wallaby range. boulders, ledges, and caves much like other site. The distribution of this rock wallabies. species falls outside of the Project site. Phascolarctus V, V In Queensland, scattered populations Inhabits temperate, subtropical and tropical The Project site is within the Likely cinereus occur throughout, occurring in moist eucalypt woodlands and open forest. distribution for the species. Koala forests along the coast, subhumid Although the koala has been known to feed There is available habitat woodlands in southern and central on more than 100 species of eucalypt, it including woodland with mature Queensland and in some eucalypt typically obtains the majority of its nutrition E. citriodora and C. crebra, woodlands along water courses in the from a few species. predominantly in the eastern semiarid environments of the western and north eastern section of the part of the State. Project site. Pteropus V, - This species is found throughout the Inhabits rainforest, eucalypt forest, urban Within the mapped distribution Possible poliocephalus coastal region from Mackay south to and production landscapes. Roosting sites and some foraging habitat is Grey-headed Melbourne. Abundance and usually in dense forest adjacent to water present (riparian) but roosting flying-fox distribution of this species varies bodies, mangrove, Casuarina spp., or sites are not. Primary habitat is greatly dependent on food availability. Melaleuca viridiflora. Roosting sites are absent. usually close to the coast or in areas of lower elevation. Reptiles Acanthophis -, NT Broadly distributed in Queensland This species is found in a wide variety of Within the mapped distribution Likely antarcticus and other States well-drained habitats, including rainforests and suitable habitat exists in Common death and wet sclerophyll forests, woodland, the Project site, especially in adder shrublands, grasslands and coastal the north eastern section. heathlands, preferring sites with deep fixed leaf litter and rocky sites.

Status (EPBC Species Distribution Habitat Requirements Habitat within study area Likelihood Act, NC Act) Delma torquata V, V Appears to have a highly fragmented This species is found in predominantly open Suitable habitat for this species Likely Collared delma distribution with important populations rocky country, such as ridgelines, in exists in the north eastern occurring in the Toowoomba ranges association with dry open eucalypt and/or section of the Project site and it and the western suburbs of Brisbane. acacia woodland. It has also been found in is within the mapped Eucalyptus tereticornis and brigalow distribution. associations with cracking clay soils. Denisonia V, V The species is known from locations The ornamental snake's preferred habitat is Within the mapped distribution Possible maculata within the Brigalow Belt from Taroom within, or close to, habitat that is favoured by but habitat is potentially limited Ornamental snake to Collinsville. its prey - frogs. The species is known to to a small ephemeral wetland prefer woodlands and open forests area. associated with moist areas, particularly gilgai (melon-hole) mounds and depressions in Queensland but also lake margins and wetlands. Egernia rugosa V, V Found from northern Queensland The yakka skink is typically found in open The Project site is within the Likely Yakka skink south to the New South Wales border dry sclerophyll forest or woodland. This skink species mapped distribution with primary population occurring in seeks refuge in dense ground vegetation, in and suitable habitat exists. Dry the Brigalow Belt and Mulga hollow logs, cavities in soil-bound root woodland with potential shelter bioregions. systems and beneath rocks. sites are present over a large area of the Project. Furina dunmalli V, V Occurs in south-east interior of Open forest and woodland, particularly Within the mapped distribution Unlikely Dunmall's snake Queensland, including the Darling brigalow Acacia harpophylla forest and but little or no habitat present Downs, and is thought to potentially woodland growing on floodplains of deep- within the Project site. extend into inland north-eastern cracking black clay and clay loam soils. NSW. Most locality records are between 200 and 500 m elevation. The species is restricted almost entirely to the southern half of the Brigalow Belt bioregion, and its range extends from Yeppoon and the Expedition Range in the north, to

Status (EPBC Species Distribution Habitat Requirements Habitat within study area Likelihood Act, NC Act) Oakey, Glenmorgan and Inglewood in the south. Paradelma V, V This species is endemic to The brigalow scaly foot is found in a wide Within the species distribution Likely orientalis Queensland and occurs mostly in the variety of open forest habitats on several soil and suitable habitat exists Brigalow scaly- Queensland Brigalow Belt bioregion, types. The species often shelters below within the Project site, primarily foot from Inglewood on the southern sandstone slabs, surface debris or amongst in the north eastern section. downs, north to Emerald and east to grass hummocks. Topography varies from Gladstone. sandstone ridges to flats and gently undulating plains with clay, loam or sand. Rheodytes V, V The species is found mostly in the The Fitzroy River turtle is found in rivers with The Project site is within the Unlikely leukops drainage system of the Fitzroy River, large deep pools with rocky, gravelly or modelled distribution but creeks Fitzroy River turtle Queensland. sandy substrates, connected by shallow are ephemeral in nature and riffles. Preferred areas have high water hence no suitable habitat is clarity, and are often associated with present. ribbonweed Vallisneria sp. beds. Strophurus -, NT Found in the Brigalow Belt bioregion Found in dry woodland and open woodland The Project site is within the Likely taenicauda* from Emerald south to northern New habitat in association with Eucalyptus spp., modelled distribution and Golden-tailed South Wales, although most Corymbia spp. and mixed Acacia woodlands. suitable habitat is present. gecko populations are located in the Brigalow Belt South bioregion. Confirmed –recorded during surveys. Likely – large area of available habitat within the study area and within known range. Possible – small area of available habitat within the study area and within or close to known range. Unlikely – no habitat along present or too far away from known range. *Recent studies suggest that Strophurus taenicauda can be divided into three separate subspecies with S.t.triaureus identified as falling within the distribution of the Project site (Brown et al., 2012).

Table 8 Regional ecosystems located in the project site and potentially occurring Endangered, Vulnerable and Near Threatened species. Area RE Description available Potential EVNT species (ha) 11.3.25 Eucalyptus tereticornis or E. 9 Grey goshawk, red goshawk, square-tailed camaldulensis woodland fringing kite, black-chinned honeyeater, black-necked drainage lines stork (wet season), northern quoll, squatter pigeon, south-eastern long-eared bat, yakka skink, brigalow scaly-foot, golden-tailed gecko 11.9.9 Eucalyptus crebra woodland on 240 Grey goshawk, red goshawk, square-tailed fine-grained sedimentary rocks kite, black-chinned honeyeater, northern quoll, koala, south-eastern long-eared bat, golden- tailed gecko 11.10.1 Corymbia citriodora open forest on 296 Square-tailed kite, black-chinned honey-eater, coarse-grained sedimentary rocks northern quoll, south-eastern long-eared bat, golden-tailed gecko

11.10.13 Eucalyptus spp. and/or Corymbia 5 Square-tailed kite, large-eared pied bat, spp. open forest on scarps and brigalow scaly-foot, common death adder, sandstone tablelands yakka skink, collared delma 11.9.9 Eucalyptus crebra woodland on 135 Grey goshawk, red goshawk, square-tailed High value fine-grained sedimentary rocks kite, black-chinned honeyeater, northern quoll, regrowth koala, south-eastern long-eared bat, golden- tailed gecko 11.10.1 Corymbia citriodora open forest on 79 Square-tailed kite, black-chinned honey-eater, High value coarse-grained sedimentary rocks northern quoll, south-eastern long-eared bat, regrowth golden-tailed gecko Non- N/A 305 Squatter pigeon remnant pasture

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Figure 12 Location of caves and rocky outcrops in vicinity of Detailed Site 1

Figure 13 Rocky outcrop and sandstone habitat in north east corner of the Project site

3.8 Migratory Fauna Based on desktop searches, 15 species of migratory fauna are determined to possibly occur within the Project site (see Table 6 below). Based on RE mapping and fauna habitat assessments, it was deemed that suitable habitat for 11 species is present within the Project site. Two migratory species considered to possibly occur are also listed as threatened species; cotton pygmy goose Nettapus coromandelianus albipennis (Near Threatened NC Act) and Australian painted snipe Rostratula australis (Vulnerable NC Act and EPBC Act, the remaining species are all Least Concern). A dam situated in the south west of the Project site may provide a small area of habitat for the cotton pygmy goose, however, the lack of observed aquatic vegetation such as water lilies may reduce the suitability for this species (Figure 12). A small wetland area close to the eastern haul road may provide habitat for Australian painted snipe during the wet season, however, this site was not accessible so conclusive habitat suitability is unknown. Field surveys confirmed the presence of one species; the rainbow bee-eater Merops ornatus. Rainbow bee- eaters are widely distributed in Australia and are found in a wide variety of habitats including forests and woodlands, and in various cleared or semi-cleared habitats, including farmland and areas of human habitation. They usually occur close to water as they commonly nest in the banks of rivers and creeks. The rainbow bee- eater is not listed as threatened under State or Commonwealth legislation.

Figure 14 Dam near Detailed Site 2

Table 9 Habitat and distribution of migratory fauna species that may occur in the Project site. Available habitat within Species Habitat Distribution the study area Anseranas semipalmata Mainly found in shallow wetlands (less than 1 m deep) The magpie goose is still relatively common in the Yes (small wetland area < Magpie goose with dense growth of rushes or sedges. Activities are Australian northern tropics, but had disappeared from 1ha). centred on wetlands, mainly those on floodplains of south-east Australia by 1920 due to drainage and rivers and large shallow wetlands formed by run-off; overgrazing of reed swamps used for breeding. Since breeding can occur in both summer and winter the 1980s there have been an increasing number of dominated rainfall areas and is strongly influenced by records in central and northern NSW. Observed as fly- water level; most breeding now occurs in monsoonal over so occurs in area. areas; nests are formed in trees over deep water; breeding is unlikely in south-eastern NSW. Apus pacificus Aerial forager, rarely alighting. Known to occur above Breeding occurs in Siberia. They arrive in Australia in Yes Fork-tailed swift most habitats. October and stay until March. They are highly mobile in Australia and widespread. Ardea alba Prefer shallow waters and other watered areas Found all over the world and over most of Australia Yes (small wetland area < Great egret including rank grasslands. with the exception of arid areas. 1ha, small dam in southwest corner) Ardea ibis Prefers wetlands and rank grasslands. Occurs over most of Australia with breeding areas in Yes (small wetland area < Cattle egret coastal wetlands or large inland wetlands. 1ha, small dam in southwest corner) Crocodylus porosus In Queensland the salt-water crocodile inhabits reef, The salt-water crocodile is found in Australian coastal No Salt-water crocodile coastal and inland waterways. waters, estuaries, freshwater sections of lakes, inland swamps and marshes. The species' distribution ranges from Rockhampton in Queensland throughout coastal Northern Territory to King Sound (near Broome) in Western Australia. Gallinago hardwickii Within Australia, Latham’s snipe uses a variety of Breeding occurs in the northern hemisphere. Possible (small wetland Latham’s snipe freshwater or brackish wetlands, preferring to be close Commonly recorded through the wetter parts of area < 1 ha) to protective vegetation cover. eastern Australia, including throughout Tasmania and the Bass Strait Islands.

Available habitat within Species Habitat Distribution the study area Haliaeetus leucogaster Breeding records are patchily distributed, mainly along The white-bellied sea-eagle is distributed along the No White-bellied sea eagle the coastline, inland sites are associated with large coastline (including offshore islands) of mainland river systems, e.g. around the Murray, Murrumbidgee Australia and Tasmania. Recorded proximal to and Lachlan Rivers. Nests in large singular trees or Project site where large lake is located. towers. Hirundapus caudacutus In Australia, the white-throated needletail is almost Breeding occurs in Siberia. In eastern Australia, it is Yes White-throated needletail exclusively aerial, from heights of less than 1 m up to recorded in all coastal regions of Queensland and more than 1000 m above the ground, most often NSW, extending inland to the western slopes of the above wooded areas. Great Divide and occasionally onto the adjacent inland plains. Hirundo rustica In Australia, the barn swallow is recorded in open The barn swallow usually occurs in northern Australia, Possible Barn swallow country in coastal lowlands, often near water, towns on Cocos-Keeling Island, Christmas Island, Ashmore and cities. Birds are often sighted perched on Reef, and patchily along the north coast of the overhead wires, and also in or over freshwater mainland from the Pilbara region, Western Australia, wetlands, paperbark Melaleuca woodland, mesophyll to Fraser Island in Queensland. shrub thickets and tussock grassland. It generally nests in buildings. Merops ornatus The rainbow bee-eater occurs mainly in open forests The rainbow bee-eater is distributed across much of Yes (breeding habitat Rainbow bee-eater and woodlands, shrublands, and in various cleared or mainland Australia, and occurs on several near-shore available in riparian semi-cleared habitats, including farmland and areas of islands. habitat) human habitation, located in close proximity to permanent water. Nesting occurs in the banks of rivers, creeks or dams, in roadside cuttings, in the walls of gravel pits or quarries, in mounds of gravel, or in cliff-faces. Monarcha melanopsis Rainforests, sclerophyll forests and woodlands. Open Near coastal from Cape York along the eastern Yes (woodland in Project Black-faced monarch woodland during migration. seaboard to Victoria. site) Monarcha trivirgatus Inhabits rainforest and damp thick forests. Near coastal from Cape York to central New South No Spectacled monarch Wales.

Available habitat within Species Habitat Distribution the study area Myiagra cyanoleuca Inhabit heavily vegetated gullies in eucalypt- In Queensland, it is widespread but scattered. The Yes (taller woodlands in Satin flycatcher dominated forests and taller woodlands. species is more widespread farther south mostly in Project site) coastal areas, but also on the Great Divide, and occasionally further west. Nettapus coromandelianus Freshwater lakes, lagoons, swamps and dams Although once found from north Queensland to the Yes (dam in eastern albipennis particularly those vegetated with waterlilies and other Hunter River in NSW, the cotton pygmy-goose is now section of the Project) Cotton pygmy-goose floating and submerged aquatic vegetation. The only a rare visitor to NSW. Uncommon in Queensland. cotton pygmy-goose uses standing dead trees with hollows close to water for roosting and breeding. Rostratula australis The Australian painted snipe is usually found in The painted snipe has a scattered distribution in Yes (small wetland area < Australian painted snipe shallow inland wetlands, either freshwater or brackish, Australia, primarily occurring along the east coast from 1 ha) that are either permanently or temporarily filled. north Queensland to the Eyre Peninsula in South Australia, and including the majority of New South Wales and Victoria. Most common in Murray Darling Basin.

3.9 Breeding Sites No rookeries or other significant breeding sites were identified in the Project site by desktop analyses. However, two areas that could potentially be used as breeding sites for numerous species were identified during field surveys. One area encompasses the creek running through both Detailed Site 1 and 3. Numerous small caves and overhangs are present in this area providing potential den sites for quolls (see Figure 12). In addition, it is also possible that these caves and overhangs are used by other species such as bats. Potential roosting and den sites are also found on the north eastern boundary of the project site. This area has numerous small rocky crevices and overhangs that could be used by species such as the northern quoll and microbats (Figure 13).

3.10 Culturally Significant Fauna There are two species that may or do occur in the Project site that may not be threatened, but are significant due to their inherent value and potential importance for the maintenance of ecosystem processes or they are considered a source of genetic information integral to an understanding of the evolution of the Australian biota and a genetic resource of potential benefit to society. Echidnas Tachyglossus aculeatus although listed as ‘Special Least Concern’ wildlife under the NC Act were recorded in two locations in the Project site, one was captured at detailed Site 5 and one was recorded at night foraging in the vicinity of Site 1 (Figure 13). Evidence of the presence of this species, scats and digging, was recorded in multiple locations in the Project site suggesting this species is widespread. Koalas were not recorded during field surveys; however examination of the WildNet database revealed koala records throughout much of broader region. Suitable habitat for this species is present in the Project site and is discussed in section 3.7.

Figure 15 Echidna (Trachyglossus aculeatus) located in trap at Detailed Site 5

3.11 Introduced Pest Species Pest animals are of concern because they have, or potentially have, detrimental effects on ecological values. Landowners have a responsibility under the Land Protection (Pest and Stock Route Management) Act 2002 to control declared pests (see section 1.4.3). The Commonwealth Government (SEWPAC) also recognises the following pests as a ‘key threatening process’ related to their impacts on biodiversity through predation, competition, land degradation and poisoning: - Rabbits; - European fox; - Feral cat; - Pigs; and - Cane toad. Six introduced species, not including domestic animals, were recorded during field surveys (see Table 10 below), of which five are considered as a key threatening process. Cane toads were widespread within the Project site, taking up a significant number of sheltering resources and food resources. In areas where water was available (Detailed Sites 1, 2 and 3) they were abundant and found to congregate in very large numbers in small water pools. Ingestion of cane toads (including eggs and tadpoles) resulting in poisoning is the primary effect of cane toads on native species such as the northern quoll (Hill and Ward, 2010; Shine, 2010). There is also evidence of cane toads affecting the growth rate of native tadpoles and even reducing rainbow bee-eater nesting success by nest usurpation (Boland, 2004; Williamson, 1999). Wild dogs Canis and/or dingoes were recorded throughout the Project site through both scats, tracks and through motion cameras at Detailed Sites 2 and 3. It is often difficult to distinguish between wild dogs and dingos, mainly due to interbreeding and genetic testing is required to definitely distinguish between them. Cats were not located on remote cameras or seen by field personnel but tracks were located at Detailed Site 3. Cats are listed as a key threatening process by SEWPAC, primarily through predation on species such as birds and reptiles. The European fox was recorded by infrared cameras at three sites, indicating it is widespread in the Project site (Figure 16). The impact of foxes on native Australian fauna has been widely documented especially during predator exclusion experiments with threatened native mammals (Dickman,1996). Foxes are known to predate on many vertebrates, but have been shown to heavily impact populations of small to medium size mammals such as rock-wallabies Petrogale spp. One pig was recorded in the north east section of the Project with scats also recorded at Detailed Site 4. It is likely this species is present throughout the Project site.

Table 10 Introduced pest species, status and location recorded during surveys. Scientific Name Common Name LP Act Status Location of Record Bufo marinus Cane toad Not declared Detailed Sites 2,3 & 4 Canis lupus Dingo/dog Class 2 Detailed Sites 2 & 3 dingo/familiaris Felis catus Cat Class 2 Detailed Site 3, incidental Oryctolagus cuniculus Rabbit Class 2 Detailed Site 3 & Secondary Site 2, incidental Sus scrofa Pig Class 2 Detailed Site 4, incidental Vulpes vulpes European fox Class 2 Detailed Site 1 & 3, Secondary Site 1

Figure 16 European fox Vulpes vulpes recorded at Secondary Site 1

4.0 Conclusions and Recommendations The primary impact of the Project will be the clearing, fragmentation and modification of existing habitat. The Brigalow Belt Bioregion has already experienced some of the highest rates of clearing in Queensland resulting in the loss of a vast area of remnant vegetation (Cogger et al., 2003). Long term monitoring of vertebrate fauna in central Queensland suggest a decline in woodland species and an increase in more generalist species (Woinarski et al., 2006). Loss of habitat is only likely to be locally significant in areas of the Project site that include remnant eucalypt and bloodwood woodlands, fringing riparian woodlands, freshwater wetlands and woodland on sandstone. Efforts should be made to limit the impact on these habitat types. Non-remnant habitat covers a significant portion of the Project site and impacts will be reduced in these areas. Although grassland species such as the eastern grey kangaroo are abundant in this area the only EVNT species likely to be present is the squatter pigeon. Although clearing of this habitat will have an impact on grassland species, the highly modified nature of this habitat (e.g. pest species and introduced buffel grass) suggest they will be minimal in a broad scale context. Fragmentation of connected woodland and riparian corridors may have flow on effects on population dynamics, population sustainability and gene flow. Species likely to be particularly sensitive include arboreal mammals, such as the greater glider and squirrel glider, and reptiles (including the threatened Brigalow Belt reptiles), and to a lesser extent small ground-dwelling mammals and small understorey birds. The eastern and north eastern portion of the Project is connected to an extensive area of woodland to the east of the Project and the preservation of connectivity should be a key consideration. The nationally threatened Brigalow Belt reptiles are likely to be associated with the north, east and west areas of the Project. Areas that are already cleared have fewer sheltering sites in the form of logs and these areas would have a lower value for these species. Particular effort should be taken to ensure that significant high quality habitat suitable for these species, i.e. riparian habitat and habitat in the north eastern portion of the Project, is not impacted on, and that connectivity with other patches is not compromised. Research by Driscoll (2004) indicates that the result of fragmentation on reptiles is dependent on ‘dispersal powers or small effective population sizes’. For many threatened Brigalow belt reptile populations that have already experienced a high degree of habitat fragmentation and have small population sizes increased clearing will have a negative impact on their population. For birds, clearing and fragmentation can lead to a decline in species richness (e.g. Hannah et al., 2007). An indirect impact of fragmentation is the potential increase of the hyper-aggressive noisy miner that has shown to have negative effects on small passerines in eastern Australia (e.g. Eyre et al., 2009). The abundance of noisy miners has been shown to be higher in intensely grazed woodland and areas with high road density (Eyre et al., 2009). With increased flows of heavy vehicle travelling around the Project consideration should be given to the installation of fauna underpasses in areas where habitat connectivity will be compromised and wildlife mortality will be highest. Previous research has shown that both underpasses and over passes are used by a variety of species, particularly small mammals but also lizards (e.g. Bond and Jones, 2008; Taylor and Goldinay, 2003). In addition, exclusion fencing has been shown to reduce mortality on roads, especially for larger species (e.g. Bond and Jones, 2008). Wildlife barriers should also be considered in areas where potential EVNT species are likely to suffer road or construction mortality, for example in riparian areas that may be used as habitat corridors by some species (e.g. northern quoll). Road mortality records can be used to identify ‘hot spots’ where barriers and/or underpasses would be valuable in reducing fauna mortality. Detailed mitigation measures for fauna are beyond the scope of this technical report but are addressed for the design, construction and operational phases of the Project in the terrestrial ecology chapter of the EIS.

5.0 References AECOM. 2012. Boundary Hill Lease Expansion Project; Quoll Surveys – December 2011. Report prepared for Anglo Coal (Callide Management) Pty. Boland, C.R.J. 2004. Introduced Cane Toads Bufo marinus are active nest predators and competitors of Rainbow Bee-eaters Merops ornatus: observational and experimental evidence. Biological Conservation. 120:53-62. Bond, A.R and Jones, N.J. 2008. Temporal trends in use of fauna-friendly underpasses and overpasses. 2008. Wildlife Research 35:103-112. Brown, D., J. Worthington Wilmer, and Macdonald, S. 2012. A revision of Strophurus taenicauda (Squamata; Diplodactylidae) with the description of two new subspecies from central Queensland and a southerly range extension. Zootaxa 3243:1-28. Churchill, S. 2008. Australian Bats. Second edition. Jacana Books, Crows Nest. Clayton, M, J.C. Wombey, I.J. Mason, R.T. Chesser, and Wells, A.B.. (2007). CSIRO list of Australian vertebrates. A reference with conservation status. CSIRO Collingwood. Cogger, H.G., H. Ford, C. Johnson, J. Holman and Butler, D. 2003. Impacts of land clearing on Australian wildlife in Queensland. Report for WWF, Australia. Cogger, H.G. 2000. Reptiles and amphibians of Australia. Reed Books: Sydney. Curtis, Lee K., A. J. Dennis, K. R. McDonald, P. M. Kyne, and Debus S.J.S., Eds. 2012. Queensland’s Threatened Animals. CSIRO Publishing, Collingswood. Department of Environment and Climate Change (DECC). 2011. Threatened Species database SPRAT. Department of Environment & Resource Management (DERM). 2011. WildNet – flora and fauna database. Accessed March 2012 . Department of Environment & Resource Management (DERM). 2009. Wetland Info – Species Information. Accessed March 2012 Department of Sustainability Environment Water Population and Communities (SEWPAC). 2009. Matters of National Environmental Significance – Significant Impact Guidelines 1.1, Environment Protection and Biodiversity Act 1999. Australian Government, Canberra. Department of Sustainability Environment Water Population and Communities (SEWPAC). 2011a. Approved Conservation Advice for various species. Accessed March 2012. Department of Sustainability Environment Water Population and Communities (SEWPAC). 2011b. EPBC Act 1999 referral guidelines for the endangered northern quoll, Dasyurus hallucatus. EPBC Policy Statement 3.25. Australian Government, Canberra. Department of Sustainability Environment Water Population and Communities (SEWPAC). 2011c. EPBC Act 1999 draft referral guidelines for the nationally listed Brigalow Belt reptiles. Australian Government, Canberra. Dickman, C. R. 1996. Impact of exotic generalist predators on the native fauna of Australia. Wildlife Biology 2(3):185-195. Driscoll, D.A. 2004. Extinction and outbreaks accompany fragmentation of a reptile community. Ecological Applications 14(1):220-240. Environment Australia. 1999. Action Plan for Australian Bats. Department of Sustainability Environment Water Population and Communities (SEWPAC), Canberra. Eyre, T.J., M. Maron, M.T. Mathieson and Haseler, M. 2009. Impacts of grazing, selective logging and hyper- aggressors on diurnal bird fauna in intact forest landscapes of the Brigalow Belt, Queensland. Austral Ecology 34:705-716. Hannah, D., J.C.Z. Woinarski, C.P. Catterall, J.C. McCosker, N.Y. Thurgate, and Fensham, R.J. 2007. Impacts of clearing, fragmentation and disturbance on the bird fauna of eucalypt savannah woodlands in central Queensland, Australia. Austral Ecology 32:261-276.

Hill B.M. and Ward S.J. 2010. National Recovery Plan for the Northern Quoll Dasyurus hallucatus. Department of Natural Resources, Environment, the Arts and Sport, Darwin. Legge, S., S. Murphy, J. Heathcote, E. Flaxman, J. Augusteyn, and Crossman, M. 2008. The short-term effects of an intensive and high-intensity fire on vertebrates in the tropical savannas of the central Kimberley, northern Australia. Wildlife Research 35:33-43. Menkhorst, P. and Knight F. 2011. A Field Guide to the Mammals of Australia. Oxford University Press, Sydney. Pizzey, G. And Knight F. 2007. The Field Guide to the Birds of Australia. P. Menkhorst, editor. Eighth edition. Harper Collins, Sydney. Richardson, R. 2006. Queensland Brigalow Belt Reptile Recovery Plan 2008-2012. Report to the Department of the Environment, Water, Heritage and Arts, Canberra. WWF-Australia, Brisbane. Ryan, S. 2006. Red Goshawk – Conservation Management Profile. Environment Protection Agency (EPA), Queensland. Shine, R. 2010. The ecological impact of invasive cane toads (Bufo marinus) in Australia. Quarterly Review of Biology 85(3):253-291. Strahan, R. (ed.) 1995. The Mammals of Australia. Reed, Sydney. Taylor, B.D. and Goldinay, R.L. 2003. Cutting the carnage: wildlife usage of road culverts in north-eastern New South Wales. Wildlife Research 30:529-537. Queensland Museum. 2012. Museum records accessed August 2012. Wilson, S. And Swan, G. 2010. A Complete Guide to the Reptiles of Australia. 2010. New Holland,Sydney. Williamson, I. 1999. Competition between the larvae of the introduced cane toad Bufo marinus (Anura: Bufonidae) and native anurans from the Darling Downs area of southern Queensland. Australian Journal of Ecology 24:636- 643. Woinarski, J.C.Z, J.C. McCosker, G. Gordon, B. Lawrie, C. james, J. Augusteyn, L. Slater and Danvers, T. 2006. Monitoring change in the vertebrate fauna of central Queensland, Australia, over a period of broad-scale vegetation clearance, 1973-2002. Wildlife Research 33:263-274.

Appendix A

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

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

0SX4PER )WXEXI2EQI )WXEXI8]TI )WXEXI8IRYVI %VIE LE 3PH7XEXI))0 +E^IXXIIV(EXI 74 1SYRX0EVGSQ 03 70 +0%(7832) 2YPP 4VSTSWIH2EXMSREP 4EVO *8= 7GVYFF]1SYRXEMR 7* 7* +0%(7832) 7XEXI*SVIWX *8= 8EVKMRMI7XEXI*SVIWX 7* 7* +0%(7832) *8= (IKEPKMP7XEXI*SVIWX 7* 7* *8= (IKEPKMP7XEXI*SVIWX 7* 7* *8= ;MIXEPEFE7XEXI 7* 7* +0%(7832) *SVIWX *8= 1SYRX1EYVMGI7XEXI 7* 7* +0%(7832) *SVIWX *8= 1SYRX1EYVMGI7XEXI 7* 7* +0%(7832) *SVIWX *8= 'YVXMW-WPERH7XEXI 7* 7* +0%(7832) *SVIWX 24; 'YVXMW-WPERH2EXMSREP 24 24 +0%(7832) 4EVO 24; (E[IW2EXMSREP4EVO 24 24 +0%(7832) *8= ;MIXEPEFE7XEXI 7* 7* +0%(7832) *SVIWX 24; &YPFYVMR2EXMSREP 24 24 +0%(7832) 4EVO 74 'EWXPI8S[IV2EXMSREP 24 24 +0%(7832) 4EVO 24; ;MPH'EXXPI-WPERH 24 24 +0%(7832) 2EXMSREP4EVO 24; ;MPH'EXXPI-WPERH 24 24 +0%(7832) 2EXMSREP4EVO

;EXIV6IWSYVGI4PER&SYRHEVMIW

2EQI *MX^VS] 'EPPMSTI &S]RI &EJJPI &YVRIXX

6IKMSREP'SEWXEP4PERW

'SHI 6IKMSR GEG 'ETVMGSVR'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GEG 'ETVMGSVR'SEWX GEG 'ETVMGSVR'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GEG 'ETVMGSVR'SEWX GEG 'ETVMGSVR'SEWX GEG 'ETVMGSVR'SEWX GYG 'YVXMW'SEWX

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

'SHI 6IKMSR GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GEG 'ETVMGSVR'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX GYG 'YVXMW'SEWX

&MSVIKMSRW

6IKMSR2EQI 7)5 7)5 7)5 7)5 &6& &6& 7)5 7)5 &6& 7)5 7)5 7)5 7)5 &6& &6& 7)5 7)5 7)5 7)5 7)5 7)5 &6& &6& &6& &6& 7)5

*EYRE7TIGMIW0MWX

/MRKHSQ 'PEWW *EQMP] 7GMIRXMJMG2EQI 'SQQSR2EQI - 2'% )4&' 2S 0EWX7IIR %RMQEPME -RGIVXEIWIHMW -RHIXIVQMREXI -RHIXIVQMREXI 9RORS[RSV'SHI4IRHMRK 2 ' %RMQEPME 1EQQEPME &SZMHEI &SWWT GEXXPI - %RMQEPME 1EQQEPME &SZMHEI &SWXEYVYW )YVSTIERGEXXPI -

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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

%RMQEPME 1EQQEPME 4XIVSTSHMHEI 2]GXMQIRIVSFMRWSRM IEWXIVRXYFIRSWIHFEX 2 ' %RMQEPME 1EQQEPME 4XIVSTSHMHEI 4XIVSTYWEPIGXS FPEGOJP]MRKJS\ 2 ' %RMQEPME 1EQQEPME 4XIVSTSHMHEI 4XIVSTYWTSPMSGITLEPYW KVI]LIEHIHJP]MRKJS\ 2 ' : %RMQEPME 1EQQEPME 4XIVSTSHMHEI 4XIVSTYWWGETYPEXYW PMXXPIVIHJP]MRKJS\ 2 ' %RMQEPME 1EQQEPME 4XIVSTSHMHEI 4XIVSTYWWT 2 %RMQEPME 1EQQEPME 4XIVSTSHMHEI 7]GSR]GXIVMWEYWXVEPMW IEWXIVRFPSWWSQFEX 2 ' %RMQEPME 1EQQEPME 1EGVSTSHMHEI 1EGVSTYWEKMPMW EKMPI[EPPEF] 2 ' %RMQEPME 1EQQEPME 1EGVSTSHMHEI 1EGVSTYWHSVWEPMW FPEGOWXVMTIH[EPPEF] 2 ' %RMQEPME 1EQQEPME 1EGVSTSHMHEI 1EGVSTYWKMKERXIYW IEWXIVRKVI]OERKEVSS 2 ' %RMQEPME 1EQQEPME 1EGVSTSHMHEI 1EGVSTYWTEVV]M [LMTXEMP[EPPEF] 2 ' %RMQEPME 1EQQEPME 1EGVSTSHMHEI 1EGVSTYWVSFYWXYW GSQQSR[EPPEVSS 2 ' %RMQEPME 1EQQEPME 1EGVSTSHMHEI 1EGVSTYWVYJSKVMWIYW VIHRIGOIH[EPPEF] 2 ' %RMQEPME 1EQQEPME 1EGVSTSHMHEI 1EGVSTYWWT 2 %RMQEPME 1EQQEPME 1EGVSTSHMHEI 3R]GLSKEPIEJVEIREXE FVMHPIHREMPXEMP[EPPEF] 2 ) ) %RMQEPME 1EQQEPME 1EGVSTSHMHEI 4IXVSKEPILIVFIVXM ,IVFIVX WVSGO[EPPEF] 2 ' %RMQEPME 1EQQEPME 1EGVSTSHMHEI 4IXVSKEPIMRSVREXE YREHSVRIHVSGO[EPPEF] 2 ' %RMQEPME 1EQQEPME 1EGVSTSHMHEI 4IXVSKEPITIRMGMPPEXE FVYWLXEMPIHVSGO[EPPEF] 2 : : %RMQEPME 1EQQEPME 1EGVSTSHMHEI 8L]PSKEPIWXMKQEXMGE VIHPIKKIHTEHIQIPSR 2 ' %RMQEPME 1EQQEPME 1EGVSTSHMHEI 8L]PSKEPIXLIXMW VIHRIGOIHTEHIQIPSR 2 ' %RMQEPME 1EQQEPME 1EGVSTSHMHEI ;EPPEFMEFMGSPSV W[EQT[EPPEF] 2 ' %RMQEPME 1EQQEPME 4SXSVSMHEI %IT]TV]QRYWVYJIWGIRW VYJSYWFIXXSRK 2 ' %RMQEPME 1EQQEPME 4LEPERKIVMHEI 8VMGLSWYVYWGERMRYW WLSVXIEVIHTSWWYQ 2 ' %RMQEPME 1EQQEPME 4LEPERKIVMHEI 8VMGLSWYVYWWT 2 %RMQEPME 1EQQEPME 4LEPERKIVMHEI 8VMGLSWYVYWZYPTIGYPE GSQQSRFVYWLXEMPTSWWYQ 2 ' %RMQEPME 1EQQEPME %GVSFEXMHEI %GVSFEXIWT]KQEIYW JIEXLIVXEMPKPMHIV 2 ' %RMQEPME 1EQQEPME 4WIYHSGLIMVMHEI 4IXEYVSMHIWZSPERW KVIEXIVKPMHIV 2 '

%RMQEPME 1EQQEPME 4WIYHSGLIMVMHEI 4WIYHSGLIMVYWTIVIKVMRYW GSQQSRVMRKXEMPTSWWYQ 2 '

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

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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%RMQEPME %ZIW 4LEPEGVSGSVEGMHEI 4LEPEGVSGSVE\WYPGMVSWXVMW PMXXPIFPEGOGSVQSVERX 2 '

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

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

/MRKHSQ 'PEWW *EQMP] 7GMIRXMJMG2EQI 'SQQSR2EQI - 2'% )4&' 2S 0EWX7IIR %RMQEPME 6ITXMPME 7GMRGMHEI 'XIRSXYWWT 2 %RMQEPME 6ITXMPME 7GMRGMHEI 'XIRSXYWXEIRMSPEXYW GSTTIVXEMPIHWOMRO 2 ' %RMQEPME 6ITXMPME 7GMRGMHEI ']GPSHSQSVTLYWKIVVEVHMM TMROXSRKYIHPMÊ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ÊVH 2 ' %RMQEPME 6ITXMPME :EVERMHEI :EVERYWKSYPHMM WERHQSRMXSV 2 ' %RMQEPME 6ITXMPME :EVERMHEI :EVERYWTERSTXIW ]IPPS[WTSXXIHQSRMXSV 2 ' %RMQEPME 6ITXMPME :EVERMHEI :EVERYWWIQMVIQI\ VYWX]QSRMXSV 2 ' %RMQEPME 6ITXMPME :EVERMHEI :EVERYWXVMWXMW FPEGOXEMPIHQSRMXSV 2 ' %RMQEPME 6ITXMPME :EVERMHEI :EVERYWZEVMYW PEGIQSRMXSV 2 ' %RMQEPME 6ITXMPME %KEQMHEI %QTLMFSPYVYWQYVMGEXYW NEGO]PMÊVH 2 ' %RMQEPME 6ITXMPME %KEQMHEI 'LPEQ]HSWEYVYWOMRKMM JVMPPIHPMÊVH 2 ' %RMQEPME 6ITXMPME %KEQMHEI (MTSVMTLSVEEYWXVEPMW 2 ' %RMQEPME 6ITXMPME %KEQMHEI (MTSVMTLSVEFMPMRIEXE X[SPMRIHHVEKSR 2 ' %RMQEPME 6ITXMPME %KEQMHEI (MTSVMTLSVERSFFM RSFFM 2 ' %RMQEPME 6ITXMPME %KEQMHEI (MTSVMTLSVEWT 2 %RMQEPME 6ITXMPME %KEQMHEI -RXIPPEKEQEPIWYIYVMM IEWXIVR[EXIVHVEKSR 2 ' %RMQEPME 6ITXMPME %KEQMHEI 4SKSREFEVFEXE FIEVHIHHVEKSR 2 ' %RMQEPME 6ITXMPME 4]KSTSHMHEI (IPQEMRSVREXE 2 ' %RMQEPME 6ITXMPME 4]KSTSHMHEI (IPQEXMRGXE 2 ' %RMQEPME 6ITXMPME 4]KSTSHMHEI (IPQEXSVUYEXE GSPPEVIHHIPQE 2 : : %RMQEPME 6ITXMPME 4]KSTSHMHEI 0MEPMWFYVXSRMW &YVXSR WPIKPIWWPMÊVH 2 ' %RMQEPME 6ITXMPME 4]KSTSHMHEI 4EVEHIPQESVMIRXEPMW FVMKEPS[WGEP]JSSX 2 : : %RMQEPME 6ITXMPME 4]KSTSHMHEI 4]KSTYWRMKVMGITW LSSHIHWGEP]JSSX 2 ' %RMQEPME 6ITXMPME 4]KSTSHMHEI 4]KSTYWWGLVEHIVM 2 ' %RMQEPME 6ITXMPME 'EVTLSHEGX]PMHEI 2ITLVYVYWEWTIV WTMR]ORSFXEMPIHKIGOS 2 '

%RMQEPME 6ITXMPME 'EVTLSHEGX]PMHEI 7EPXYEVMYWWEPIFVSWYW VSYKLXLVSEXIHPIEJXEMPIH 2 ' KIGOS

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

/MRKHSQ 'PEWW *EQMP] 7GMIRXMJMG2EQI 'SQQSR2EQI - 2'% )4&' 2S 0EWX7IIR %RMQEPME 6ITXMPME 'EVTLSHEGX]PMHEI 9RHIV[SSHMWEYVYWQMPMM 2 '

%RMQEPME 6ITXMPME (MTPSHEGX]PMHEI %QSPSWMEPIWYIYVMM 0IWYIYV WZIPZIXKIGOS 2 ' %RMQEPME 6ITXMPME (MTPSHEGX]PMHEI %QSPSWMEVLSQFMJIV ^MK^EKKIGOS 2 ' %RMQEPME 6ITXMPME (MTPSHEGX]PMHEI (MTPSHEGX]PYWZMXXEXYW [SSHKIGOS 2 ' %RMQEPME 6ITXMPME (MTPSHEGX]PMHEI 0YGEWMYQWXIMRHEGLRIVM 7XIMRHEGLRIV WKIGOS 2 ' %RMQEPME 6ITXMPME (MTPSHEGX]PMHEI 2IFYPMJIVEVSFYWXE VSFYWXZIPZIXKIGOS 2 ' %RMQEPME 6ITXMPME (MTPSHEGX]PMHEI 3IHYVEQSRMPMW 2 ' %RMQEPME 6ITXMPME (MTPSHEGX]PMHEI 3IHYVEWT 2 %RMQEPME 6ITXMPME (MTPSHEGX]PMHEI 3IHYVEXV]SRM WSYXLIVRWTSXXIHZIPZIX 2 ' KIGOS %RMQEPME 6ITXMPME (MTPSHEGX]PMHEI 7XVSTLYVYWXEIRMGEYHE KSPHIRXEMPIHKIGOS 2 28 %RMQEPME 6ITXMPME (MTPSHEGX]PMHEI 7XVSTLYVYW[MPPMEQWM WSJXWTMRIHKIGOS 2 ' %RMQEPME 6ITXMPME +IOOSRMHEI +IL]VEGEXIREXE 2 ' %RMQEPME 6ITXMPME +IOOSRMHEI +IL]VEHYFME 2 ' %RMQEPME 6ITXMPME +IOOSRMHEI +IL]VEWT 2 %RMQEPME 6ITXMPME +IOOSRMHEI ,IQMHEGX]PYWJVIREXYW LSYWIKIGOS - %RMQEPME 6ITXMPME +IOOSRMHEI ,IXIVSRSXMEFMRSIM &]RSI WKIGOS 2 ' %RMQEPME 6ITXMPME 'LIPMHEI 'LIPSHMREI\TERWE FVSEHWLIPPIHVMZIVXYVXPI 2 ' %RMQEPME 6ITXMPME 'LIPMHEI 'LIPSHMREPSRKMGSPPMW IEWXIVRWREOIRIGOIHXYVXPI 2 ' %RMQEPME 6ITXMPME 'LIPMHEI )PWI]EEPFEKYPE WSYXLIVRWRETTMRKXYVXPI 2 ' %RMQEPME 6ITXMPME 'LIPMHEI )PWI]EWT 2 %RMQEPME 6ITXMPME 'LIPMHEI )Q]HYVEQEGUYEVMMOVIJJXMM /VIJJX WVMZIVXYVXPI 2 ' %RMQEPME 6ITXMPME 'LIPMHEI )Q]HYVEWT 2 %RMQEPME 6ITXMPME 'LIPMHEI 6LISH]XIWPIYOSTW *MX^VS]6MZIVXYVXPI 2 : : %RMQEPME 6ITXMPME 'LIPMHEI ;SPPYQFMRMEPEXMWXIVRYQ WE[WLIPPIHXYVXPI 2 ' %RMQEPME 6ITXMPME 'LIPSRMMHEI 'EVIXXEGEVIXXE PSKKIVLIEHXYVXPI 2 ) ) %RMQEPME 6ITXMPME 'LIPSRMMHEI 'LIPSRMEQ]HEW KVIIRXYVXPI 2 : : %RMQEPME 6ITXMPME 'LIPSRMMHEI )VIXQSGLIP]WMQFVMGEXE LE[OWFMPPXYVXPI 2 : : %RMQEPME 6ITXMPME 'LIPSRMMHEI 2EXEXSVHITVIWWYW JPEXFEGOXYVXPI 2 : : %RMQEPME 6ITXMPME 'VSGSH]PMHEI 'VSGSH]PYWTSVSWYW IWXYEVMRIGVSGSHMPI 2 : %RMQEPME %QTLMFME &YJSRMHEI 6LMRIPPEQEVMRE GERIXSEH - %RMQEPME %QTLMFME ,]PMHEI ']GPSVEREEPFSKYXXEXE KVIIRWXVMTIJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI ']GPSVEREFVIZMTIW WYTIVFGSPPEVIHJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI ']GPSVERERSZEILSPPERHMEI IEWXIVRWRETTMRKJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI 0MXSVMEGEIVYPIE GSQQSRKVIIRXVIIJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI 0MXSVMEGLPSVMW SVERKII]IHXVIIJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI 0MXSVMEHIRXEXE FPIEXMRKXVIIJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI 0MXSVMEJEPPE\ IEWXIVRWIHKIJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI 0MXSVMEKVEGMPIRXE KVEGIJYPXVIIJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI 0MXSVMEMRIVQMW FYQT]VSGOIXJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI 0MXSVMEPEXSTEPQEXE FVSEHTEPQIHVSGOIXJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI 0MXSVMEREWYXE WXVMTIHVSGOIXJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI 0MXSVMETIEVWSRMERE GEWGEHIXVIIJVSK /VSSQFMX 2 ) /VSSQFMX8STW 8STW %RMQEPME %QTLMFME ,]PMHEI 0MXSVMETIVSRMM IQIVEPHWTSXXIHXVIIJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI 0MXSVMEVSXLMM RSVXLIVRPEYKLMRKXVIIJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI 0MXSVMEVYFIPPE VYHH]XVIIJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI 0MXSVMEWT 2 %RMQEPME %QTLMFME ,]PMHEI 0MXSVMEX]PIVM WSYXLIVRPEYKLMRKXVIIJVSK 2 ' %RMQEPME %QTLMFME ,]PMHEI 0MXSVME[MPGS\MM IEWXIVRWXSR]GVIIOJVSK 2 ' %RMQEPME %QTLMFME 1]SFEXVEGLMHEI 'VMRMEHIWIVXMGSPE GLMVTMRKJVSKPIX 2 ' %RMQEPME %QTLMFME 1]SFEXVEGLMHEI 'VMRMETEVMRWMKRMJIVE FIITMRKJVSKPIX 2 ' %RMQEPME %QTLMFME 1]SFEXVEGLMHEI 'VMRMEWMKRMJIVE GPMGOMRKJVSKPIX 2 ' %RMQEPME %QTLMFME 1]SFEXVEGLMHEI 'VMRMEWT 2 %RMQEPME %QTLMFME 1]SFEXVEGLMHEI 1M\STL]IWJEWGMSPEXYW KVIEXFEVVIHJVSK 2 ' %RMQEPME %QTLMFME 1]SFEXVEGLMHEI 4WIYHSTLV]RIQENSV KVIEXFVS[RFVSSHJVSK 2 ' %RMQEPME %QTLMFME 1]SFEXVEGLMHEI 4WIYHSTLV]RIVEZIRM GSTTIVFEGOIHFVSSHJVSK 2 ' %RMQEPME %QTLMFME 1]SFEXVEGLMHEI 4WIYHSTLV]RIWT 2 %RMQEPME %QTLMFME 1]SFEXVEGLMHEI 8EYHEGX]PYWTPIMSRI /VSSQFMXXMROIVJVSK 2 ) ') %RMQEPME %QTLMFME 1]SFEXVEGLMHEI 9TIVSPIMEJYWGE HYWO]KYRKER 2 '

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

/MRKHSQ 'PEWW *EQMP] 7GMIRXMJMG2EQI 'SQQSR2EQI - 2'% )4&' 2S 0EWX7IIR %RMQEPME %QTLMFME 1]SFEXVEGLMHEI 9TIVSPIMEPEIZMKEXE IEWXIVRKYRKER 2 ' %RMQEPME %QTLMFME 1]SFEXVEGLMHEI 9TIVSPIMEVYKSWE GLYFF]KYRKER 2 ' %RMQEPME %QTLMFME 1]SFEXVEGLMHEI 9TIVSPIMEWT 2 %RMQEPME %QTLMFME 0MQRSH]REWXMHEI %HIPSXYWFVIZMW XYWOIHJVSK 2 :

%RMQEPME %QTLMFME 0MQRSH]REWXMHEI 0MQRSH]REWXIW QEVFPIHJVSK 2 ' GSRZI\MYWGYPYW %RMQEPME %QTLMFME 0MQRSH]REWXMHEI 0MQRSH]REWXIWJPIXGLIVM FEVOMRKJVSK 2 '

%RMQEPME %QTLMFME 0MQRSH]REWXMHEI 0MQRSH]REWXIWTIVSRMM WXVMTIHQEVWLJVSK 2 '

%RMQEPME %QTLMFME 0MQRSH]REWXMHEI 0MQRSH]REWXIWWEPQMRM WEPQSRWXVMTIHJVSK 2 '

%RMQEPME %QTLMFME 0MQRSH]REWXMHEI 0MQRSH]REWXIWXEWQERMIRWMW WTSXXIHKVEWWJVSK 2 '

%RMQEPME %QTLMFME 0MQRSH]REWXMHEI 0MQRSH]REWXIWXIVVEIVIKMREI WGEVPIXWMHIHTSFFPIFSRO 2 '

%RMQEPME %QTLMFME 0MQRSH]REWXMHEI 4PEX]TPIGXVYQSVREXYQ SVREXIFYVVS[MRKJVSK 2 '

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

%RMQEPME 3WXIMGLXL]IW 1IPERSXEIRMMHEI 1IPERSXEIRMEJPYZMEXMPMW 1YVVE]6MZIVVEMRFS[JMWL 2

%RMQEPME 3WXIMGLXL]IW 1IPERSXEIRMMHEI 1IPERSXEIRMEWTPIRHMHE IEWXIVRVEMRFS[JMWL 2 WTPIRHMHE %RMQEPME 3WXIMGLXL]IW 1IPERSXEIRMMHEI 6LEHMRSGIRXVYWSVREXYW SVREXIVEMRFS[JMWL 2

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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

4EKI 5YIIRWPERH+SZIVRQIRX ;IXPERH1ET'YWXSQ6ITSVX

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

4EKI )4&'%GX4VSXIGXIH1EXXIVW6ITSVX

8LMWVITSVXTVSZMHIWKIRIVEPKYMHERGISRQEXXIVWSJREXMSREPIRZMVSRQIRXEPWMKRMJMGERGIERHSXLIV QEXXIVWTVSXIGXIHF]XLI)4&'%GXMRXLIEVIE]SYLEZIWIPIGXIH

-RJSVQEXMSRSRXLIGSZIVEKISJXLMWVITSVXERHUYEPMJMGEXMSRWSRHEXEWYTTSVXMRKXLMWVITSVXEVI GSRXEMRIHMRXLIGEZIEXEXXLIIRHSJXLIVITSVX

-RJSVQEXMSREFSYXXLI)4&'%GXMRGPYHMRKWMKRMJMGERGIKYMHIPMRIWJSVQWERHETTPMGEXMSRTVSGIWW HIXEMPWGERFIJSYRHEXLXXT[[[IRZMVSRQIRXKSZEYITFGEWWIWWQIRXWETTVSZEPWMRHI\LXQP

6ITSVXGVIEXIH

7YQQEV] (IXEMPW 1EXXIVWSJ2)7 3XLIV1EXXIVW4VSXIGXIHF]XLI)4&'%GX )\XVE-RJSVQEXMSR 'EZIEX %GORS[PIHKIQIRXW

8LMWQETQE]GSRXEMRHEXE[LMGLEVI 'SQQSR[IEPXLSJ%YWXVEPME +ISWGMIRGI%YWXVEPME 471%

'SSVHMREXIW &YJJIV/Q

7YQQEV]

1EXXIVWSJ2EXMSREP)RZMVSRQIRX7MKRMJMGERGI

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AECOM Boundary Hill South Terrestrial Fauna Technical Report

Appendix B

Fauna Habitat Assessments

Appendix B Fauna Habitat Assessments

Detailed Site 1 Habitat description: Continuous open grassy woodland on a slope/hill. Lightly grazed. General condition: Ground and understorey habitat modified by hot fire. Light grazing evidenced throughout site and minor erosion along creekline. Fair condition. Dominant species: Canopy: E crebra and C. citriodora Midstorey: Petalostigma pubescens, Alphitonia excelsa Understorey: Grewia latifolia Ground cover: Lantana montevidensis, Heteropogon, Cymbopogon Corresponding RE:11.10.1 Projected Cover (grass, shrub, canopy): Canopy:25% Midstorey:15% Understorey:<5%

Ground cover:85% Disturbances: - Hot fire 95% trees with fire scars, 98% site affected by fire, < 6 months, scar height approximately 1m - Weeds moderate coverage predominantly Lantana (prostrate) and minor prickly pear (Opuntia spp.) - Light grazing throughout site Habitat features: No termite mounds, hollows present (<5cm, more than 10, >15cm 3 to 5), logs present mostly small (< 50cm dbh). Fire had reduced ground cover. Fauna signs (diggings, scats): Native bee nest, echidna diggings, cattle tracks throughout site Potential EVNT species: Square-tailed kite, black-chinned honey-eater, northern quoll, south- eastern long-eared bat, golden-tailed gecko

Detailed Site 2 Habitat description: Continuous open grassy woodland on undulating hills with light grazing, seasonal intermittent stream. General condition: Habitat modification due to light grazing throughout site with some erosion along creeklines. Multiple weeds species present throughout site. Fair condition. Dominant species: Canopy: Eucalyptus crebra, Corymbia citrodora, Eucalyptus exerta, Eucalyptus tessellaris Midstorey: Alphitonia excelsa, Petalostigma pubescens, Acacia spp. Groundcover: grasses- mostly native, Lantana montevidensis Corresponding RE: 11.9.9 Projected Cover (grass, shrub,

canopy): Canopy: 30% Midstorey: 15% Understorey: 5% Groundcover: 90% with Disturbances: - 30% cover- prostrate lantana, <1% coverage of prickly pear and various introduced grass species - 2% trees exhibited fire scars likely >10years prior - Continual grazing - Creek bank erosion along entire creek bed - Cane toads prolific on site, Habitat features: No termite mounds, medium density of logs providing potential cover for reptiles, small mammals. Fauna signs (diggings, scats): Bee (introduced species) hive Probable bandicoot diggings, cattle pads, dingo recorded on site. Potential EVNT species: Grey goshawk, black-necked stork (wet season), red goshawk, square- tailed kite, black-chinned honeyeater, northern quoll, koala, south-eastern long-eared bat, golden-tailed gecko

Detailed Site 3 Habitat description: Woodland along seasonal intermittent stream on gentle slope with evidence of partial clearing. Site connects to continuous forest. General condition: Habitat modification due to clearing/grazing evident by bare areas and erosion. Fair condition. Dominant species: Canopy: E. teriticornis and E.crebra Midstorey: Acacia spp. Understorey: Carrisa ovata and Acacia spp. Groundcover: Buffel grass Corresponding RE: 11.3.25 Projected Cover (grass, shrub, canopy): Canopy: 25% Midstorey: 10% Understorey: 5% Groundcover: 85% Disturbances: - 5% of trees/shrubs affected by die back - 10% weed cover including Lantana montevidensis and Opuntia stricta - Impacted by medium/high intensity grazing - Partial clearing - 65 of site affected by fire - Gully erosion - Cane toads very abundant near water Habitat features: Sheetrock (10%), high cover of Carissa ovata providing potential cover sites for many species. Large number of logs that would provide suitable cover for reptiles & mammals, some large hollows in stags that would provide suitable nest/den sites. Fauna signs (diggings, scats): Rabbits and bandicoot diggings. Macropod and rabbit scats. Abundant tracks of wild dog/dingo and feral cat. Owl pellet. Striated pardalotes nesting in creek bed. Potential EVNT species: Grey goshawk, red goshawk, square-

tailed kite, black-chinned honeyeater, black-necked stork (wet season), northern quoll, squatter pigeon, south- eastern long-eared bat, yakka skink, brigalow scaly-foot, golden-tailed gecko

Detailed Site 4 Habitat description: Open woodland on gentle slope, connects to continuous forest. General condition: Modified primarily by recent fire, ground cover and understorey limited. Fair condition. Dominant species: Canopy: Corymbia clarksoniana (dominated), Eucalyptus crebra Midstorey: mainly open Understorey: mainly open Groundcover: native grasses, buffel, Lantana montevidensis Corresponding RE: 11.9.9 Projected Cover (grass, shrub, canopy): Canopy: 15% Midstorey: 10% Understorey: <5% Groundcover: 40% Disturbances: - 98% of site affected by fire, 95% trees with fire scars (1-4 m), < 5 canopy affected by fire - 10% weed cover including Lantana montevidensis and Opuntia stricta - Impacted by medium/low grazing - Evidence of cattle and pigs

Habitat features: Numerous small logs but limited larger logs, but no hollows, no termite mounds, large scattered Brachychiton spp. Fauna signs (diggings, scats.): Feed tree (squirrel glider), two green tree frogs in small hallow, bandicoot diggings, noisy miner nest, macropod scats numerous, mice hollows. Potential EVNT species: Square-tailed kite, black-chinned honeyeater, south-eastern long-eared bat, golden-tailed gecko, squatter pigeon

Detailed Site 5 Habitat description: Woodland on gentle slope. General condition: Lower vegetative structure modified by hot fire. Fair condition. Dominant species: Canopy: Eucalyptus crebra and Corymbia citriodora Midstorey: Acacia spp., Alphitonia excelsa Understorey: Acacia spp. Groundcover: Predominantly native grasses, Grewia latifolia Corresponding RE: 11.10.1 Projected Cover (grass, shrub, canopy): Canopy: 30% Midstorey: 15% Understorey: 5% Groundcover: 35%

Disturbances: - 95% of site affected by hot fire, < 12 months - 5% of trees/shrubs affected by die back - 30% weed cover including Lantana montevidensis and Opuntia stricta - Light grazing Habitat features: Very high density of logs (50 20-50 cm) providing habitat for reptiles/mammals. Large stags with hollows (19 < 15 cm, 8 > 15 cm), potential sites for owl and arboreal mammals (greater glider observed). Two termite mounds. Fauna signs (diggings, scats.): Macropod scats, echidna diggings (caught on site), cattle, rabbit, possible bandicoot diggings. Potential EVNT species: Square-tailed kite, black-chinned honeyeater, northern quoll, south- eastern long-eared bat, yakka skink, golden-tailed gecko.

Habitat Assessment 1 Habitat description: Open woodland of with gentle undulating hills. Lightly grazed (continuously) and in otherwise reasonable condition. General condition: Modified by grazing and weedy grasses. Fair condition. Dominant species: Canopy: Corymbia citriodora and Eucalyptus crebra Midstorey: Acacia spp., Alphitonia excelsa Understorey: Herbaceous shrub with medic like leaves Groundcover: Buffel grass, Heteropogon contortus, Chloris spp. Corresponding RE:11.10.1 (regrowth) Cover (grass, shrub, canopy): Canopy: 15% Midstorey: 35% Understorey: 5% Groundcover: 90% with <2% bare ground and <1% small stones/gravel

Disturbances: - 25% weed cover: Lantana montevidensis and buffel grass; - Historic evidence of fire, with no signs of recent fire; - The site experiences constant low impact grazing. Habitat features: Very few logs (all small <50 cm), no termite mounds, average number of hollows, most <15 cm. Fauna signs (diggings, scats ): Cattle tracks no other signs observed. Potential EVNT species: Squatter pigeon

Habitat Assessment 3 Habitat description: Cleared pasture land with irregular acacia and eucalypt regrowth connected to high value regrowth to the west. General condition: Highly modified habitat by grazing and introduced grasses. Poor condition. Dominant species: Canopy: irregular Corymbia clarksoniana (at 100-200m spacings) Midstorey: Acacia leiocalyx Understorey: absent Groundcover: Rhodes and sabi grass, Aristida spp and Heteropogon contortus Corresponding RE: Cleared non-remnant Cover (grass, shrub, canopy): Canopy: 5% Midstorey: 20-30% Understorey: absent Groundcover: 80-90% with 10-15% exposed ground

Disturbances: - Extensive clearing - 10% Lantana montevidensis cover Habitat features: Low log density, < 5 cm only. No observed hollows or termite mounds. Fauna signs (diggings, scats): Macropod scats Potential EVNT species: Squatter pigeon

Habitat Assessment 4 Habitat description: Very sparse open woodland with thick acacia understorey on a hillcrest with coarse grained sediment. General condition: Modified by hot fire and light grazing. Fair condition. Dominant species: Canopy: Corymbia trachyphloia Midstorey: Acacia julifera Understorey: Acacia spania Groundcover: Goodenia hederacea, Aristida spp. Corresponding RE: 11.10.13 Cover (grass, shrub, canopy): Canopy: <10% Midstorey: 10-30% Understorey: 30-50% Groundcover: 30-50%

Disturbances: - 50-70% of trees showed obvious signs of fire scarring across >70% of the site with 40% of canopy affected by fire and 40% of saplings destroyed. Anticipated to have occurred <3years prior to assessment. - 0% weed cover Habitat features: Large quantity of woody debris (logs) >50m in 50x10 m plot. Some hollows but main habitat is ground sheltering sites. 30% litter on ground also contribute potential fauna sheltering opportunities. Fauna signs (diggings, scats.): Heavy recent fire disturbance made it difficult to identify fauna signs. Potential EVNT species: Square-tailed kite, large-eared pied bat, brigalow scaly-foot, common death adder, yakka skink, collared delma

Habitat Assessment 5 Habitat description: Scattered eucalypt, Corymbia mixed grassy open woodland on low undulating hills with deep red loams. General condition: Modified by grazing and previous clearing, very open habitat. Fair/poor condition. Dominant species: Canopy: Eucalyptus crebra, Corymbia clarksoniana Midstorey: Eucalyptus crebra, Corymbia clarksoniana Understorey: Alstonia constricta, Eucalyptus crebra, Corymbia clarksoniana Groundcover: Bothriochloa bladhii, sabi grass (Urochloa mosambicensis) Corresponding RE: High value regrowth 11.9.9 Cover (grass, shrub, canopy): Canopy: 20% Midstorey: 11% Understorey: 5-10% Groundcover: >90% with 5% exposed ground and 5% leaf litter coverage Disturbances: - 10% Lantana montevidensis - Feral animals- wild dogs/dingoes Habitat features: Habitat for grass dwelling fauna. Some logs for gound cover but all < 50cm. Very sparse tree hollow habitat Fauna signs (diggings, scats.): Macropod scats, dingoes and/or wild dogs Potential EVNT species: Squatter pigeon

Habitat Assessment 6 Habitat description: Low rolling hills with deep red loams and light red surface sand supporting sparse open woodland of mixed eucalypt and bloodwoods with grassy ground covering. General condition: Modified by light grazing and previous thinning. Fair condition. Dominant species: Canopy: Eucalyptus crebra, Corymbia tessellaris Midstorey: Acacia leoicalyx, hakea loreai, Alphitonia excelsa Understorey: Stylosanthes scabra Groundcover: Aristida sp., Heteropogon contortus Corresponding RE: 11.9.9 Cover (grass, shrub, canopy): Canopy: 10% Midstorey: 10% Understory: 10-20% Groundcover: 80% with 10% exposed ground 5% woody debris and 20% leaf litter

Disturbances: - Scattered weed presence of Opuntia sp., Lantana montevidensis - No evidence of fire > 10 years - Some areas thinned historically - Sheet erosion - Marginal grazing Habitat features: Some habitat value for grassy open woodland fauna Low tree hollow habitat value Medium log/woody debris habitat, 20% leaf litter Fauna signs (diggings, scats): Macropod scats Potential EVNT species: Black-chinned honeyeater, squatter pigeon

Appendix C

Terrestrial Fauna Recorded during Field Surveys

Appendix C Terrestrial Fauna Recorded during Field Surveys Birds Acanthiza nana yellow thornbill Accipiter fasciatus brown goshawk Alisterus scapularis Australian king parrot Anthus novaeseelandiae Australasian pipit Aprosmictus erythropterus red-winged parrot Ardeotis australis Australian bustard Artamus leucorynchus white-breasted wood swallow Cacatua galerita sulphur-crested cockatoo Cacatua sanguinea little corella Centropus phasianinus pheasant coucal Chalcophaps indica emerald dove Coracina novaehollandiae black-faced cuckoo-shrike Corcorax melanorhamphos white-winged chough Corvus orru Torresian crow Coturnix ypsilophora brown quail Cracticus nigrogularis pied butcherbird Cracticus torquatus grey butcherbird Dacelo novaeguineae laughing kookaburra Elanus axillaris black-shouldered kite Entomyzon cyanotis blue-faced honeyeater Eulophus roseicapillus galah Falco berigora brown falcon Falco cenchroides nankeen kestrel Geopelia humeralis bar-shouldered dove Geopelia striata peaceful dove Geophaps scripta squatter pigeon Gergone olivacea white-throated gerygone Grallina cyanoleuca magpie lark Grus rubicundus brolga Gymnorhina tibicen Australian magpie Hirundo neoxena welcome swallow Lichenostomus chrysops yellow-faced honeyeater Lichenostomus leucotis white-eared honeyeater Lichenostomus virescens singing honeyeater Malurus melanocephalus red-backed fairy-wren Manorina melanocephala noisy miner Meliphaga lewinii Lewin's honeyeater Melithreptus albogularis white-throated honeyeater Melithreptus gularis black-chinned honeyeater Merops ornatus rainbow bee-eater Milvus migrans black kite Ninox novaeseelandiae southern boobook owl

Birds Nymphicus hollandicus cockatiel Ocyphaps lophotes crested pigeon Oriolus sagittatus olive-backed oriole Pachycephala rufiventris rufous whistler Pardalotus punctatus spotted pardalote Pardalotus striatus striated pardalote Phaps chalcoptera common bronzewing Philemon buceroides helmeted friarbird Philemon corniculatus noisy friarbird Platycercus adscitus pale-headed rosella Podargus strigoides tawny frogmouth Pomatostomus temporalis grey-crowned babbler Rhipidura albiscarpa grey fantail Rhipidura leucophrys willy wagtail Smicornis brevirostris weebill Stiltia isabella Australian pratincole Strepera graculina pied currawong Struthidea cinerea apostlebird Tachyhaptus novaehollandiae Australasian grebe Taeniopygia bichenovii double-barred finch Threskiornis spinicollis straw-necked ibis Todiramphus macleayii forest kingfisher Trichoglossus haematodus rainbow lorikeet Tyto javanica Pacific barn owl Vanellus miles masked lapwing Mammals

Canis lupus dingo/familiaris* dingo/dog Chaerephon jobensis northern freetail bat Chalinolobus gouldii Gould's wattled bat Chalinolobus picatus little pied bat Felis catus* cat Isoodon macrourus northern brown bandicoot Macropus giganteus eastern grey kangaroo Macropus parryi whiptail wallaby Miniopterus australis little bentwing bat Miniopterus schreibersii eastern bentwing bat Mormopterus beccarii Beccari's freetail bat Mormopterus spp. freetail bat spp. mus musculus* house mouse Nyctophilus spp.. long-eared bat sp. Oryctolagus cuniculus* rabbit Petaurus norfolcensis squirrel glider Petaurus volans greater glider Rhinolophus megaphyllus eastern horseshoe bat

Birds Saccolaimus flaviventris yellow-belled sheathtail bat Scotorepens greyii little broad-nosed bat Sus scrofa* pig Tachyglossus aculeatus short-beaked echidna Tadarida australis white-striped freetail bat Vespadelus troughtoni eastern cave bat Vulpes vulpes* European fox Wallabia bicolor black wallaby Reptiles

Aspidites melanocephalus black-headed python Carlia munda

Carlia vivax lively rainbow skink Diplodactylus vittatus eastern stone gecko Diporiphora australis Tommy roundhead dragon Furina diadema red-naped snake Gehyra dubia

Morelia spilota carpet python Oedura rhombifer zigzag velvet gecko Pogona barbata bearded dragon Amphibians

Limnodynastes ornatus ornate burrowing frog Litoria caerulea green tree frog Bufo marinus* cane toad

Appendix D

Fauna Analyses Results

Prepared for (“Client”): AECOM Survey location/project name: Boundary Hill Coal Mine Survey dates: 5-10 September 2012 Client project reference: 60238883 Task 1.02.19 Job no.: AECO1208 Report date: 28 September 2012

DISCLAIMER:

© Copyright – Balance! Environmental, ABN 75 795 804 356. This document and its content are copyright and may not be copied, reproduced or distributed (in whole or part) without the prior written permission of Balance! Environmental other than by the Client for the purposes authorised by Balance! Environmental (“Intended Purpose”). To the extent that the Intended Purpose requires the disclosure of this document and/or its content to a third party, the Client must procure such agreements, acknowledgements and undertakings as may be necessary to ensure that the third party does not copy, reproduce, or distribute this document and its content other than for the Intended Purpose. This disclaimer does not limit any rights Balance! Environmental may have under the Copyright Act 1968 (Cth). The Client acknowledges that the Final Report is intended for the sole use of the Client, and only to be used for the Intended Purpose. Any representation or recommendation contained in the Final Report is made only to the Client. Balance! Environmental will not be liable for any loss or damage whatsoever arising from the use and/or reliance on the Final Report by any third party. Methods

Data receipt and processing

Bat calls were recorded over four consecutive nights (5-9 or 6-10 September 2012) using Song Meter SM2BAT detectors (Wildlife Acoustics, Concord MA, USA). Survey data were downloaded from the detectors’ SD cards using Wildlife Acoustics’ Kaleidoscope software. Bat call data were saved in Anabat (zero-crossing) format, with some 3305 Anabat sequence files submitted to Balance Environmental for analysis.

Zero-crossing analysis

The Anabat sequence files were viewed using AnalookW (Corben 2009) and a representative sub-set of all observed call types were extracted for identification. Calls with fewer than four clearly-defined, non-fragmented pulses were excluded from the identification process.

Species identification was achieved manually by viewing sonograms of the extracted calls in AnalookW and comparing them with reference calls from central and southern Queensland and/or with published call descriptions (e.g. Reinhold et al. 2001; Milne 2002; Pennay et al. 2004).

Determination of species' identity was refined by considering probability of occurrence based on general distribution information (e.g. Churchill 2008; van Dyck & Strahan 2008) and/or database records obtained from WildNet (DERM 2012) and/or the Queensland Museum (QM 2008) and/or the Atlas of Living Australia (http://www.ala.org.au).

Reporting standard

The format and content of this report follows Australasian Bat Society standards for the interpretation and reporting of bat call data (Reardon 2003), available on-line at http://www.ausbats.org.au/.

Species nomenclature follows Armstrong & Reardon (2006).

Results

Data quality and duration of detection sessions

A high proportion of the sequence files contained only background noise or very brief/weak/fragmented bat calls that were of no use for species identification purposes. It was, however, possible to extract some 650 calls of fair-to-good quality for further processing and identification.

Time signatures saved in the data files indicate that all detection sessions were conducted overnight, commencing around 6:00pm and ceasing at about 6:00am the following morning.

Species recorded

Thirteen microbat species were positively identified from this survey data (see Table 1). Up to sixteen species may have been present, but some species could not be reliably identified due to a combination of poor call quality and similarities in call characteristics between several species.

AECO1208_Boundary Hill Mine_bat call analysis.docx 28/09/2012 Page 2 of 8 Table 1. Microbat species recorded at Boundary Hill Coal Mine, 5-10 September 2012. ♦ = species positively identified from call data □ = species possibly present, but not reliably identified

Secondary Site: Site 3 Site 4 Site 5 Site 1

Total no. sequence files: 253 540 316 2196

No. calls identified: 41 153 145 314

SPECIES

Rhinolophus megaphyllus ♦ ♦

Chalinolobus gouldii □ ♦ ♦ ♦

Chalinolobus morio □ □ □

Chalinolobus picatus □ ♦ ♦ □

Nyctophilus species ♦ ♦ ♦

Scotorepens greyii ♦ □ ♦

Vespadelus baverstocki □ □ □ □

Vespadelus troughtoni ♦ ♦ □

Miniopterus australis ♦ ♦

Miniopterus schreibersii ♦ ♦ ♦ □

Tadarida australis ♦ ♦

Chaerephon jobensis ♦ ♦ ♦ ♦

Mormopterus beccarii ♦ ♦

Mormopterus species 2 ♦ ♦ ♦ ♦

Saccolaimus flaviventris ♦ ♦ ♦ ♦

Taphozous georgianus * □ □

* Churchill (2008) shows the widely distributed sheath-tailed bat in Queensland as T. troughtoni, citing taxonomic analyses undertaken by T. Reardon and B. Thomson; however, since this taxonomic change has not been formerly published or accepted by the international nomenclature authorities, T. georgianus remains the correct species name for the majority of the Queensland distribution (T. Reardon, pers. comm.).

Discussion

Thirteen of the sixteen species listed in Table 1 were positively identified from at least one call in one or more detection sessions; however, some of those 13 species are listed only as “probable” for other sessions. Where this is the case, fragmented and/or brief calls were recorded that may have been from the listed species or from one or more other species that overlap in frequency and have similar

AECO1208_Boundary Hill Mine_bat call analysis.docx 28/09/2012 Page 3 of 8 pulse shape characteristics. Such calls are attributed to a species group depending on frequency range.

Species groupings used in this analysis for calls with low reliability of identification include:

 Saccolaimus flaviventris / Chaerephon jobensis (Fc=16-20 kHz);

 Taphozous georgianus / Mormopterus beccarii (Fc=22-24 kHz);

 Chalinolobus gouldii / Mormopterus species 2 (Fc=28-34 kHz);

 Chalinolobus picatus / Scotorepens greyii / Vespadelus baverstocki (Fc=39-42 kHz);

 Nyctophilus species (Fc=35-50 kHz);

 Miniopterus schreibersii / V. baverstocki (Fc=43-46 kHz); and

 Chalinolobus morio / Vespadelus troughtoni (Fc=48-53 kHz).

Where a species group is identified, all species within the group are listed as “probable” in the results; however, if a species within the group was also identified positively from other calls, they are listed as such in Table 1.

Within the above species groups, there are four species for which no positive identification was made from this data set. These are discussed in more detail below.

Chalinolobus morio

This species’ frequency range completely overlaps that of Vespadelus troughtoni; however, the two can usually be separated on distinctive pulse shapes – slanted body with down-sweeping tail in C. morio compared with curved body and up-swept tail in V. troughtoni.

Some calls were reliably attributed to V. troughtoni based on these characteristics, but a number of calls appeared to have pulse features intermediate between the two and were thus listed as possibly from C. morio in the results.

Nyctophilus species

These species’ calls have steep, almost-linear, broad-band pulses that terminate around 35-45 kHz. They are readily distinguished from the calls of other bats, but species within the genus cannot be reliably differentiated on call structure. Two species probably occur in the study area: N. geoffroyi and N. gouldi.

Vespadelus baverstocki

This species’ calls have steep, short-duration, broad-band pulses with curved to cup-shaped bodies. Frequency range overlaps with both Miniopterus schreibersii and Chalinolobus picatus, but most calls from these species can be distinguished on pulse shape (M. schreibersii has longer duration pulses with slanted bodies and no tail) or inter-pulse frequency alternation (C. picatus). These features were used to positively identify a number of calls for each species at several sites. Many calls, however,

AECO1208_Boundary Hill Mine_bat call analysis.docx 28/09/2012 Page 4 of 8 were fragmented or had intermediate pulse characteristics; with those around 44-45 kHz labelled as M. schreibersii/V. baverstocki and a few around 42 kHz as C. picatus/V. baverstocki.

Taphozous georgianus

Churchill (2008) shows the widely distributed sheath-tailed bat in Queensland as T. troughtoni, citing taxonomic analyses undertaken by T. Reardon and B. Thomson; however, this taxonomic change has not been formerly published or accepted by the international nomenclature authorities (T. Reardon, pers. comm., 2012), so T. georgianus remains the correct species name for the common sheath-tailed bat that occurs in central Queensland.

Characteristics frequency (22-25 kHz) overlaps substantially with that of Mormopterus beccarii (Fc=23-27 kHz) and some calls are difficult to differentiate. The latter species was reliably identified from a number of calls where pulses were strongly-curved, with downward-sloping tails; however, a few calls with shorter-duration, flatter pulses with no clear tails could have been from either species.

Given the presence of other cave-dependent species (Miniopterus spp., V. troughtoni and Rhinolophus megaphyllus) in the data set, there is a strong possibility that T. georgianus was responsible for some of these intermediate calls.

References

Armstrong, K. and Reardon, T. (2006). Standardising the common names of Australian bats – an update. The Australasian Bat Society Newsletter, 26, 37-42.

Churchill, S. (2008). Australian Bats. Jacana Books, Allen & Unwin; Sydney.

Corben, C. (2009). AnalookW Version 3.7w. Software for bat call analysis using ZCA data.

Corben, C. (2011). CFCread Storage ZCAIM interface Version 4.3s.

DERM (2012). WildNet database extract: Vespadelus baverstocki & Vespadelus vulturnus. Department of Environment and Resource Management, Mackay. Extracted May 2012.

QM (2008). Queensland Museum specimen register database extract: Vespertilionidae. Queensland Museum, South Bank, Brisbane. Extracted January 2008.

Pennay, M., Law, B. and Reinhold, L. (2004). Bat Calls of New South Wales. Department of Environment and Conservation, Hurstville.

Reardon, T. (2003). Standards in bat detector based surveys. Australasian Bat Society Newsletter 20, 41-43.

Reinhold, L., Law, B., Ford, G. and Pennay, M. (2001). Key to the bat calls of south-east Queensland and north-east New South Wales. Department of Natural Resources and Mines, Brisbane. van Dyck, S. and Strahan, R. (ed.) (2008). The Mammals of Australia (Third Edition). New Holland; Sydney.

AECO1208_Boundary Hill Mine_bat call analysis.docx 28/09/2012 Page 5 of 8 Rhinolophus megaphyllus Chalinolobus gouldii

Possibly Chalinolobus morio Chalinolobus picatus

Nyctophilus species Scotorepens greyii Figure 1 Representative call sequences recorded at Boundary Hill Mine, September 2012. (10msec per tick; time between pulses removed)

AECO1208_Boundary Hill Mine_bat call analysis.docx 28/09/2012 Page 6 of 8 Possibly Vespadelus baverstocki Vespadelus troughtoni

Miniopterus australis Miniopterus schreibersii

Tadarida australis Chaerephon jobensis Figure 1 (cont.) Representative call sequences recorded at Boundary Hill Mine, September 2012. (10msec per tick; time between pulses removed)

AECO1208_Boundary Hill Mine_bat call analysis.docx 28/09/2012 Page 7 of 8 Mormopterus beccarii Mormopterus sp. 2

Saccolaimus flaviventris Possibly Taphozous georgianus Figure 1 (cont.) Representative call sequences recorded at Boundary Hill Mine, September 2012. (10msec per tick; time between pulses removed)

AECO1208_Boundary Hill Mine_bat call analysis.docx 28/09/2012 Page 8 of 8 Biloela - scat and hair samples

No. Date Site Location Sample Mammal ID - definite Mammal ID - probable 1 9/09/2012 1 caves bird pellet insect material only 2 9/09/2012 2 caves cat scat insect material; Felis catus (grooming) 3 9/09/2012 3 caves ?quoll/fox scat feathers only 4 9/09/2012 4 caves ?quoll/fox scat feathers only 5 9/07/2012 Secondary 1 rocky outcrops dog scat insect material, seeds; Canis familiaris (gr) 6 9/07/2012 Secondary 1 rocky outcrops ?fox scat Isoodon macrourus 7 9/07/2012 Secondary 1 rocky outcrops ?dog scat insect material, seeds 8 9/07/2012 Secondary 1 rocky outcrops bird pellet insect material only 9 9/07/2012 Secondary 1 rocky outcrops dog scat Wallabia bicolor 10 9/07/2012 Secondary 1 rocky outcrops dog scat C. familiaris (prey) 11 9/07/2012 Secondary 1 rocky outcrops macropod scats Macropus sp. M. rufogriseus 12 9/07/2012 Secondary 1 rocky outcrops macropod scats Macropus sp. M. rufogriseus 13 9/07/2012 Secondary 1 Boundary Hill ?fox scat I. macrourus 14 9/07/2012 3 Boundary Hill dog scat Mus musculus 15 9/09/2012 4 pig scats Sus scrofa 16 9/09/2012 4 pig scats S. scrofa 17 9/09/2012 4 Boundary Hill hair tube M. musculus 18 9/09/2012 4 Boundary Hill hair tube M. musculus