Environment Protection and Biodiversity Conservation (Recovery Plan—Mahogany Glider (Petaurus gracilis)) Instrument 2021

The recovery plan is structured around a small set of interlocking technical and planning concepts, each defined and applied in the document. Those concepts determine the choice of actions, measurement of success, and the Plan’s scope of influence.

• Listed conservation status and legal source: The Mahogany Glider is listed Endangered under the EPBC Act and the Queensland Nature Conservation Act 1992 (Summary 1.2; section 2.2). The recovery plan is made under s 269A(3) EPBC Act; the Plan is therefore an instrument that identifies priorities for recovery under Commonwealth conservation policy (instrument header; 2.1).

• Habitat critical to survival: The Plan sets out a broad functional definition of "habitat critical to survival", which includes any habitat where the species is likely to occur within the known distribution, newly discovered sites extending its range, and mapped subpopulations and priority corridors (Summary 1.4; section 3.6). The Plan explicitly links this to Queensland's "Essential Habitat" under the Vegetation Management Act 1999 and to corridors linking such habitat (section 3.6).

• Threat taxonomy: The Plan classifies threats into historical (broadscale clearing), current (habitat loss and fragmentation, inappropriate fire regimes, grazing mismanagement, weeds, small population size, roads/easements, barbed wire fencing, extreme climatic events) and potential future threats (climate change, introduced predators, Myrtle Rust disease) (Summary 1.5; section 4). Each threat entry gives mechanisms by which the threat reduces habitat quality, connectivity or population viability (e.g. fire regime changes leading to rainforest transition and sclerophyll thickening, increasing canopy cover and loss of food/den trees, section 4.2.2).

• Connectivity and corridors: Maintaining and restoring connectivity is central to recovery. The Plan identifies 10 subpopulations and 55 priority corridors, assigns priorities for each corridor and quantifies gaps >30 m and combined gap lengths (Map 3; Appendix B). The Plan treats corridors as both movement pathways and management priorities rather than long‑term refugia (section 3.6; 8.3.1).

• Management toolbox: The Plan focuses on a prescribed set of management instruments: targeted grazing incentives and extension (Action 1.1), prescribed and adaptive fire regimes (1.2, 8.3.3), revegetation and corridor plantings (1.4, 8.3.1), removal or retrofitting of barbed wire (1.1 and 8.3.5), installation of glider poles or rope bridges (1.4; 8.3.1 and 8.3.2), weed control (1.3), monitoring frameworks and genetic studies (2.1-2.4), community engagement (Objective 4), and emergency response planning including trigger thresholds for captive breeding and translocation assessments (Objective 5, actions 5.1-5.4).

• Governance and funding: The Plan positions the MGRT as the coordinating governance body (section 2.4; 6.2.3). It sets out indicative partner roles and indicative costs across five years (Table 8) but explicitly states that implementation is subject to budgetary constraints and that a detailed implementation plan must be negotiated with responsible partners (section 7.1).

• Success metrics and adaptive review: The Plan includes measurable criteria (increase in extent of high‑quality habitat; improved population trajectory; maintenance of genetic diversity; connectivity restoration in at least 5 priority corridors; infrastructure guidelines implemented; adoption of grazing and fire regimes by landholders; community engagement metrics) to be achieved or started within 10 years (Summary 1.6-1.7; section 6.2.2). A formal review is required no later than five years after endorsement (section 7.2).

Each of these concepts carries operational implications. For example, "habitat critical to survival" as defined will be used to prioritise mapping, monitoring and potentially influence impact assessments (section 3.6; 8.2). "Connectivity" is operationalised as corridors with quantifiable gap metrics (Appendix B), and "management toolbox" actions are linked to measurable units (hectares revegetated, kilometres of barbed wire removed) in Tables 3-8. The Plan therefore converts high‑level conservation goals into spatially explicit, partner‑allocated, time‑phased actions with indicative budgets.

The recovery plan names the principal parties expected to act under the Plan and those affected by its implementation. The text identifies a mix of public agencies, private landholders, industry participants and community groups as both implementers and subjects of measures.

• Commonwealth and State agencies: The Commonwealth Department of Agriculture, Water and the Environment (DAWE) and the Queensland Department of Environment and Science (DES) are key partners and recipients of monitoring data (section 2.3; 6.2.2; 7.1). Other Queensland departments named as potential partners include Department of Natural Resources, Mines and Energy (DNRME); Department of Agriculture and Fisheries (DAF); Department of Transport and Main Roads (TMR); Queensland Fire and Emergency Services (QFES) and Queensland Rural Fire Service (QRFS) (Table 8).

• Local government and statutory managers: Cassowary Coast Regional Council (CCRC), Hinchinbrook Shire Council (HSC), and other local authorities are identified as potential partners for landholder outreach, planning instruments, and local-level measures (section 2.3; Table 8; 7.4).

• Landholders and private owners: Private landholders are directly affected: the Plan anticipates engagement of at least fifteen private landholders historically and proposes targeted programs to modify grazing, fencing and revegetation practices across private tenure (section 5; Action 1.1; 7.4). The Plan contemplates developing mechanisms "for protection of Mahogany Glider habitat on freehold tenures" and "specific impact assessment and restrictions for Lot Reconfiguration applications" and for Material Change of Use (MCU) applications (Action 1.5; section 4.2.1). These are proposed outcomes, not immediate statutory prohibitions in the Plan text, but they indicate intended regulatory or planning change that would affect property rights and land‑use decisions if enacted.

• Infrastructure operators and utilities: Transport and easement managers, including TMR, Powerlink, Ergon/Energy Queensland, and Queensland Rail, are named as partners and targets for guidelines to avoid habitat fragmentation, to adopt launch tree retention and to install mitigation such as glide poles where gaps exceed average glide distances (sections 1.6; 6.2.3; 8.3.2).

• Natural Resource Management organisations and NGOs: Terrain NRM, North Queensland Dry Tropics (NQDT), Wildlife Preservation Society Queensland (WPSQ), and other NGOs are repeatedly nominated as implementation partners for on‑ground works, data collection, and community engagement (sections 2.3, 6.2.3, Table 8).

• First Nations and Traditional Owners: Girringun Aboriginal Corporation, Girringun Rangers and First Nations people are explicitly included as partners, with the Plan recognising the role of Traditional Owners in monitoring, on‑country management, and the incorporation of cultural knowledge where negotiated (sections 2.3, 2.4, 7.5, 6.2.3 Action 4.2).

• Community groups, schools and volunteers: The Plan sets measurable community engagement targets (Action 4.3: engagement with at least one school and 20 new volunteers annually; Action 4.1 to establish local leaders network).

• Research institutions and zoos: James Cook University (JCU) and research partners are named for monitoring, genetic studies, and captive-breeding assessments (Actions 2.1-2.4; 5.4). Zoos and facilities (David Fleay Wildlife Park, Currumbin Sanctuary, Dreamworld, and university facilities) are discussed in the context of husbandry and the existing captive population (section 8.3.7).

Who bears costs and compliance effort: the Plan explicitly allocates indicative costs in Table 8 across actions and years, and identifies which partner types are expected to supply labour, governance and funding. It states implementation is "subject to budgetary and other resource opportunities and constraints" and that "where possible, the cost... should be incorporated into core business expenditure of the affected organisations and through additional funds obtained" (section 7.1). At present many measures are framed as voluntary, incentivised, or to be delivered via programs and grants rather than via immediate statutory compulsion (sections 1.5; 7.1). However the Plan envisages development of statutory planning instruments and specific impact assessment measures for lot reconfiguration and MCU applications (Action 1.5) which, if implemented, would change regulatory burdens on developers and landowners.

Practical implications for private actors: The Plan signals that developers and infrastructure operators should consider potential "significant impacts" under the EPBC Act Significant Impact Guidelines (2013), specifically where vegetation clearing, removal of den trees, or fragmentation across corridors could occur (section 8.2). It also identifies concrete operational thresholds , for example average glide distance (~30 m) as a functional gap metric relevant to whether an action may fragment a population (sections 4.2.6; 8.3.2).

The recovery plan largely sets out duties and rights in programmatic and administrative terms rather than imposing new criminal sanctions. The text defines expected duties, suggested rights and the decision points that will shape future statutory or regulatory change.

Duties and obligations created or triggered by the Plan (as expressed in the document)

• Ministerial instrument under EPBC Act: The Plan is a recovery plan made under subsection 269A(3) EPBC Act. That status makes it an official recovery instrument which will inform Commonwealth decision‑making under the EPBC Act. The Plan is the formal document ministers will rely upon when coordinating recovery actions, but the Plan itself does not specify new offence provisions (instrument header; sections 2.1, 7.1).

• Data and reporting duties for implementation partners: Partners and contributors are expected to collect and share monitoring data. The Plan requires updating and maintaining sightings and actions databases (Terrain NRM maintained, upload to WildNet managed by DES and DAWE), training contributors and regular reporting (Action 2.2; section 6.2.2).

• Governance duties for the MGRT: The MGRT is tasked with coordinating implementation, ensuring reporting, facilitating funding arrangements, and conducting the five‑year review (sections 2.4; 6.2.3; 7.2). Membership is drawn from named sectors but may change; the MGRT has responsibility to develop an implementation plan and governance protocols for funds (section 7.1; Action 3.2).

• Duty to develop or adopt guidelines and best practice: The Plan requires development and dissemination of best practice guidelines for grazing, fire, revegetation, infrastructure planning and maintenance, glider pole installation, fencing, and disaster recovery, to be taken up by agencies, councils, landholders and infrastructure providers (Actions 1.1-1.6; 8.3).

• Emergency response duties: The Plan requires identification of trigger thresholds and emergency response protocols (Action 5.1), establishment of governance and protocols for emergency responses (Action 5.2), and development of post‑cyclone recovery strategies (Action 5.2-5.3).

Rights and procedural expectations

• Rights to consultation and negotiated implementation: The Plan repeatedly frames actions as to be implemented through negotiated partnerships and through development of implementation plans with agreed partner contributions; it anticipates consultations with landholders, First Nations people, councils and agencies (sections 6.1; 7.1; 7.4; Actions 1.5, 4.2).

• Access to incentive programs and funding: The Plan envisages incentives and possible funding mechanisms for private landholders (Action 1.1; 7.1). It also requires the MGRT to investigate philanthropic, corporate investment and offsets as funding sources and to establish governance for managing these funds (Action 3.2).

• Procedural role in planning and approvals: While the Plan does not itself create statutory powers to veto or require consent for development, it expressly advises proponents to consult the EPBC Significant Impact Guidelines and to consider the Plan’s maps and definitions in assessing potential significant impacts (section 8.2). The Plan proposes that specific assessment and restrictions for Lot Reconfiguration and MCU applications be developed, thereby potentially affecting rights attached to property subdivision and land‑use changes if implemented (Action 1.5).

What the Plan does not do (explicit absences)

• It does not in its text create new criminal offences, penalties, or a directly enforceable regulatory regime. Enforcement and penalties for damaging Matters of National Environmental Significance remain those under the EPBC Act (the Plan itself contains no penalty schedule). The document repeatedly notes that implementation is subject to funding and negotiation and that statutory instruments may be developed in future (sections 7.1; Action 1.5).

• It does not guarantee funding or compulsory action: many targets are contingent, presented as performance measures to be met if funding and partner commitments occur (Tables 3-8; section 7.1). The Plan also contains a formal disclaimer about funding commitments and that stakeholders "have not necessarily committed to undertaking specific actions" (front matter disclaimer and section 2.1).

In short, the Plan creates administrative duties for MGRT and suggested duties for partners to prepare and implement guidelines, monitoring and on‑ground works, and it creates an evidentiary and planning template that can be invoked in assessments and planning decisions. It signals intended regulatory change (e.g. developing statutory planning instruments) but does not itself legislate those changes.

The recovery plan document and the EPBC Act instrument text provided do not create new standalone penalties or enforcement mechanisms within the Plan. The Plan instead relies on existing statutory frameworks and on negotiated, programmatic and incentive‑based implementation. The instrument and Plan contain explicit statements that implementation is subject to budgetary and other constraints and that stakeholders have not necessarily committed to undertaking specific actions (front matter disclaimer; section 7.1). The relevant enforcement and penalty implications are therefore indirect and administratively mediated.

Key points from the Plan about enforcement, compliance and consequences

• No new penalty provisions in the Plan text: The Plan is an administrative recovery plan made under s 269A(3) EPBC Act and contains no clause creating offences or financial penalties. It sets out recommended actions, priority indicators, performance measures and indicative costs (Tables 3-8), but enforcement of on‑ground compliance is to be delivered through partner agreements, statutory planning instruments yet to be developed (Action 1.5), and through existing regulatory systems including the EPBC Act and Queensland legislation (sections 1.5; 7.1; 8.2).

• EPBC Act assessment and significant impact test remains operative: The Plan cross‑references the EPBC Act Significant Impact Guidelines 1.1 (Department of the Environment, 2013) and instructs proponents to consider criteria under which an action may have a significant impact on an endangered species. Examples include clearing within corridors, removal of den trees (trees with hollows, DBH ≥20 cm), creation of gaps >30 m, and insufficient management of remaining habitat (section 8.2). Where a proposed action is a controlled action under the EPBC Act, civil or criminal penalties under that Act remain in play; the Plan itself does not add to that statutory regime.

• Enforcement relies on existing and future statutory instruments: The Plan envisages developing statutory planning instruments and specific impact assessment requirements for Lot Reconfiguration and MCU applications (Action 1.5). If such instruments are created under state planning law, they could introduce enforceable conditions or obligations through the planning approvals process. Until those instruments exist, the Plan’s guidance is advisory and programmatic.

• Implementation via agreements and funding conditions: A significant portion of delivery is expected to be through negotiated implementation plans, grant funding, incentives and landholder programs. Compliance in those contexts will depend on contractual terms, funding agreements and the allocation of resources through the MGRT and partner organisations (section 7.1; Action 3.2).

• Monitoring, reporting and review as administrative enforcement levers: The Plan uses monitoring systems (sightings database, WildNet, MGRT database) and scheduled reviews (five‑year review) as mechanisms to track progress, adapt action and inform funding and planning decisions (Actions 2.1-2.2; 7.2). Non‑performance may reduce future funding or priority standing, but the Plan does not specify administrative sanctions.

In practice, enforcement and penalties that would arise from implementation are likely to flow from:

• Assessments under the EPBC Act where an action triggers the significant impact test and becomes a controlled action;
• State and local planning instruments (existing or created to implement Plan intentions) that could attach conditions, prohibitions or obligations as part of land‑use approvals; and
• Contractual or grant conditions imposed by funding bodies and programs that support Plan delivery.

The Plan is explicit that it is not a funding commitment and that the "attainment of objectives and the provision of funds may be subject to budgetary and other constraints" (front matter disclaimer; section 7.1). Readers should therefore treat the Plan as a guide and policy instrument that shapes assessment and funding decisions rather than as a self‑executing enforcement code.

The recovery plan situates itself within a multi‑layered statutory and policy environment and identifies specific linkages to Commonwealth, State and local planning frameworks and operational guidelines. The Plan repeatedly recognises that it complements, informs and will interact with other instruments rather than supplanting them.

Explicit interactions and cross‑references in the text

• EPBC Act: The recovery plan is made under s 269A(3) of the EPBC Act (instrument header). The Plan references the EPBC Act Significant Impact Guidelines 1.1 (Department of the Environment, 2013) as the criteria proponents should use to assess significant impacts on an endangered species (section 8.2). That guideline sets the threshold under Commonwealth law for when an action will require referral and assessment. The Plan is therefore normative for Commonwealth environmental assessment and will be taken into account in EPBC decision‑making.

• Queensland Nature Conservation Act 1992 (NCA): The Plan records that the Mahogany Glider is listed Endangered under the NCA (Summary 1.2; section 2.2). It references the Code of Practice under the NCA for care of sick, injured or orphaned protected animals (section 8.3.7). Implementation on Queensland land will therefore need to be reconciled with NCA obligations and permits.

• Vegetation Management Act 1999 (VMA) and "Essential Habitat": The Plan explicitly treats Essential Habitat under the Queensland VMA as part of "habitat critical to survival" and identifies corridors linking Essential Habitat as part of the critical habitat network (section 3.6). This ties Commonwealth recovery priorities to a Queensland statutory category used in vegetation clearing and planning contexts.

• Local government planning and MCU/Lot Reconfiguration approvals: The Plan identifies Material Change of Use (MCU) applications and Lot Reconfiguration as local planning mechanisms that can lead to intensification of land use and incremental habitat loss; the Plan proposes developing specific impact assessment and restrictions for these application classes (Action 1.5; section 4.2.1). That indicates intended interaction with local planning schemes and development approvals.

• State sector plans and policies: The Plan lists state and regional documents with which it interacts (section 8.1), including the Queensland Coastal Plan (2011), State Policy for Vegetation Management (2013), Wet Tropics regional plans, regional pest management strategies and local government biosecurity and planning documents. The Plan aims to "not restate" those instruments but to identify common approaches and promote alignment.

• Infrastructure regimes and easement maintenance: The Plan advises that road, rail and powerline planning, construction and maintenance guidelines be updated to minimise habitat fragmentation and maintain launch trees (Action 1.5 and 8.3.2). This suggests operational interaction with agencies' asset management regimes and maintenance contracts and with vegetation clearance rules governing easement corridors.

• Disaster recovery and emergency powers: The Plan calls for development of post‑cyclone recovery strategies and recovery protocols, noting that post‑cyclone clean‑up can itself threaten habitat (section 8.3.6; Action 5.2-5.3). Implementation will interact with emergency management and disaster recovery frameworks at state and local levels.

Operational consequences of these interactions

• Evidence‑based weighting in assessments: The Plan provides spatial maps, corridor priorities and explicit criteria (e.g. launch tree DBH, gap distances) that assessment officers and proponents can use when applying the EPBC significant impact test. The Plan’s maps and definitions will be an evidentiary input into project assessments (section 8.2; Maps 1-3).

• Regulatory instruments to be developed: The Plan anticipates development of statutory planning instruments for habitat protection on freehold tenures and specific impact assessment measures for MCU and Lot Reconfiguration (Action 1.5). Where developed, such instruments would represent a direct legal interaction that could alter land‑use rights and approval pathways.

• Co‑regulatory and incentive approach: Many of the Plan’s actions are to be delivered by negotiation, grants, incentives and voluntary adoption by landholders. Implementation therefore depends on cross‑agency coordination, conditional funding and contractual mechanisms rather than single statutory commands (sections 6.2.3; 7.1; Action 3.2).

• Complementarity with state conservation lists and regional strategies: Since the species is listed under both Commonwealth and state law, the Plan supports alignment of recovery actions and monitoring across jurisdictions. It also aims to leverage existing regional plans and NRM programs to avoid duplication and to target resources (section 8.1).

In short, the recovery plan positions itself as a coordinating document that will influence Commonwealth assessment decisions and seeks to guide state, local and infrastructure operators’ practice. Direct legal force beyond informing assessments and prompting the development of statutory planning instruments is not itself contained in the Plan, but the Plan establishes the factual and policy basis for those possible legal interactions.

The recovery plan document records a short amendment and replacement history and situates the current instrument in a lineage of recovery planning for the species.

Key dated events and documents recorded in the Plan

• Original recovery plan: The earlier "National recovery plan for the Mahogany Glider Petaurus gracilis" prepared by Parsons & Latch (2006) is explicitly referenced as the previous recovery plan that the current Plan replaces (section 2.1; Appendix A). The 2006 plan’s objectives and outputs are summarised and evaluated in Appendix A.

• Review of previous plan: A review of the 2006 recovery plan was undertaken in 2013; the Plan summarises the review findings and identifies reasons the previous plan’s objectives were not fully met, notably lack of funding, limited habitat mapping for condition and extent, and impacts from extreme weather events (section 2.1; Appendix A).

• Current recovery plan publication date: The recovery plan document itself carries a publication date of April 2021 (cover and title page: "National Recovery Plan for the Mahogany Glider (Petaurus gracilis) April 2021"). The text of the Plan thus dates from 2021.

• Instrument dates and registration: The ministerial instrument making the recovery plan is signed by the Queensland Minister Meaghan Scanlon on 9 December 2021 and by the Commonwealth Minister Sussan Ley on 1 February 2022. The Plan as an instrument under s 269A(3) will come into force on the day after the Plan is registered on the Federal Register of Legislation (instrument header).

• Indicative implementation timeline: The Plan sets out indicative timeframes for actions and funding across the first five years (Table 8) and requires a formal review no later than five years after endorsement/public availability (section 7.2). The Plan also sets 10‑year criteria for success to judge whether recovery has progressed (Summary 1.7; section 6.2.2).

Notable features about amendment and review mechanics

• The Plan prescribes a five‑year formal review to reassess priorities, the need for adaptation, and whether a recovery plan should remain in force or be replaced by conservation advice (section 7.2). That review is to be coordinated by the MGRT in consultation with partners.

• The Plan explicitly allows for adaptive modification to reflect new knowledge, implementation experience and changing conservation status (section 7.2). It anticipates that initial indicative costs and timeframes for actions beyond year five will be updated as programs roll out and data accrues (section 7.1).

• There is no text in the recovery plan instrument specifying a formal amendment procedure for the ministerial instrument under EPBC Act beyond the normal processes under the EPBC Act for making or revoking recovery plans. The Plan’s administrative review cadence is the operational mechanism for amendment.

• The Plan replaces the previous recovery plan for the species; the Appendix A evaluates the prior plan and sets out what was implemented and what was not. That provides a documented baseline for future amendments and reviews (Appendix A).

To summarise, the Plan’s amendment history is: 2006 plan -> 2013 review -> current Plan published April 2021 -> ministerial making late 2021/early 2022 with activation on registration. The Plan builds in a five‑year formal review and ongoing adaptive management as the principal mechanism by which content will be amended or superseded.

The recovery plan and instrument as provided do not record any litigation history. The text contains no references to legal proceedings, court decisions, or statutory litigation concerning the Mahogany Glider recovery plan, its maps, or its prior implementations. Appendix A evaluates prior plan performance and lists impediments to implementation (lack of funding, mapping deficits, extreme weather), but does not mention legal challenges.

What the Plan does reference that could be the subject of judicial or administrative review (but which the Plan itself does not litigate)

• EPBC Act assessment decisions: The Plan is intended to feed into assessments under the EPBC Act Significant Impact Guidelines 1.1 (section 8.2). Decisions under the EPBC Act about whether particular actions are controlled actions, or about conditions attached to approvals, are subject to administrative law review and possibly merits or judicial review in appropriate circumstances. The Plan provides evidence and policy guidance that could be argued in litigation over approvals, but the document contains no instance of such litigation.

• Planning instruments and development approvals: The Plan anticipates eventual development of statutory planning instruments and impact assessment restrictions associated with Lot Reconfiguration and MCU applications (Action 1.5). Those future instruments, once made, could be the subject of disputes or review if they restrict land use or planning decisions.

• Property and compensation claims: The Plan contemplates protection mechanisms on private land and landholder incentives (Action 1.5; 7.1). If statutory instruments are later introduced that restrict use, affected landholders could mount administrative or judicial challenges under planning or compensation regimes. The Plan itself contains no such litigation record.

• Emergency measures and translocation/captive breeding triggers: The Plan calls for development of emergency triggers for translocation and captive breeding assessments (Objective 5). Decisions about whether to implement emergency ex situ measures could give rise to dispute, but there is no litigation recorded.

Because the Plan contains no litigation references, practitioners should review contemporaneous EPBC Act decisions and Queensland planning or vegetation case law for any disputes where the Plan has been invoked. The document functions as a policy instrument that parties may rely on in administrative decision processes that are themselves subject to review.

This section flags practical pitfalls, likely sources of uncertainty and points where the Plan’s language or structure may create implementation or legal surprises for users. Each item is grounded in the Plan text.

1. "Habitat critical to survival" is broad and dynamic. The Plan defines habitat critical to survival to incorporate any habitat where the species is likely to occur within its known distribution, newly discovered locations that extend range, and subpopulation areas and priority corridors (Summary 1.4; section 3.6). That is spatially extensive language that does not confine critical habitat to a small catalogue of parcels. For landholders and proponents, this means that absence of a prior known sighting is not a safe screen. The Plan also ties that concept to "Essential Habitat" under Queensland VMA (section 3.6), which can have clearing implications.

2. Aspirational performance measures with contingent funding. The Plan lists specific quantitative targets (e.g. revegetation of 25 ha across five corridors, removal of 200 km barbed wire in national parks, etc., Table 3 and Table 8). However these are presented as indicative and conditional on funding and negotiated partner commitments (section 7.1). The front matter disclaimer reiterates that stakeholders "have not necessarily committed to undertaking specific actions". Practitioners should distinguish between targets that are contractual obligations in funded instruments and those that are aspirational in the Plan.

3. Potential regulatory creep via planning instruments. The Plan proposes investigating and developing "mechanisms for protection of Mahogany Glider habitat on freehold tenures" and "specific impact assessment and restrictions for Lot Reconfiguration and Material Change of Use applications" (Action 1.5). Those are not yet enacted instruments but the Plan signals a possible future expansion of planning constraints. Developers should track follow‑on planning instruments closely.

4. Reliance on voluntary landholder uptake and incentives. Many key interventions (grazing regime changes, fencing replacement, revegetation, fire regime adjustments) are to be delivered through landholder engagement and incentives (Action 1.1, 1.4). Where private landholders decline participation, the Plan notes implementation gaps could persist. The Plan anticipates funding via offsets, donations and philanthropic sources (Action 3.2) rather than relying solely on statutory obligations.

5. Gap metric (30 m average glide distance) is used as a planning rule of thumb. The Plan repeatedly uses ~30 m as the average glide distance and 60 m as a minimum corridor width for effective use (sections 3.6, 4.2.6, 8.3.2). This biological metric is operationalised in the Plan and could be used in impact assessments, but it is a species average and dependent on tree height, launch trees and landscape conditions. Applying it rigidly without site‑specific assessment risks mischaracterising impacts.

6. Monitoring and data burdens on small groups. The Plan requires integration of monitoring programs, data uploads to WildNet and training for contributors (Action 2.2). NGOs, community groups and small First Nations organisations may face resource costs to comply with monitoring expectations absent funded support (Action 2.1; Table 8 shows indicative budgets but many actions rely on partners to deliver).

7. Emergency triggers for translocation/captive breeding are intentionally non‑prescriptive. The Plan asks for development of triggers, feasibility assessments and protocols (Actions 5.1-5.4). Until those triggers are defined, there is uncertainty about when and how emergency interventions will be launched. The Plan also cautions that a captive breeding program is not currently recommended but that triggers should be prepared (section 8.3.7).

8. Interaction with disaster clean‑up operations. The Plan warns that post‑cyclone clean‑up may damage den trees and habitat, and calls for post‑cyclone recovery strategy adoption across government (8.3.6). However disaster response is often time‑sensitive and delivered under emergency powers; operational alignment between emergency management and conservation planning can be difficult to achieve in practice.

9. The Plan’s success criteria mix absolute and programmatic indicators. For example, "connectivity has been restored within 5 priority corridors" is explicit and spatial, while "community recognition and support increased" is qualitative with numeric proxies in actions (Action 4.3). Funders and implementers will need to align on which indicators trigger further investment.

10. Data used for mapping and corridor selection will evolve. The Plan relies on habitat mapping (Jackson et al. 2011; 2018a; 2020). As monitoring improves, the mapped corridors and subpopulations might be revised, altering priorities and landholder obligations under any future statutory instruments (section 3.3-3.7; Appendix B).

In short, the Plan is operationally detailed but many obligations are contingent, programmatic, and rely on negotiated funding. Users should not assume the Plan itself instantly changes property rights; instead it alters the planning, assessment and funding landscape and signals where statutory measures may follow.

This section sets out concrete, source‑based steps for actors who need to align with the recovery plan’s objectives, whether they are landholders, proponents, infrastructure operators, local councils, or agencies. All recommendations below cite the Plan provisions that set out the expectation.

For developers and proponents (construction, MCU, lot reconfiguration, infrastructure upgrades)

• Consult the EPBC Act Significant Impact Guidelines 1.1 and the Plan’s guidance at section 8.2 prior to committing to clearing or construction. The Plan lists activities likely to be significant: clearing within corridors, removal of den trees (living or dead Myrtaceae trees with hollows, DBH ≥20 cm), creation of gaps exceeding glide distances (~30 m), and disturbance during breeding season (section 8.2).

• Use the Plan’s spatial products (Map 1: current distribution; Map 3: subpopulations and priority corridors) to screen project footprints early. If a footprint intersects mapped habitat critical to survival or priority corridors, engage with DAWE and DES early and account for potential EPBC referral obligations (Summary 1.4; sections 3.6; 8.2).

• Where vegetation removal is unavoidable, design avoidance first. If a launch tree must be removed, the Plan recommends mitigation such as installing glide poles or rope bridges to maintain connectivity and mitigate road kill risk (Action 1.4; 8.3.1-8.3.2). Ensure mitigation is installed per best practice guidance once developed.

• Time works to avoid disruption during critical breeding periods, recognising the breeding season runs from April to October (section 3.2.4) and that disruption of breeding can be a significant impact (section 8.2).

For private landholders and graziers

• Engage with local NRM groups (Terrain NRM, NQ Dry Tropics), Girringun, and MGRT to access extension programs and possible incentives for best practice grazing, fencing, weed control and revegetation (Action 1.1; Table 8). The Plan targets 500 ha for adoption of grazing regimes across subpopulations and sets performance measures for woody weed control and barbed wire removal.

• Replace high‑risk barbed‑wire top strands with plain wire or retrofits such as polypipe at launch tree crossing points (Action 1.1; 8.3.5). The Plan records past fencing replacement achievements and encourages funding mechanisms such as Nature Assist for cost reduction.

• Adopt the Plan’s best practice grazing guidelines once published: they will address stock density, fire interactions, and weed control to support tree recruitment (Action 1.1; 8.3.4).

• Participate in monitoring: submit sightings to the Terrain database and ensure data is shared with DES/WildNet as required (Action 2.2). Training and community engagement actions are part of the Plan and expected to be supported by NRM groups (Action 2.1-2.2).

For infrastructure operators (roads, rail, powerlines)

• Integrate the Plan’s guidance into asset planning, construction and maintenance manuals. The Plan calls for guidelines for infrastructure upgrades and maintenance designed to minimise habitat fragmentation and mortality (Action 1.5; 8.3.2).

• Retain priority "launch trees" where possible , the Plan defines these as trees with lateral branches >20 m above ground and recommends restricting gaps to less than average glide distance (~30 m) where feasible (section 8.3.2). Where clearance is necessary, fund and install glide poles, rope bridges, or canopy bridges at gap locations and known road‑kill sites (1.4; 8.3.1-8.3.2).

• Minimise overspray and unscheduled widening of easements to prevent creation of new dispersal barriers and weed incursions (section 8.3.2).

For local councils and planning authorities

• Use the Plan’s criteria when considering MCU and Lot Reconfiguration applications that fall within the species’ mapped distribution or priority corridors. The Plan specifically flags these application classes as having potential to incrementally worsen habitat loss and suggests developing specific impact assessment restrictions (Action 1.5; 4.2.1).

• Where possible, adopt or reference the Plan’s mapping and best practice guidance in local planning schemes and development control measures to provide clarity to applicants and reduce assessment friction (section 8.1; Action 1.5).

• Fund and facilitate landholder incentive programs and community engagement actions described in the Plan (Actions 1.1; 4.1-4.4). Table 8 sets out indicative cost shares and shows local councils may be partners.

For researchers and universities

• Support the Plan’s monitoring and genetic studies (Actions 2.1-2.4). The Plan explicitly seeks a program that enables community groups to contribute long‑term data and to assess genetic structure among subpopulations.

• Publish and share findings that update habitat mapping and corridor priorities; the Plan foresees updates as data improves and maps can be revised (section 7.2; 3.3-3.7).

For First Nations organisations and Girringun

• Engage in MGRT processes and co‑design monitoring and on‑country management as the Plan anticipates First Nations involvement and cultural knowledge inclusion where negotiated (section 7.5; Actions 4.2).

For all actors , governance and funding steps

• Expect to negotiate a more detailed implementation plan that specifies partner contributions, annual budgets and reporting milestones as required by the MGRT. Section 7.1 requires that an implementation plan be developed to identify and commit partners to agreed actions.

• Track the five‑year formal review trigger and be prepared to provide monitoring data, evidence of adoption of best practice or reasons for non‑adoption. The Plan uses the review to inform adaptive changes and reassess conservation status (section 7.2).

• Use the Plan as an evidentiary reference for EPBC Act referral decisions. The Plan provides concrete biological thresholds (e.g. DBH ≥20 cm for den trees, average glide distances) that are appropriate to cite in assessments (section 8.2; 8.3.2).

Practical checklist (immediate operational steps)

• Screen the project or property against Map 1 and Map 3; identify whether habitat critical to survival or priority corridors are present.
• If present, commission targeted ecological surveys to identify den trees (DBH ≥20 cm), launch trees and measure gap distances.
• Where actions could cause gaps >30 m or den tree removal, engage early with DAWE and DES to determine referral obligations and mitigation options.
• Document avoidance measures and, where necessary, propose mitigation (glide poles, rope bridges), revegetation plans and fencing retrofits with costed schedules.
• Join or liaise with local NRM partners to access training and funding opportunities and to register sightings in the Terrain database and WildNet.

These steps align with the Plan’s operational expectations and, where implemented in funded agreements, will bring actions in line with the Plan’s performance measures (section 6.2.3; Table 8).