Threat Abatement Plan for Predation by the European Red Fox

The TAP’s architecture is conceptual and pragmatic rather than prescriptive. Key concepts used repeatedly in the text are these.

Threat abatement plan: defined in the glossary as “a plan providing for the research, management, and any other actions necessary to reduce the impact of a listed key threatening process on affected species and ecological communities.” The TAP is the instrument that sets out those actions for the red fox (Glossary; 1 Introduction).

Key threatening process: fox predation is a process listed under the EPBC Act. The TAP attaches to that listing and directs targeted responses to reduce its impact (1.2.1).

Prioritisation: the TAP instructs decision‑makers to target resources to “priority areas” selected by evidence of species significance, degree of threat posed by foxes relative to other threats, feasibility of action and cost‑effectiveness (Action 2.1). Actions carry explicit priority ratings and timeframes to guide resource allocation (Objective tables).

Scale and integration: the TAP repeatedly emphasises that regional NRM plans and site‑based plans are the best operational scale for implementation; it promotes integrated pest control (multi‑species programs) because single‑species control can produce unintended ecological outcomes (1.1; Objective 3, Actions 3.2-3.4).

Prevention, containment and eradication: the plan distinguishes three strategic responses. Prevention and monitoring at invasion edges is important; eradication is targeted at islands and Tasmania where feasible and cost‑effective; containment and long‑term suppression are the pragmatic response on the mainland (1.2.3; Objective 1 Actions 1.1-1.4).

Monitoring and evaluation: the TAP places significant emphasis on development of simple, cost‑effective monitoring protocols for foxes and affected native species (Actions 3.1 and 3.5) and on alignment with the National Monitoring and Evaluation Framework (NRMMC 2003) (3.3).

Technical development: the TAP identifies specific R&D priorities: improved bait media, canid‑specific toxins, M44 ejectors, bait delivery stations, fertility control and genetic monitoring (Objectives 3-4, Actions 3.1, 4.1-4.2). It also promotes the use of genotyping of scats/hairs and population genetic analysis to track invasion routes and abundance (1.2.3; Action 3.1).

Humaneness and standards: the plan requires promotion of humane methods and adoption of model codes of practice and the National Competency Standards for Vertebrate Pest Management (Action 4.7; Objective 4).

Cost focus: the TAP acknowledges that implementation is resource dependent and provides concrete cost examples to frame expectations: aerial baiting of ~35,000 km2/year costs about $1.3 million, and exclusion fencing can cost up to $10,000 per km (3.1).

Species focal list: Appendix A lists named threatened and unlisted species and ecological communities potentially affected by fox predation. The list is “indicative and not comprehensive” and is intended to guide prioritisation (Appendix A; 3.3).

Collectively these concepts create a plan that is action‑oriented (20 specified actions), evidence‑oriented (priority based on species significance and feasibility), and designed to be implemented through coordination rather than top‑down regulation (1.1; 3.2).

The TAP identifies a broad range of stakeholders who will be affected in practice, explicitly naming categories rather than creating legal obligations.

Australian Government (DEWHA and Commonwealth land managers)

• DEWHA’s role is central: it develops TAPs, facilitates implementation, establishes a TAP implementation team and will implement the plan on Commonwealth land (1.1; 3.2). The Australian Government may allocate funds for key national environmental priorities and relevant TAP actions (3.1-3.2). DEWHA also establishes national databases, extension material and coordination mechanisms.

State and territory governments and statutory agencies

• The plan anticipates coordination with state/territory conservation and pest management agencies, and with the Vertebrate Pests Committee under the Australian Pest Animal Strategy (1.1; 3.2). State TAPs (for example NSW NPWS’ red fox TAP is referenced) and local programs are the vehicle for on‑ground work (1.2.4).

Regional NRM bodies and local government

• The TAP designates regional NRM plans and site‑based plans as the best operational context for developing and implementing control programs and contingency plans; regional bodies will therefore be implementers and decision‑makers for local actions (1.1; Objective 2).

Private landholders and leaseholders

• The plan expressly recognises the role and limitations of private landholders and leaseholders in on‑ground control and asks that implementation supports their efforts through incentives, negotiated agreements and partnerships (1.1; Action 2.3). It also flags the need to consider Indigenous communities’ views in implementation (3.2).

Researchers and industry

• Universities, CRCs (the text mentions the Invasive Animals Cooperative Research Centre), and other R&D providers are affected by the plan’s research priorities (genotyping, bait development, fertility control) (1.2.3; Actions 3.1, 4.1-4.2).

Community groups and volunteers

• The TAP anticipates community groups and volunteers will be participants in regional control programs and extension activities, and includes stakeholder awareness and extension (Objective 5; Action 5.1).

Conservation‑listed species and ecological communities

• Appendix A lists specific threatened species (critically endangered, endangered, vulnerable) and unlisted taxa that may be adversely affected. These named taxa are the intended beneficiaries of targeted control programs and hence guide prioritisation of resources (Appendix A).

Private business and primary producers

• The TAP recognises that pest control intersects with primary production and that R&D and control programs should integrate interests of both primary production and environmental conservation (1.1). This implies private industry (e.g. pastoralists, farmers) will face costs or opportunities from coordinated control programs and any incentives offered.

Who pays and who decides

• The TAP is explicit that investment will be determined by stakeholder resource commitments, with Australian Government funds potentially available for national priorities (3.1-3.2). Decision authority for on‑ground action is distributed: DEWHA coordinates and supports, but state/territory, regional NRM, landholders and communities largely decide implementation specifics in their tenures (1.1; 3.2). The Vertebrate Pests Committee is responsible for implementation of the Australian Pest Animal Strategy, into which the TAP feeds (1.1).

Who is not directly constrained by the TAP

• The TAP does not itself impose statutory duties or criminal penalties on any of these actors; it is a coordination and guidance instrument under the EPBC Act framework (1.1). That means affected parties are influenced through policy, funding, standards and technical guidance rather than new statutory prohibitions within this document.

This TAP does not create novel statutory duties, licences or explicit private rights. It operates as a central policy framework under the EPBC Act to guide and coordinate actions by governments and non‑government actors. The operative duties and rights therefore follow from the instruments, programmes and administrative arrangements it interacts with, rather than from the TAP text itself.

Administrative and coordination duties

• DEWHA is tasked with developing TAPs, facilitating implementation and supporting a TAP implementation team; those are administrative obligations described in the plan (1.1; 3.2). The Australian Government is required by the EPBC framework to consider TAPs when addressing key threatening processes; here, implementation on Commonwealth land is specifically identified (3.2).

Priority‑setting duties (informal)

• The TAP directs that priority areas should be identified on a scientific basis (Action 2.1), that islands or isolated sites be assessed and contingency plans developed (Actions 1.1-1.3), and that monitoring protocols be developed and applied (Action 3.1). These are framed as actions for agencies and stakeholders to implement. They create administrative expectations for agencies that accept implementation funding or leadership roles.

Standards and compliance expectations

• The plan requires promotion and continued adoption of model codes of practice and standard operating procedures for humane management of foxes and their recognition under the National Competency Standards for Vertebrate Pest Management (Action 4.7). While this is not itself enforceable law, competence standards and model codes typically feed into procurement, funding eligibility and operational conditions administered by governments.

Research and monitoring obligations (programme levers)

• Actions 3.1, 3.5 and 4.1-4.2 set research and monitoring priorities. Funding recipients (government or grant‑funded researchers) will be expected to follow those priorities. The TAP also requires alignment with national monitoring frameworks (3.3), which can affect reporting obligations where funds or approvals are tied to DEWHA or NRMMC processes.

Rights and entitlements

• The TAP does not confer property rights or compensation rights. It does specify that Australian Government funds may be available for TAP actions and regional priorities (3.1), implying potential eligibility for grants or co‑investment for those who align with TAP objectives. The TAP also envisages incentives, partnerships and negotiated agreements with private and leasehold lands for on‑ground control (Action 2.3), which are voluntary mechanisms rather than enforceable rights.

No direct penalties in the TAP

• The document contains no penalty regime or criminal sanctions. Legal obligations and penalties for harming threatened species or breaching EPBC‑regulated approvals remain in the EPBC Act and subordinate instruments, but this TAP itself does not create statutory offences or penalties. Its effect on behaviour derives from funding, coordination, technical guidance, and the influence of the EPBC Act process under which it was made (1.1).

Summary

• The TAP creates administrative expectations for government agencies and guidance for practitioners: identify priorities, apply national protocols, integrate pest control, develop contingency plans and adopt humane practices. Compliance is primarily achieved through policy levers,funding, guidance, standards and inter‑governmental coordination,rather than through new statutory duties within the text of the TAP.

The TAP document does not establish novel criminal offences, civil penalties or a standalone enforcement regime. It is a strategic policy document prepared under the EPBC Act framework and structured to guide research, management and coordinated action. The TAP therefore operates through non‑coercive mechanisms: funding decisions, guidance, standards, intergovernmental coordination and stakeholder engagement (1.1; 3.2).

What enforcement mechanisms are expressly in the TAP

• The TAP sets expectations for adoption of model codes of practice and National Competency Standards (Action 4.7). Adoption of those codes will influence operational practice and may be incorporated into contracts, grant conditions or licensing arrangements administered by agencies, but the TAP does not itself specify enforcement sanctions for non‑adoption.

Indirect enforcement via other instruments

• Practical enforcement or sanctioning for activities that harm EPBC‑listed species or communities would continue to come from the EPBC Act and associated regulations. The TAP does not substitute for the EPBC Act; it complements it by providing priority actions and a strategic framework (1.1). Where TAP‑guided work is tied to funding, failure to meet contractual or grant conditions informed by TAP priorities could produce administrative enforcement (suspension of funds, termination of agreements), but those are contractual or administrative, not statutory penalties imposed by the TAP itself.

Monitoring and evaluation as an accountability mechanism

• The TAP emphasises development of national monitoring protocols, indicators and evaluation under the NRMMC monitoring and evaluation framework (3.3). These systems create transparency and public accountability. If monitoring shows failure to meet performance indicators, that is intended to guide adaptive management and reprioritisation rather than to trigger direct penalties within the TAP (Performance indicators under each Objective).

Operational consequences for implementers

• Practitioners and agencies accepting public funds or participating in coordinated programs will face practical consequences if they do not meet TAP‑linked standards: loss of funding, lower priority status in national coordination, reduced access to technical support, or reputational costs. The TAP is explicit that achievement is resource‑dependent and that DEWHA will facilitate partnerships and co‑investment (1.1; 3.1-3.2).

Summary

• The TAP itself contains no penal provisions. Enforcement pressures arise from companion statutory instruments (the EPBC Act), contractual conditions on funding, national standards and codes of practice recommended by the TAP, and the monitoring and evaluation processes (3.3) designed to report progress against the TAP’s performance indicators.

The TAP is an instrument produced within the EPBC Act framework and is expressly designed to operate alongside and feed into a network of other policy frameworks, statutory arrangements and non‑statutory guidelines. The document refers repeatedly to those interactions.

EPBC Act

• The TAP was continued in force under the EPBC Act 1999 and derives its standing from the Act’s requirement for approaches to listed key threatening processes (cover page; 1 Introduction; 1.1). The TAP provides the research and management actions necessary to abate that listed process. The EPBC Act remains the primary statute for legal protection of threatened species and ecological communities identified in Appendix A.

Australian Pest Animal Strategy and Vertebrate Pests Committee

• The TAP is to be implemented in the broader context of the Australian Pest Animal Strategy (2007) and the Vertebrate Pests Committee, which comprises representatives from Australian, state and territory governments and is responsible for implementation of that strategy (1.1). This links TAP priorities into intergovernmental pest‑management fora.

Australian Biosecurity System for Primary Production and the Environment (AusBIOSEC)

• The plan is to operate under the overarching framework of AusBIOSEC, integrating biosecurity and pest management for both primary production and environmental outcomes (3.2). That links the plan to biosecurity policy processes that often have statutory dimensions for import controls and movement of risk materials.

National Monitoring and Evaluation Framework (NRMMC)

• Monitoring and evaluation are expected to conform with the National NRM monitoring framework established by the Natural Resource Management Ministerial Council (NRMMC 2003). This creates an interaction between TAP reporting and the broader national monitoring arrangements (3.3).

State and territory laws and plans

• The TAP anticipates that state and territory pest management rules, subsidies, licensing and animal welfare statutes will remain operative. It invites coordination with existing state TAPs and regional NRM plans (1.1; 1.2.4). For example, NSW NPWS’ Threat abatement plan for predation by the red fox is cited as a complementary instrument (1.2.4).

Model codes, competency standards and SOPs

• The TAP promotes adoption and adaptation of model codes of practice and standard operating procedures for humane management of foxes, including their recognition under the National Competency Standards for Vertebrate Pest Management (Action 4.7). Where these codes become references in funding or procurement, they will interact functionally with administrative law and contractual regimes.

Pesticide registration and agricultural chemical law

• The TAP’s research and operational recommendations (Action 4.1-4.2) discuss toxins such as 1080, canid‑specific toxins and other delivery systems. The TAP does not alter pesticide registration or approvals, so any operational use of toxins remains subject to registration, label instructions, and state/territory chemical control laws and animal welfare rules.

Property and tenure law

• The TAP’s measures for islands, fencing and landholder incentives (Objective 1 and Action 2.3) interact with land tenure arrangements, leasehold regulations and private property decision‑making. The plan recognises that partnerships and negotiated agreements on private or leasehold land are needed rather than top‑down statutory compulsion (Action 2.3).

Summary

• The TAP is a coordinating policy instrument that complements and interacts with the EPBC Act, biosecurity and pest animal strategies, state/territory pest laws, pesticide regulation, national monitoring frameworks and competency standards. It does not amend or supersede statutory laws; rather, it informs funding priorities, best practice standards and intergovernmental coordination.

The compilation header and endnotes provide the amendment and registration history relevant to this document. Key points drawn from the endnotes and front matter are:

• The plan published here is the 2008 TAP prepared by the Department of the Environment, Water, Heritage and the Arts (DEWHA) and is a replacement for the original 1999 TAP (1 Introduction; 1.2.4). The document states it replaces the TAP for foxes published in 1999 (EA 1999a).

• Compilation details at the front indicate Compilation No. 1, compilation date 1 October 2008, and that the compilation includes amendments up to F2009L00064 (cover page and “About this compilation”).

• Endnote 3 provides two registration/commencement entries. It lists: • Threat Abatement Plan for Predation by the European Red Fox, registration 15 Oct 2008 (F2008B00667), commencement 2 July 1999; and • Threat Abatement Plan for Predation by the European Red Fox 2008, registration 12 Jan 2008 (F2009L00064), commencement 1 October 2008. These entries reflect the compilation metadata and the replacement role of the 2008 TAP (Endnote 3).

• Endnote 4 indicates the Threat Abatement Plan for Predation by the European Red Fox was revised and shows the entry “rs F2009L00064”, signalling a repeal and substitution or replacement associated with that instrument (Endnote 4).

• The plan also records the 2004-05 Bureau of Rural Sciences review (Hart 2005) as the basis for changes to the original 1999 TAP and for retaining largely the same objectives while updating actions and implementation advice (1.2.4).

Practical implication

• For legal and administrative purposes, the TAP is the 2008 version; it supersedes the 1999 TAP and contains updated actions and priorities. The compilation notes that uncommenced amendments and modifications may exist and that readers should consult the legislation register for details (front matter, “This compilation” notes).

Caveat

• The TAP’s endnotes show compilation and registration metadata rather than legislative amendments of a statute. The plan is a statutory instrument in the sense it was made under earlier statutory authority and continued under the EPBC Act, but the amendment history here documents the TAP versions themselves rather than amendments to the EPBC Act.

The TAP contains no case law citations and does not record any judicial decisions concerning the plan itself. The document’s references are to scientific reports, reviews and policy materials (e.g. Hart 2005, Saunders & McLeod 2007, BRS reports), not to litigation (References).

What the TAP records

• The document records reviews and scientific evaluations (e.g. Hart 2005 review of 1999 TAPs) and cites scientific literature on fox impacts and control methods. It does not identify any court decisions, tribunal determinations or legal challenges to the TAP or to specific actions listed (References; 1.2.4).

What this means in practice

• Because the TAP is a policy instrument that sets national priorities and guidance, legal disputes about obligations or enforcement would most likely be routed through the EPBC Act, administrative law (judicial review of agency decisions), pesticide regulatory law, or state/territory animal welfare and pest legislation. The TAP itself creates no enforcement mechanism that could be directly litigated; litigation would typically concern whether particular government decisions that rely on the TAP complied with statutory duties, procedural fairness, or evidenced reasonable administrative exercise of power. None of that litigation history is discussed in the TAP.

Recommendation for due diligence

• Practitioners seeking case law or judicial reactions to TAP‑driven decisions should search EPBC Act judicial review decisions, administrative determinations and case law concerning threatened species approvals, pesticide approvals, or funding decisions. The TAP does not provide that record.

Practical pitfalls, implementation risks and common misunderstandings that arise from reading and applying this TAP are listed below, grounded in the document’s own statements.

It is guidance, not a binding statute

• The TAP is a national policy framework under the EPBC Act but does not itself impose statutory criminal or civil penalties. Expectation creation (priority setting, monitoring) is the mechanism, not compulsion. Practitioners sometimes misinterpret TAP‑actions as legally mandatory; they are policy directions intended to be implemented by governments and partners (1.1; Key duties and rights).

Eradication vs suppression: feasibility caveat

• The TAP explicitly states continental eradication is currently infeasible and that objectives therefore focus on suppression and targeted eradication of islands/Tasmania where feasible and cost‑effective (1.2.3; Objective 1 Actions). Planning for eradication without considering this feasibility statement can misallocate resources.

Resource dependence and uncertain funding

• The TAP repeatedly notes implementation is resource dependent (3.1). The document provides concrete cost examples (aerial baiting ≈ $1.3 million per 35,000 km2/year; fencing up to $10,000/km) to signal ongoing high costs. Expectation mismatch between the TAP’s ambitions and available funding is a material implementation risk.

Monitoring difficulty and attribution problem

• The BRS review found it is difficult to link TAP outputs to reduced impacts because of paucity of national data and monitoring inconsistencies (1.2.4). The TAP therefore emphasises development of national monitoring protocols (Action 3.1) but implementing robust, comparable monitoring over large jurisdictions is technically and politically hard. This complicates claims about TAP effectiveness.

Reinvasion and spatial scale problem

• Fox populations recover rapidly, often through reinvasion, and successful control at a site often requires coordinated control in adjacent areas (Objective 2; Action 2.2). Site‑level efforts that fail to manage surrounding reinvasion sources are liable to fail.

Unintended ecological effects

• The TAP warns control in isolation can produce unintended outcomes (e.g. mesopredator release) and calls for integrated multi‑species programs and research into interactions between foxes, cats, wild dogs and rabbits (Actions 3.2-3.4). Single‑species campaigns without ecological assessment risk shifting predation pressure rather than reducing net threat.

Humaneness, regulatory approvals and public acceptance

• The TAP promotes research into new toxins and delivery methods (Action 4.1-4.2) including canid‑specific approaches and fertility control. However, any operational use of new toxins or methods will require pesticide registration, animal welfare assessment and public consultation. The TAP does not override those processes; developers must navigate them.

Dependence on stakeholder cooperation

• The TAP’s success rests on coordination among landholders, local government, state/territory agencies and the Australian Government (1.2.5). Where cooperation is limited, the plan’s measures (incentives, negotiated agreements) may not be sufficient and on‑ground outcomes will lag.

Islands and contingency planning complexity

• Action 1.2 directs contingency planning for islands and isolated mainland ‘islands’. That requires detailed biosecurity, social licence, and logistics planning. The TAP acknowledges DEWHA is establishing a national database for offshore islands, but data gaps can delay or misdirect priority selection (Objective 1; Action 1.1).

Scope creep and multi‑threat context

• The TAP focuses on fox predation but repeatedly notes foxes interact with habitat loss, other pests, disease and fire regimes. Effective investment may need to address these other threats; funding constrained to fox control alone may deliver limited biodiversity gains.

Data reliance and species list limits

• Appendix A is explicitly “indicative and not comprehensive.” Practitioners must not treat it as exhaustive; local species at risk may be absent from the list but still require protection (Appendix A statement).

Summary

• The TAP is clear about its own limitations: funding constraints, monitoring challenges, reinvasion risks, and the need for integrated multi‑species management. Practical implementation requires careful prioritisation, robust monitoring design, inter‑jurisdictional cooperation, and alignment with pesticide, biosecurity and animal welfare regulatory requirements.

The TAP sets expectations and practical actions rather than prescriptive legal requirements. For practitioners (state agencies, regional NRM bodies, landholders, contractors, researchers) who want to align with the TAP and be eligible for associated funding and partnership support, the following concrete steps are grounded in the TAP text.

1. Use the plan’s prioritisation framework (Action 2.1)

• Identify priority areas for fox control using the TAP criteria: significance of affected populations/ecological communities, degree of fox threat relative to other threats, cost‑effectiveness of maintaining fox populations below a damage threshold, and feasibility of remedial action (Action 2.1). Document the evidence base used for prioritisation (species distributions, habitat risk maps, fox distribution).

2. Align monitoring to national protocols (Actions 3.1 and 2.2)

• Adopt or participate in development of national, simple and cost‑effective monitoring methods for fox abundance and affected species (Action 3.1). Where available, apply the NRMMC monitoring and evaluation framework for reporting outcomes (3.3). Keep pre‑ and post‑control monitoring records, follow genotyping approaches where appropriate, and report results to regional and national databases.

3. Integrate multi‑species control (Actions 3.2-3.4)

• Coordinate fox control with programs for feral cats, wild dogs and rabbits. Consider likely ecological interactions and the potential for mesopredator release. Plan concurrent or phased interventions to minimise unintended consequences (Actions 3.2-3.4).

4. Prepare island contingency and eradication plans (Objective 1 Actions)

• For islands and isolated mainland refugia, collate data on conservation values and invasion risk (Action 1.1), develop contingency plans for prevention, monitoring and rapid response (Action 1.2), and implement containment/eradication actions where feasible (Actions 1.3-1.4). Ensure plans account for biosecurity, logistics, community engagement and post‑eradication monitoring.

5. Follow model codes and competency standards (Action 4.7)

• Ensure personnel delivering control are trained to National Competency Standards for Vertebrate Pest Management and that operations follow recognised model codes of practice and SOPs for humane management (Action 4.7). Maintain training records and accreditation evidence.

6. Document cost‑benefit and feasibility analyses (Actions 1.4; 4.3)

• For proposed eradication (e.g. island projects) or costly infrastructure (exclusion fencing), prepare explicit feasibility and cost‑effectiveness analyses, referencing the TAP’s cost examples (3.1) and the TAP’s call for testing fence designs and disseminating cost data (Action 4.3).

7. Use incentives and negotiated agreements on private lands (Action 2.3)

• Where programs rely on private or leasehold land, put in place negotiated agreements and incentive structures (other than bounties) to encourage sustained control in adjacent areas to prevent reinvasion (Action 2.3). Keep records of agreements and incentive payments for audit and evaluation.

8. Participate in research priorities and data sharing (Actions 3.1, 4.1-4.2)

• Contribute to or adopt R&D outcomes on improved baiting media, target specificity and non‑lethal approaches. Share genetic or monitoring data with national databases (the TAP mentions the Invasive Animals CRC genetic database development) to improve population genetics understanding and invasion‑route identification (1.2.3; Action 3.1).

9. Budget for ongoing costs and plan for sustainability (3.1)

• Factor in ongoing high costs and operational requirements. Use the TAP’s example figures for planning (aerial baiting costs and fencing costs) as a conservative budget guide, and seek co‑investment and multi‑year commitments.

10. Communicate and provide extension (Action 5.1)

• Develop extension material on TAP objectives, best practice control techniques, humane methods and the rationale for priority areas, and distribute to landholders, community groups and local government (Action 5.1). Document outreach activities and uptake metrics for reporting.

Recordkeeping checklist for auditors and funders

• Priority area maps and selection rationale (Action 2.1).
• Pre/post‑control monitoring data and methods (Action 3.1).
• Training and competency certificates for operational staff (Action 4.7).
• Contractual records for incentive agreements and partnerships on private land (Action 2.3).
• Feasibility and cost‑benefit analyses for eradication or infrastructure projects (Action 4.3; 1.4).
• Data sharing agreements and genetic monitoring outputs when used (Action 3.1).

Legal compliance overlays

• Ensure all pesticide use, toxins and delivery systems comply with registration and label instructions and relevant state/territory rules. Secure any necessary approvals before deploying new toxins or devices (Actions 4.1-4.2).
• Align animal welfare obligations to applicable state/territory law and to the TAP’s humane standards (Action 4.7).

Summary

• To be “compliant” with the TAP in practice means to implement TAP actions where relevant and feasible, to follow the plan’s priority and monitoring guidance, to adopt the recommended standards and training, and to document outcomes. Because the TAP influences funding and coordination, proactive alignment will aid access to joint programs and grants and reduces risk of disjointed local efforts that fail due to reinvasion or unintended ecological effects (Objective 2, Objective 3).