The instrument centres on a small set of statutory and administrative concepts explicitly invoked in the text: "adoption" under section 269A, "recovery plan", "addendum" pursuant to subsection 269A(7), "critical habitat", and references to sections 207A and 270(2)(d) of the EPBC Act. The document uses these concepts in specific ways.

• Adoption under s 269A: The instrument repeatedly states it is made "under section 269A of the Environment Protection and Biodiversity Conservation Act 1999", and it uses the statutory form of adoption. The instrument therefore relies on the Ministerial power or procedural route in s 269A to recognise State recovery plans as recovery plans under the Commonwealth Act. The instrument also invokes "Sub section 269A (7)" when attaching addenda, indicating the Minister is using a power or process in that subsection to modify or add text to adopted plans.

• Recovery plan: The phrase "recovery plan" is used in two senses in the instrument. First, to identify pre-existing State documents (for example, "Davidson’s Plum Recovery Plan"). Second, to indicate that those documents are being adopted as recovery plans under the EPBC Act. The instrument thus creates a bridge: the content authored by State agencies becomes, by adoption, a Commonwealth recovery plan document. The recovery plans themselves vary: some are labelled "Interim Recovery Plan (2004-2009)", others have specified date ranges or single-year publication dates.

• Addendum and performance criteria: For Davidsonia jerseyana the addendum is detailed. It inserts a modified "Recovery Objectives, Actions and Performance Criteria" section, and it sets quantifiable targets,"The number of individual plants within wild populations and/or the number of wild populations have increased by 10 percent or more over the five-year life of the recovery plan under the EPBC Act" and "The area under conservation management agreements has increased by 10 percent or more over the five-year life of the recovery plan under the EPBC Act." These are explicit, time-bound performance measures attached to the adopted plan.

• Critical habitat clarification: For the WA plans, the instrument contains a textual addendum under the heading "Critical Habitat" that describes what the plan's mapped or identified "critical habitat" includes (areas a set distance around known populations, similar habitat, areas that may have contained the species historically). Critically, the instrument then states: "These areas identified in the plan do not represent areas of critical habitat as defined under section 207A of the EPBC Act, nor do they represent habitats that are critical to the survival of the species identified pursuant to Section 270(2)(d) of the EPBC Act." It goes on, "Habitats identified in Section 270(2)(d) are limited to the area of occupancy if known populations." That is a ministerial textual qualification, inserted as an addendum to the State recovery plans.

• Commencement: The instrument expressly records that the recovery plans "will come into force on the date of signing". This fixes an immediate commencement for the documents as federal recovery plans.

These concepts interplay: the Minister uses s 269A adoption to treat State products as federal recovery plans, but simultaneously uses the addendum mechanism to alter or circumscribe certain plan elements (numerical performance targets for Davidsonia; a restriction on the legal status of "critical habitat" in the WA plans). The instrument therefore performs both recognition and adjustment functions, turning State outputs into Commonwealth recovery plans while refining particular content elements.

The instrument identifies specific species and State agencies, and by adopting State recovery plans as Commonwealth recovery plans it creates practical relevance for several groups. The instrument itself lists the affected species explicitly (e.g. Davidsonia jerseyana; Pseudemydura umbrina; Parantechinus apicalis; Acacia taxa; orchids; Eucalyptus species; Philotheca basistyla; Villarsia calthifolia; and others). That list determines which species are the subject of the adopted recovery plans.

Directly named decision-makers and public bodies:

• The Minister for the Environment and Heritage is the signatory and adopting authority in this instrument (Ian Campbell, 18 August 2005).
• State departments/agencies of New South Wales and Western Australia are the authors of the recovery plans and thus the sources of the adopted content (e.g. NSW Department of Environment and Conservation; Department of Conservation and Land Management, Wanneroo, WA).

Practitioners and private actors likely affected (implicit from adoption):

• Landholders and occupiers within areas identified by the State plans. The instrument adopts plans that identify habitats, areas around populations, and outline objectives and actions; such identification is likely to bear on land management choices where those plans apply.
• Developers, resource companies and other project proponents whose activities may interact with habitats or populations of the listed species. They will have a stake in how the Commonwealth treats recovery plan content for referral, assessment and approvals under the EPBC Act framework (the instrument itself does not describe approval pathways but places recovery plans into the Commonwealth rubric).
• Conservation and natural-resource NGOs, researchers and consultants engaged in monitoring, restoration, or the negotiation of conservation management agreements. The Davidsonia addendum explicitly references "conservation management agreements" and sets a quantitative target for area under those agreements.
• State agencies that produced the plans: adoption makes their documents the Commonwealth recovery plan, creating a Commonwealth-level status that will affect reporting and intergovernmental coordination.

Groups whose legal position is clarified by the instrument:

• Those concerned with habitat protection in WA: the instrument expressly states that plan-identified areas do not represent critical habitat as defined under s 207A and are not "habitats that are critical to the survival" under s 270(2)(d). That statement affects any party relying on plan maps to claim automatic equivalence with s 207A critical habitat or s 270(2)(d) habitat.

Not named but plausibly affected:

• Commonwealth enforcement or compliance officers, because adopted recovery plans will form part of the Commonwealth's recovery-planning framework. The instrument, however, does not purport to create or define enforcement instruments in this text.

Who pays: The instrument does not itemise budgets, funding sources or imposed fees. It records the adoption of plans authored by State bodies (which implies State resources were used to prepare the plans), and it references "conservation management agreements" as a performance measure for Davidsonia; increased area under such agreements may shift costs onto landholders, conservation groups or government budget lines depending on how agreements are negotiated. The instrument itself contains no appropriation or funding provision.

Who decides: The immediate decision recorded in the instrument is the Minister's adoption of the State plans under s 269A, and the Minister's insertion of addenda pursuant to s 269A(7). The plans, once adopted, become the Commonwealth recovery plans at least as to their texts and addenda in this instrument. The instrument thus places the Minister centrally as the decision-maker for adoption and qualification of the State documents.

The instrument’s text is declaratory: it adopts State recovery plans and inserts addenda. It does not itself set out express civil obligations or define statutory penalties. Nevertheless the instrument creates, or at least records, duties and rights in the following ways.

Duties arising from adopted plan content:

• Recovery objectives, actions and performance criteria in the Davidsonia jerseyana addendum create explicit, measurable expectations. The addendum requires that, over the five-year life of the recovery plan under the EPBC Act, (a) the number of individual plants within wild populations and/or the number of wild populations increase by 10 per cent or more, and (b) the area under conservation management agreements increases by 10 per cent or more. Those are obligations framed as recovery criteria; they impose an administrative performance standard for the adopted plan. The instrument does not itself state which body must achieve these outcomes, but the addendum becomes attached to the federally adopted recovery plan, so responsibility for reporting, monitoring and the coordination of actions will likely be exercised by the relevant Commonwealth and State agencies named in the adopted materials.

• The State plans adopted (both NSW and WA) contain actions and interim recovery measures (many are titled "Interim Recovery Plan 2003-2008" or "2004-2009"). Those original plan actions (as authoritatively identified in the instrument) will form the substance of the adopted recovery plan. Where the plans call for specific actions (e.g. surveys, fencing, control programs, habitat restoration, management agreements), those measures are incorporated into the adopted federal recovery plan as text.

Rights and procedural features recorded:

• The instrument is explicit that the Minister adopted the plans pursuant to s 269A and used subsection 269A(7) to add text. That procedural step is recorded and thus creates an administrative record of ministerial action which may be relied upon by parties engaging with the recovery plan (for example, in negotiations over management agreements or in project assessment processes where the presence of a federal recovery plan is relevant). The instrument also records the date of entry into force (the signing date), which fixes the temporal starting point for any obligations or performance periods embedded in the plans (notably the five-year life of the Davidsonia recovery plan performance measure).

Limitations and clarifications that alter duties:

• The WA addendum explicitly narrows the legal scope of plan-identified "critical habitat". The instrument states these areas "do not represent areas of critical habitat as defined under section 207A", nor "habitats that are critical to the survival ... pursuant to Section 270(2)(d)". The addendum also says "Habitats identified in Section 270(2)(d) are limited to the area of occupancy if known populations." In practice this reduces the likelihood that rights or constraints that flow from an assertion of statutory critical habitat under s 207A or the s 270(2)(d) threshold will be triggered merely because the state plan maps broader buffer or historical habitat areas. That is a ministerial clarification built into the adopted plan, and it narrows the legal characterisation of the plan-identified areas.

What the instrument does not itself do:

• The instrument does not itself create offences, civil penalties, or explicit compliance mechanisms. It does not specify a compliance timetable for each action beyond the Davidsonia five-year performance period. The instrument does not define technical or measurement standards (for example, how to count "individual plants" or measure "area under conservation management agreements") and it does not assign explicit enforcement roles.

Practical consequence for duties: Practitioners should treat the adopted plans and their addenda as Commonwealth recovery plan texts for the listed species. The instrument records performance targets and clarifications that will inform intergovernmental coordination and any downstream assessments or negotiations. The precise allocation of duties to particular agencies, landholders or proponents is not spelled out in the instrument; instead the adopted plans’ text, combined with other EPBC Act provisions and any implementation arrangements, will govern operational responsibility.

The instrument contains no penal clauses, civil-penalty schedules or enforcement provisions. It is a ministerial adoption instrument: its text records which State plans are adopted and attaches addenda; it does not itself state any penalties or specify enforcement processes.

What the instrument does tell us about enforcement-relevant matters:

• The Davidsonia addendum creates measurable performance criteria over a five-year period. While the instrument does not specify sanctions for failure to meet these criteria, the existence of quantified objectives introduces a monitoring and reporting implication: someone (presumably the responsible Commonwealth or State environmental agency) will need to measure outcomes against the targets. The instrument, however, does not assign responsibility for measurement or specify consequences of non-achievement.

• The WA addendum expressly withdraws any automatic equivalence between plan-identified habitat and statutory "critical habitat" as defined in s 207A, and it clarifies the scope of s 270(2)(d) habitat as "limited to the area of occupancy if known populations." Because the instrument itself treats plan-identified habitat as distinct from statutory critical habitat, parties cannot rely on the plan alone to claim that s 207A critical habitat protections apply. Conversely, this ministerial clarification could reduce the potential for enforcement actions premised solely on plan-identified areas being treated as s 207A critical habitat.

What the instrument does not say (and therefore what needs checking elsewhere):

• The text does not set out how recovery-plan compliance is enforced under the EPBC Act, nor does it state what offences or administrative sanctions apply for non-compliance with recovery-plan measures. It does not reproduce the enforcement or offence provisions of the EPBC Act. Practitioners must therefore consult the EPBC Act itself and relevant Regulations for criminal or civil penalties, infringement notices, compliance tools, or enforcement processes related to recovery plans and matters of national environmental significance.

Practical enforcement implications and likely administrative processes (based on the instrument’s content, not on unprinted Act text):

• Monitoring and reporting: The inclusion of time-bound, measurable targets for Davidsonia implies monitoring obligations. Responsible agencies will need to collect baseline data, implement surveys and record the area under conservation management agreements. The instrument does not provide methodology; dispute about measurement could arise in implementation.
• Administrative follow-up: The Minister’s adoption and addenda create an administrative record that can be referenced in policy, assessment, and negotiation. Where a recovery plan guides mitigation or offsets for proposed actions, the adopted plan will likely be used by Commonwealth and State officials in designing or approving management measures.
• Dispute potential: Because the instrument narrows the legal effect of plan-identified critical habitat in the WA plans, disputes could arise between proponents, landholders and conservation interests about the weight to be given to plan maps when assessing impacts or seeking approvals. The instrument’s explicit narrowing reduces, but does not eliminate, the potential for enforcement disputes tied to those plan maps.

In short, the instrument records adoption and sets measurable expectations in one case, but it does not itself create or articulate the enforcement framework or penalties. Practitioners must consult the EPBC Act and administrative guidance to determine how compliance with recovery-plan measures is enforced in practice.

The instrument expressly references sections of the EPBC Act and it brings State recovery plans into the Commonwealth recovery-plan framework. The interaction points it records are limited to the textual intersections it creates.

Interplay with the EPBC Act (as invoked in the instrument):

• Adoption pursuant to s 269A: The instrument is made under s 269A of the EPBC Act and uses subsection 269A(7) for addenda. That is the primary statutory interaction recorded. By adopting State plans under s 269A, the instrument places State-authored recovery plan content within the Commonwealth recovery plan category provided for in the EPBC Act.
• Critical habitat provisions: The WA addendum references s 207A, and s 270(2)(d). The Minister’s text explicitly states that the plan-identified areas are not "areas of critical habitat as defined under section 207A", and that they are not "habitats that are critical to the survival of the species identified pursuant to Section 270(2)(d)". The addendum further states that "Habitats identified in Section 270(2)(d) are limited to the area of occupancy if known populations." That is an interpretive statement about how the Minister will treat plan-identified areas relative to the statutory categories in the EPBC Act. The instrument therefore carves out a specific relationship between the plan maps and statutory habitat definitions.

Inter-governmental and State law interactions:

• The instrument adopts State documents authored by New South Wales and Western Australian agencies. Mechanically, this is an intergovernmental recognition: the Commonwealth accepts State recovery-plan content and attaches it to the federal recovery-plan framework. The instrument does not state that the adoption displaces State law or State approvals; it simply adopts the documents as Commonwealth recovery plans. The adoption likely harmonises the recovery-objective texts at the Commonwealth level, but the instrument does not describe how State statutory or regulatory regimes (for example, native vegetation clearing laws, State-listed threatened species listings, land-use approvals) will change or align.

Overlap and potential duplication:

• Because the instrument imports State plan text into a Commonwealth recovery-plan role, the same actions may be reflected in both Commonwealth policy documents and State implementation strategies. The instrument does not resolve duplication, funding responsibilities, or the primacy of Commonwealth versus State instruments. Practitioners should expect both overlap and the necessity for coordination between Commonwealth and State agencies, because the State authored the plans and the Commonwealth adopted them.

Implications for approvals, assessments and referrals:

• The instrument does not describe or alter referral, assessment or approval processes under the EPBC Act; it simply adopts the recovery plans. However, recovery plans often inform impact assessment and mitigation measures in practice. The WA addendum’s explicit denial of equivalence between plan-identified habitat and s 207A critical habitat suggests that plan maps alone will not trigger certain statutory obligations tied to those sections. That interpretive stance reduces the chance of automatic application of any statutory consequences that may flow from s 207A or s 270(2)(d) designations, at least to the extent the Minister’s addendum is applied in decision-making.

Interaction with agreements and landholder arrangements:

• The Davidsonia addendum measures success partly by "The area under conservation management agreements". That creates an interstitial interaction between the recovery plan and private law instruments (management agreements). The instrument does not define the legal form of those agreements or their terms; it simply identifies the area under such agreements as a performance metric. Implementation will therefore intersect with contract practice, landholder negotiations and State or Commonwealth funding/incentive programs.

In summary, the instrument establishes a formal linkage between State recovery-plan content and Commonwealth recovery-plan status under the EPBC Act and clarifies the Minister’s approach to plan-identified habitat for the WA plans in relation to s 207A and s 270(2)(d). It does not, however, reproduce the EPBC Act’s wider regulatory architecture or explicitly reallocate powers between levels of government; those interactions must be explored in the full text of the EPBC Act and related secondary instruments.

The instrument itself functions as a single adoption instrument dated 18 August 2005 and signed by the Minister for the Environment and Heritage, Ian Campbell. It records adoption of a set of State recovery plans published in 2003-2004 and it attaches addenda pursuant to subsection 269A(7). Within the text provided there is no record of prior or subsequent amendments to this particular instrument.

What the instrument records about temporal features:

• Recovery plan publication dates: The State plans adopted span publication years largely in 2003-2004 (examples: NSW plan dated 2004; WA plans dated 2003-2004). Several WA plans are labelled "Interim Recovery Plan 2003-2008" or "2004-2009," which indicates the original State documents contained explicit lifespans. The Davidsonia plan has a five-year life under the EPBC addendum, as stated in the instrument.
• Commencement: The instrument states the recovery plans "will come into force on the date of signing of this instrument" and records the signing date as 18 August 2005.

No textual amendments recorded in this instrument:

• The instrument does not provide a history of amendments to the EPBC Act itself or to the recovery plans prior to adoption (except to cite the State plan titles and dates). It does not indicate that previous versions of the same Commonwealth adoption instrument existed, nor does it record revocations or supersessions of earlier Commonwealth recovery-plan adoptions.

Practical consequences for amendment searches:

• For a practitioner wanting the complete amendment history relevant to these adopted plans, the instrument is a single snapshot: it shows the State plan texts as adopted on 18 August 2005 and the addenda inserted on that date. To find later amendments or superseding Commonwealth recovery plans, one must search the Federal Register of Legislation, the EPBC Act notice registers, or Ministerial instruments issued after this date. The text provided contains no references to later ministerial actions, amending instruments, revocations, or reviews.

Embedded amendment-like actions:

• The instrument performs an editorial modification of State plans by adding text under the authority of subsection 269A(7). Those addenda function as amendments or qualifications to the State plan texts at the point of adoption. For example, the Davidsonia plan is adopted "with the following additional text included as an addendum," and the WA plans are adopted "with the following additional text included as an addendum" dealing with critical habitat. Those addenda are, in effect, amendments to the plan texts as they become Commonwealth recovery plans.

Records of plan durations:

• Several adopted State plans are themselves interim plans with specified end years (2008, 2009). The instrument adopts those documents but does not renew, extend, or amend the duration of the interim plans beyond the content of the original State documents and the five-year performance measure added for Davidsonia. Any subsequent extension or replacement would require a further ministerial instrument or action not recorded here.

In short, this instrument is a discrete adopting instrument dated 18 August 2005, incorporating State recovery plans and attaching addenda; it does not record a multi-stage amendment history or any later revocations. For the full amendment trail affecting these recovery plans after August 2005, users must consult subsequent ministerial instruments, Federal Register entries, or the EPBC Act legislative history.

The instrument includes no statement of litigation history. It is a ministerial adoption instrument and does not report any legal proceedings, judicial decisions, or dispute resolutions relating to the adoption or to the underlying State recovery plans. The text lists plan titles, authors and dates, and records the ministerial addenda and commencement date; it contains no references to court proceedings.

What the absence of recorded litigation in the instrument means in practice:

• The instrument’s silence on litigation does not prove there has been no litigation related to the species, the State plans, or the broader EPBC framework; it simply does not document any litigation. Practitioners should not assume there is no relevant case law simply because the instrument does not record it. The instrument itself is not a source of litigation history.

Potential litigation or legal review avenues (administrative risks to note):

• Administrative law review challenges to a ministerial adoption instrument are a theoretical possibility where parties allege the Minister exceeded statutory power, failed to follow required procedures, acted irrationally, or breached procedural fairness. The instrument signals the use of s 269A and s 269A(7); a challenger could, in principle, seek judicial review of whether the Minister acted within those provisions. The instrument does not mention such challenges, nor does it include procedural detail that might reveal reasons susceptible to judicial review. Practitioners should therefore treat the instrument as a possible target for administrative review, but must consult case law and the full EPBC Act for standing, grounds and remedy principles.

• Disputes over interpretation and application of the addenda: The Davidsonia plan’s numerical performance criteria and the WA addendum’s restriction on the legal meaning of plan-identified "critical habitat" could be the subject of administrative disagreements or litigation in the context of specific approvals, enforcement actions, or intergovernmental disputes. The instrument does not document any such litigation.

When litigation does occur, where to look:

• Because the instrument itself contains no litigation citations, practitioners wishing to know whether any decisions have tested the legal status or application of this particular instrument should search administrative law decisions, Federal Court and Federal Circuit Court records, and commentary or submissions from affected parties (for example, conservation organisations or industry proponents) that might have led to court proceedings. The instrument gives the precise date and ministerial signature, which can be used to locate any later cases that reference this adoption instrument.

In summary, the instrument provides no litigation history. It records an administrative action that could, in theory, be litigated, but the text contains no mention of any past or pending legal proceedings. Practitioners should therefore conduct separate searches for case law and judicial review proceedings if litigation history is material to their matters.

This instrument raises several practical risks, ambiguities and implementation friction points that practitioners and decision-makers should note. These "gotchas" are grounded in the instrument’s text and the mechanics it implements.

1. Plan-identified "critical habitat" is expressly not statutory critical habitat (WA addendum)

• The WA addendum states plan-identified areas "do not represent areas of critical habitat as defined under section 207A" and "do not represent habitats that are critical to the survival ... pursuant to Section 270(2)(d)". The gotcha is that a map or buffer zone included in an adopted recovery plan will not, by itself, carry the legal label "critical habitat" under the cited sections. Parties relying on plan maps to assert automatic statutory protections under s 207A or s 270(2)(d) will find a ministerial disclaimer that reduces the maps’ automatic legal weight. That creates potential confusion: the plan still identifies habitat and may recommend management, but it is not, by the instrument’s text, equated to statutory habitat definitions.

2. Measurement and definitional ambiguity for Davidsonia performance targets

• The Davidsonia addendum inserts two explicit quantitative metrics (10 per cent increase in individual plants/populations; 10 per cent increase in area under conservation management agreements over five years). The instrument does not define baseline dates, counting methodologies, units of measure, what qualifies as "the number of individual plants within wild populations" (e.g. seedling vs mature plant), or what exactly counts as "area under conservation management agreements" (formal agreement type, minimum term, tenure, whether private management plans count). Implementation disputes are therefore likely unless agencies adopt standardised measurement protocols. Practitioners should anticipate contested baselines and demand clarity on monitoring methodology.

3. Who bears implementation costs is unresolved

• The instrument does not allocate funding or implementation responsibilities. The Davidsonia target implies a need for survey work, restoration, management agreements and possibly incentive payments to landholders. The instrument does not state who pays for monitoring, private landholder incentives, or for conservation management agreement compensation, leaving those financial arrangements to subsequent processes. That raises risks for NGOs and landholders asked to enter agreements without commensurate funding.

4. The instrument’s immediate commencement date creates retroactivity and timing pressure

• The recovery plans "will come into force on the date of signing" (18 August 2005). For stakeholders, that means the adopted texts and addenda become the Commonwealth recovery plans at once. Parties mid-way through planning or negotiations may find new federal plan text applies immediately. This raises risks in project planning and in the timing of management agreements or approvals.

5. Intergovernmental coordination is implied but not specified

• Adoption of State plans creates expectations of cooperation between Commonwealth and State agencies, but the instrument contains no operational protocols for coordination, reporting lines, dispute resolution or funding. Where State plans call for actions requiring Commonwealth approvals or funding, the instrument leaves operational detail to separate arrangements. This can produce delay and uncertainty for private proponents and landholders.

6. The instrument does not set enforcement or sanction consequences

• The adopted plans contain actions and targets, but the instrument does not specify penalties for non-performance or failure to meet recovery criteria. That raises the risk of "soft law" expectations without teeth. Stakeholders should not assume that failure to meet the Davidsonia numerical targets will trigger a particular sanction; the instrument is silent. Enforcement pathways will need to be sought in the EPBC Act and its administrative practice.

7. Potential for mismatched spatial scopes: plan buffers vs statutory occupancy

• The WA addendum notes plans identify areas "a set distance around known populations" and "areas that do not currently contain the species but may have done so in the past." The addendum points out that s 270(2)(d) habitats are "limited to the area of occupancy if known populations." The gotcha is that plan buffers and historical habitat areas are broader than the statutory "area of occupancy," yet both exist in the adopted document. This difference creates a two-tiered spatial vocabulary that can be confusing in assessments: plan buffers may be treated operationally for management but not as statutory habitat subject to particular statutory obligations.

8. Interim plans and expiry windows

• Several adopted documents are called "Interim Recovery Plan 2003-2008" or 2004-2009. The instrument adopts those interim plans but does not state whether they will be reviewed, extended or replaced at Commonwealth level. Practitioners must verify whether the adopted plan remains current and whether a successor Commonwealth recovery plan has been issued since 2005.

9. Reliance on State-produced evidence without federal specification

• The recovery plans were prepared by State agencies. The instrument adopts them but does not endorse their scientific methodology or data standards. Parties relying on plan data for assessments or mitigation should verify the underlying evidence and its currency rather than assuming federal endorsement equals independent federal verification.

10. Addenda inserted by s 269A(7) may be narrow or contestable in interpretation

• The instrument uses subsection 269A(7) to add text. Where addenda qualify or alter the State plan (e.g. clarifying "critical habitat" or inserting performance criteria), disputes may arise about whether the addenda are consistent with the State plan’s original intent, whether they alter substantive obligations, or whether they create enforceable federal standards. The instrument’s text provides a ministerial position; parties ought to confirm how that position is applied in downstream assessments and agreements.

These gotchas mean that adopting the instrument as a compliance milestone is only the first step: practitioners need to secure clarifications (measurement standards, funding, jurisdictional roles) and to check for subsequent ministerial actions or guidance that operationalise the plan content.

The instrument is an adoption instrument; compliance advice below focuses on practical steps to align with the adopted recovery plans and the addenda recorded in the text. Because the instrument itself contains no enforcement clauses, compliance in practice means aligning with adopted plan content, preparing for monitoring and reporting, and engaging proactively with Commonwealth and State agencies.

Immediate steps (administrative and documentary)

1. Obtain the adopted plan texts and the addenda. The instrument names the precise titles, authors and dates for each adopted plan (e.g. "NSW Department of Environment and Conservation (2004). Davidson’s Plum (Davidsonia jerseyana) Recovery Plan"). Practitioners should obtain full copies of each State recovery plan and preserve the adoption instrument as the Commonwealth adoption record (signed 18 August 2005). For Davidsonia, ensure the addendum language is captured and appended to the plan text.

2. Confirm plan status and currency. Several adopted plans are labelled "interim" with life spans (2003-2008, 2004-2009). Check whether those plans have been superseded, extended or updated at Commonwealth or State level since 2005. The adoption instrument alone does not confirm currentness beyond its signing date.

3. Map the spatial scope. For WA plans, note the instrument’s critical-habitat clarification: plan-identified "critical habitat" may include buffers and historical habitat but is not equated with statutory s 207A critical habitat per the addendum. For practical compliance, prepare spatial layers that distinguish: (a) area of occupancy (known populations), (b) plan-identified buffer/historical habitat, and (c) any formally designated s 207A critical habitat (if any). Use the adopted plan maps but annotate them with the ministerial clarification.

Monitoring, measurement and reporting (practical protocols) 4. Establish baselines and methodologies. The Davidsonia addendum requires a 10 per cent increase in plant numbers/populations and a 10 per cent increase in area under conservation management agreements over five years. To demonstrate compliance:

• Define baseline counts (date, survey method, life-stage included, sampling effort).
• Choose repeatable survey protocols (timing, transects, observer calibration).
• Document data quality and chain-of-custody for survey records.
• Record the baseline and subsequent counts against the five-year period commencing 18 August 2005 (or as clarified by implementing guidance).

5. Define "area under conservation management agreements." The instrument does not define this. Before relying on the metric, agree with the responsible agency what qualifies:

   • Formal legal instruments (conservation covenants, contractual management agreements).
   • Minimum term lengths and conservation obligations.
   • Whether voluntary stewardship, landholder management plans or informal arrangements count.
   • Measurement units (hectares under agreement, mapped polygons).

6. Prepare monitoring reports and engage early with Commonwealth/State agencies. Because the adopted plan contains explicit targets, expect requests for monitoring data. Submit data in the format agreed with the responsible agency and preserve records of consultation.

Negotiation and landholder engagement 7. If your land is in plan-identified habitat, expect to be approached about conservation management agreements. Given the Davidsonia performance criteria, agencies will have an incentive to increase land under agreements. Parties should:

• Seek clarity on payment/incentive mechanisms before entering agreements.
• Insist on clear terms for obligations, duration, and exit/transferability.
• Document baseline conditions and entitlements to avoid future disputes.

Assessments, approvals and project planning 8. Do not assume plan-identified habitat automatically equals s 207A critical habitat. The WA addendum expressly cautions against that assumption. For impact assessment and referral purposes:

• Distinguish between plan-identified buffer zones and statutory habitat definitions.
• Confirm whether a particular area has any statutory designation under s 207A or s 270(2)(d) independent of the plan text.
• Consult the EPBC Act and the Federal Department for direction on referral obligations if a proposed action may affect listed species.

Funding and resource allocation 9. Anticipate funding needs for monitoring and management. The instrument imposes performance expectations without budget. Entities proposing to meet targets (government agencies, NGOs, landholders) should secure funding commitments or negotiate cost-sharing arrangements as part of conservation agreements.

Record-keeping and administrative proof 10. Keep administrative records of all interactions with agencies, agreements, and monitoring data. The adoption instrument itself is an administrative record; demonstrate compliance by preserving contemporaneous data, correspondence, and signed management agreements.

Legal and risk management steps 11. Seek legal advice before entering conservation management agreements or relying on plan maps for statutory protection. Because the instrument narrows the legal meaning of plan-identified habitat, contractual arrangements and statutory compliance should be considered separately.

12. If in doubt about enforcement or statutory consequences, refer to the EPBC Act. This instrument does not reproduce enforcement, referral or offence provisions. For obligations that may arise under other parts of the EPBC Act, consult the Act and existing administrative guidance.

Practical checklist summary

• Obtain the full texts of the adopted State plans and addenda identified in the instrument.
• Verify current status and any subsequent Commonwealth actions.
• Establish monitoring baselines and agreed methodologies, especially for the Davidsonia targets.
• Distinguish plan-identified habitat from statutory critical habitat per the WA addendum.
• Negotiate funding and clear terms before entering management agreements.
• Keep detailed records and liaise early with Commonwealth and State agencies.

By following those steps, practitioners will align their activities with the content of the adopted recovery plans as recorded in this instrument, reduce uncertainty on measurement and reporting, and avoid treating plan-identified habitat as automatically triggering statutory critical-habitat consequences given the ministerial clarification included in the addendum.