The central concept is a “recovery plan” under the EPBC Act. Although the instrument does not define the term, Part 13 Division 5 of the EPBC Act (sections 269A to 270) provides the framework. A recovery plan is a document that sets out the research and management actions necessary to stop the decline of, and support the recovery of, a listed threatened species or an ecological community. It must specify the actions to be taken, the criteria against which success is measured, the estimated cost and time frame, and the stakeholders responsible. Under section 269A(7), the Minister may adopt a plan that has been prepared by a state or territory agency, or by another person or body, with or without modifications. That adoption gives the plan legal status under Commonwealth law even though it was drafted by a state authority. The modifications are critical: a state plan might not address all matters required by the EPBC Act, or it might be inconsistent with water trigger or other federal obligations, so the Minister adds an addendum to align it.

The adoption “with modifications” means that the plan as adopted is not simply the state document; it is the state document plus the changes in the addendum. A person reading the recovery plan must also consult the addendum to know the exact legal content. The instrument lists the species and the plain‑text citation of the recovery plan (author, year, title, publisher). It also contains a note beneath the NSW table that the plans are adopted with modifications as highlighted in an addendum. The same is implied for the other tables by the common‑sense structure, though the Victoria and Western Australia tables do not carry that same explicit sentence; however, since the legal effect is that s 269A(7) allows adoption with modifications, and the instrument does not say “without modification” for those, the default is that any modifications included in the addendum apply. The addenda themselves are not published in the text of this instrument; they are separate documents referenced only by “as highlighted in an addendum”. This creates a gap for a person trying to ascertain the precise legal rules without obtaining the addenda.

Another key concept is revocation under the Acts Interpretation Act 1901 s 33(3). This section provides that where an Act confers a power to make an instrument, that power includes power to repeal, revoke, or amend the instrument in the same manner and subject to the same conditions. The instrument relies on that to replace the old Helmeted Honeyeater plan. The revocation is absolute and does not depend on the new plan being in force at the same time; it takes effect independently.

The instrument most directly affects the Commonwealth Department of the Environment (now DCCEEW) and the state environment agencies that prepared the adopted plans: the New South Wales Department of Environment and Conservation (now DPIE), the Victorian Department of Sustainability and Environment (now DEECA), and the Western Australian Department of Environment and Conservation (now DBCA). Those agencies are responsible for implementing the actions set out in the plans, and the adoption under the EPBC Act means that the Commonwealth must not act inconsistently with the plans when exercising its functions. For example, when the Minister assesses a referral under Part 7 of the EPBC Act for an action that may have a significant impact on the Smoky Mouse, the recovery plan (as adopted) becomes a mandatory consideration.

Proponents of development or land‑use change in areas where these 18 species occur are indirectly affected. They may be required to show how their proposed actions are consistent with the relevant recovery plan if the action is likely to have a significant impact on a listed species. For instance, a mining project near Corrigin, Western Australia, where the Corrigin Grevillea grows, must reckon with the recovery plan’s actions, habitat protection zones, and recovery criteria. If the plan specifies that certain areas are critical habitat, that may increase the likelihood that the action will be rejected or subjected to strict conditions. The revocation of the old Helmeted Honeyeater plan may affect projects that were designed around its 1999 provisions; those project proponents now need to update their compliance assessments to the 2008 plan.

Landholders and land managers on whose land the species occur are also affected. The recovery plans may recommend voluntary or compulsory management actions, such as fencing, weed control, or grazing exclusion. While the EPBC Act itself does not directly impose duties on private landholders to implement recovery plans, the plans can inform conditions on approvals for actions that require Commonwealth permission. They may also be cited in conservation agreements under s 306A of the EPBC Act or in biosecurity and planning decisions.

The instrument affects the listed species themselves only indirectly, by providing a legally recognised document that directs public resources and regulatory attention. The 16 species named (including one subspecies and one animal: Helmeted Honeyeater, Smoky Mouse, and Muir’s Corella) are the objects of the plans. The revocation of the 1999 plan does not affect the species’ listing status, only the operative plan.

The instrument itself does not create duties directly enforceable by private persons. The duties arise from the EPBC Act once the plan is adopted. Section 270 of the EPBC Act (now repealed or amended, but in force at the time) required the Minister to ensure that a recovery plan was in force for listed species, and that the Commonwealth took all reasonable steps to ensure the plan was implemented. Section 268 also required that the Commonwealth’s actions not be inconsistent with a recovery plan. Those duties fall on the Commonwealth, not on private parties.

Third‑party rights are limited. A person cannot bring an action for breach of the EPBC Act solely because a recovery plan is not being complied with, unless that plan is tied to a specific permit condition or conservation agreement. However, a person may have standing to seek judicial review of a decision that is inconsistent with a recovery plan, such as a decision to approve a destructive action without proper regard to the plan. The instrument’s adoption of the plans strengthens those grounds, because the plan becomes an adopted legislative instrument that the Minister must consider. The revocation of the old plan removes any legal reliance on that plan, so a person cannot argue that the Minister failed to consider the 1999 plan after revocation.

The adoption with modifications means that the addenda are part of the instrument. The public has a right to see those addenda, because they are referenced in a legislative instrument. However, the instrument does not spell out where the addenda are published. Under the Legislation Act 2003, an incorporated document must be available, but the instrument does not include a statement about accessibility. This could create a practical burden for anyone trying to understand the exact content of the adopted plans.

The revocation power under the Acts Interpretation Act s 33(3) is a procedural right of the Minister. There is no duty to consult or to provide reasons for revocation, unless the EPBC Act or regulations impose such a duty. The source does not show any such duty.

The instrument does not create any penalties. Penalties arise under other provisions of the EPBC Act for conduct that contravenes the Act’s requirements. For example, section 196B prohibits actions that kill, injure, or take a listed threatened species without a permit, and section 200 prohibits damage to critical habitat. If a recovery plan identifies critical habitat, then the Part 13 protections become relevant. The maximum penalty for a breach of such provisions is typically 500 penalty units (for a person) or 5,000 penalty units (for a body corporate) plus possible confiscation and remediation orders. However, the instrument itself is not a source of penal liability.

Enforcement mechanisms include civil proceedings (the Commonwealth or an interested person can seek an injunction or a remediation order) and criminal prosecution where the breach is wilful. The instrument may indirectly enlarge the scope of enforcement by making the recovery plan a binding document. For instance, if the EPBC Act requires a permit condition to be consistent with a recovery plan, and a permit holder acts inconsistently, that could be a breach of the permit, leading to revocation or enforcement action.

The revocation of the Helmeted Honeyeater 1999 plan has no penalty consequences in itself. It simply removes the legal status of that old plan. However, if a person relied on the old plan to justify an action (e.g., a development that was assessed under the old plan), the new plan might impose stricter requirements. The instrument does not provide a grace period, so an action that was formerly consistent with the 1999 plan may now be considered inconsistent with the 2008 plan. This could expose the proponent to enforcement if they continue without seeking a variation of approval.

There is also the potential for third‑party enforcement of the plans themselves. Section 487 of the EPBC Act gives extended standing to interested persons to seek civil remedies for breaches of the Act or regulations. The plans may form part of the “protections” that can be enforced.

The instrument operates within the framework of the EPBC Act, but it intersects with state and territory legislation. The recovery plans adopted are themselves state plans, prepared under state threatened species laws (e.g., the NSW Biodiversity Conservation Act 2016, the Victorian Flora and Fauna Guarantee Act 1988, the WA Wildlife Conservation Act 1950). By adopting them under the EPBC Act, the Commonwealth gives them federal force. This creates a dual‑layer regime: a state landholder may have to comply with the state version of the plan (which may have direct statutory force under state law) and also with the federal version (which binds the Commonwealth and informs federal decisions). Where the two versions differ because of the modifications in the addendum, a proponent must comply with the more stringent of the two (though the state law might be stricter if it imposes direct duties).

The instrument also interacts with the referral and assessment provisions of the EPBC Act (Part 7, Part 8). When a person proposes an action that is likely to have a significant impact on a listed species, the Minister must consider any approved recovery plan. The adoption of 18 new plans means that the number of species with an active federal plan has increased, potentially expanding the pool of actions that require careful assessment or are more likely to be declared “controlled actions”. The revocation of the 1999 plan reduces the pool for one species (Helmeted Honeyeater) but the new plan replaces it, so the net effect is a replacement.

The use of the Acts Interpretation Act s 33(3) to revoke is consistent with general federal legislative‑instrument practice. That section applies unless the enabling Act (here the EPBC Act) shows a contrary intention. The EPBC Act does not expressly exclude revocation, and the courts have held that s 33(3) applies to instruments such as recovery plans (although whether a recovery plan is a legislative instrument for all purposes is a separate question; this instrument was registered on FRLI, confirming its status).

The instrument may also intersect with the Environment Protection and Biodiversity Conservation Regulations 2000, which may prescribe matters relating to recovery plans, such as content requirements. The addenda likely ensure consistency with any relevant regulations.

This is the instrument itself. There is no amendment history within the source; it is the original and only version that the user has provided. However, it is possible that later instruments have amended or replaced these adoptions. The recovery plans themselves are subject to periodic review under s 269B of the EPBC Act (as in force at the time). Typically, plans have a life of five to ten years, after which they are reviewed and either replaced or revoked. The instrument dates from 2008, which means many of these plans would now be aged. Some may have been superseded by newer plans adopted in later instruments. For example, the Helmeted Honeyeater plan adopted here (Menkhorst 2008) has likely been updated since. The instrument’s adoption of the 2008 plan means that earlier 2000‑era plan was revoked. That is the only amendment history evident from the source.

The instrument itself could be amended under s 33(3) of the Acts Interpretation Act. The Minister could later issue a new instrument adding further species, revoking the adoption of a particular plan, or adopting a revised plan. Since the instrument does not contain a sunset clause, it remains in force until specifically revoked or the plan is replaced. Practitioners must check the current state of FRLI to see if this instrument is still operative. The instrument number is not given, but it would have been published as a legislative instrument with a unique F20120000000 or similar number.

The source does not contain any litigation history. However, the instrument is of a type that has been litigated around the edges. Recovery plan adoptions have been challenged on grounds such as failure to comply with the EPBC Act’s content requirements, failure to consider relevant matters, or improper delegation. For example, in Save the Ridge Inc v Commonwealth [2005] FCAFC 191, the Federal Court considered the status of recovery plans in the context of approvals. The instrument’s adoption with modifications could be challenged if the addenda alter a state plan beyond the scope of s 269A(7) or if the Minister failed to have regard to scientific advice. The revocation of the 1999 plan could be challenged if it was done without giving proper notice or if it was inconsistent with the object of the Act (i.e., to promote the recovery of species). The Minister’s discretion is broad but not unlimited; a court could set aside the adoption if it was based on a misunderstanding of the plan’s content or if the modifications were not properly identified.

The instrument’s reliance on s 33(3) for revocation might also be tested. Some instruments under the EPBC Act are not legislative instruments or are subject to a contrary intention; however, the Minister’s own registration of this instrument as a legislative instrument suggests they accepted that status. No case law directly on point for recovery plans is cited in the source.

Several features of this instrument could catch unwary readers.

First, the adoption is “with modifications” for the NSW plans, and by inference for all plans, but the instrument does not set out the modifications. To know the full legal content, one must obtain each addendum. The minister’s website or the department’s species profile page may host them, but the instrument itself does not provide a URL or a FRLI link to the addenda. This is a compliance trap: a person who reads only the state plan may miss crucial variations.

Second, the effective date is the day after registration. Registration on FRLI can occur without public notice. There is no grace period for actions already underway. If a proponent was working under the old Helmeted Honeyeater plan (1999), they must immediately adjust to the new plan. The instrument does not contain a transitional arrangement, so any action that was approved under the old plan may now be inconsistent with the new plan. This could force a variation of approval or expose the proponent to risk.

Third, the instrument does not state that the revocation of the 1999 plan is conditional on the new plan taking effect. Both happen on the same day. If the registration of the adoption fails for some reason (e.g., the instrument is disallowed by the Senate), the revocation would still be valid because revocation is a separate act. This could leave a gap if the adoption is later found invalid but the revocation remains. The source does not address this.

Fourth, the instrument lists 18 plans, but the table for Western Australia has 12 listed in the first part and then two more (Tufted Plumed Featherflower and Muir’s Corella) listed separately after the table. That totals 13, but a person counting from the first table only might miss two. The double‑table format is confusing and could lead to oversight.

Fifth, the adoption of two Zieria species from NSW, and three Victorian species, but the instrument does not adopt plans for any other states. This means that federally listed species occurring elsewhere (e.g., Queensland, South Australia) are not covered. The instrument’s scope is geographically and taxonomically limited.

Compliance with this instrument is not a direct legal obligation for private parties. Rather, compliance consists of ensuring that any action that may have a significant impact on the 18 listed species respects the content of the adopted recovery plans (including the addenda). The steps are as follows.

First, identify whether the action or activity involves any of the 16 species or subspecies listed in the schedules (Ingram’s Zieria, Zieria obcordata, Enigmatic Greenhood, Helmeted Honeyeater, Smoky Mouse, and the 13 Western Australian species). Use the EPBC Act Protected Matters Search Tool or consult a biologist. If a species is present or likely to be affected, obtain the relevant recovery plan and the associated addendum. The plan citation is given in the instrument (e.g., Menkhorst 2008 for the Helmeted Honeyeater). Download the full plan from the department’s website (or the relevant state department). Crucially, also obtain the addendum that modifies the plan. The instrument says the addendum is part of the adoption, so ignoring it is risky.

Second, assess whether the proposed action is consistent with the recovery plan. The plan often contains specific actions such as no‑go zones, weed control requirements, fire management prescriptions, or population targets. The addendum may add more stringent conditions. If the action is likely to be inconsistent, the proponent should consider redesigning the action or applying for a permit under the EPBC Act that may impose conditions to ensure consistency.

Third, if the action is a controlled action under the EPBC Act (i.e., requires approval), the proponent must demonstrate to the Minister that the action is not inconsistent with the recovery plan. The plan will be a key consideration in the assessment. The revocation of the 1999 Helmeted Honeyeater plan means that any assessment or condition referencing that old plan is now obsolete; the 2008 plan applies.

Fourth, for the Helmeted Honeyeater specifically, check that any past approvals that were conditioned on the 1999 plan are still valid. The Minister may need to revisit those approvals if the new plan contains different requirements. The proponent should proactively seek advice from the department on transitional arrangements, even though the instrument provides none.

Fifth, maintain records. The instrument is a legislative instrument and can be cited in litigation or enforcement proceedings. Keep a copy of the instrument and the plans, along with the addenda, as part of the environmental compliance documentation.

For land managers on whose property these species occur, compliance is more passive: they should be aware of the plan’s recommendations and avoid actions that would frustrate the plan’s objectives. If they receive EPBC‑related funding or are subject to a conservation agreement, the plan may become binding. In all cases, treating the plan as a guide rather than a binding set of commands is insufficient; the Minister’s duties mean that any major land‑use change that is proponent‑driven must contend with the plan.