Nuclear Waste Storage Facility (Prohibition) Act 2000

The Act’s operative architecture rests on a small set of interlocking concepts: the definition of "nuclear waste"; the scope of a "nuclear waste storage facility"; the prohibitions on certain acts; the allocation of enforcement and remedial powers; and the restrictions on public funding. Each is material to defining regulated activity, enforcement exposure and compliance choices.

Definitions and import of the Code of Practice

• "Nuclear waste" is defined expansively. It expressly includes Category A, B and C radioactive waste as defined in the Code of Practice for the Near-Surface Disposal of Radioactive Waste in Australia (1992) (the Code of Practice) (s 4). It also reaches any waste material containing a radioactive substance derived from specific nuclear operations including reactors, nuclear weapons facilities, radioisotope production facilities, uranium enrichment plants, testing/use/decommissioning of nuclear weapons, or conditioning/reprocessing of spent nuclear fuel (s 4). The Act therefore reaches a range of materials beyond a narrow industrial-class waste by linking to the Code and enumerating sources.
• The Code of Practice itself is incorporated by reference in the definition (s 4). The Act identifies the Code by title and publication details, creating an externally authored taxonomy that determines categories referenced in the statutory prohibition.

Scope of prohibited facility

• "Nuclear waste storage facility" is defined broadly as "any installation for the storage or disposal of nuclear waste" (s 4). The word "installation" is not further qualified in the Act, so the definition potentially captures a wide spectrum of constructed or assembled sites or structures used for storage or disposal.

Prohibitions

• Two distinct types of prohibitions operate in tandem:
  • A person must not construct or operate a nuclear waste storage facility (s 8).
  • A person must not bring nuclear waste into the State or transport nuclear waste within the State for delivery to such a facility (s 9).
• The Act also preserves lawful pre-existing arrangements: it does not apply to nuclear waste lawfully stored in the State before commencement of the Act, nor to nuclear waste from radioactive material used or handled under the Radiation Protection and Control Act 1982 pursuant to a licence, permit or other authority where storage/disposal has been authorised by or under that Act (s 6).

Enforcement framework and remedies

• Criminal sanctions are set as maximum penalties in ss 8 and 9.
• Corporate and personal culpability is extended to directors and persons concerned in management when a body corporate is guilty of an offence, unless the individual demonstrates reasonable diligence (s 10).
• Public authorities have remedial powers to remove unlawful facilities and make good environmental harm (s 11).
• Courts, on conviction, can order specific actions for removal, remediation, prevention or mitigation; publicity about contraventions; and payment to public authorities and injured private persons for costs and compensation (s 12).

Public money restriction

• The Act bans appropriation, expenditure or advancement of public money to encourage or finance construction or operation of a nuclear waste storage facility in the State (s 13(1)).
• It allows public money to be used for the maintenance or sharing of information or to enable the State to engage with other jurisdictions (s 13(2)). This carve-out preserves certain state functions despite the financing ban.

Parliamentary inquiry mechanism

• If the Commonwealth grants a licence, exemption or other authority to construct or operate a nuclear waste storage facility in the State, the Environment, Resources and Development Committee of Parliament must inquire into, consider and report on likely environmental and socio-economic impacts for the State (s 14).

Permanence and Crown effect

• The Act binds the Crown (s 5) and takes precedence over other Acts or laws (s 7), which shapes how public agencies and Crown entities must act. The legislative notes caution that references to other instruments may be obsolete; the Act itself cross-refers to other legislation in key definitions (s 4).

These main concepts determine who is regulated, which activities are prohibited or permitted, what evidentiary or governance burdens fall on corporations and their directors, what powers public authorities and courts possess to compel remedial action and compensation, and how public funding and parliamentary oversight are constrained in the context of nuclear waste storage proposals.

The Act allocates obligations, prohibitions and enforcement exposure across several identified actors. Understanding who pays, who decides and who changes behaviour requires mapping those statutory players.

Persons proposing or carrying out storage, operation and construction

• Natural persons and bodies corporate contemplating construction, operation or ownership of installations for storage or disposal of nuclear waste are directly affected by the primary prohibitions (s 8). The prohibition is framed as a general criminal proscription: "A person must not construct or operate a nuclear waste storage facility" (s 8). That exposure includes project proponents, developers, contractors engaged in construction, operators of facilities, and landowners who host such installations.

Persons importing or transporting nuclear waste

• Any person who brings nuclear waste into the State or transports it within the State for delivery to a nuclear waste storage facility is subject to the separate prohibition in s 9. Transporters, logistics providers, shippers and consignors are therefore within the statutory reach if the movement is for delivery to a facility.

Bodies corporate and their directors / managers

• When a body corporate commits an offence, each director or person concerned in management is personally liable to the same penalty as a natural person unless they prove reasonable diligence prevented the offence (s 10(1)-(2)). This extension places compliance duties on boards and senior management to establish and document reasonable diligence measures and oversight.

Public authorities and the Crown

• The Act binds the Crown in right of the State and, as far as the State’s legislative power permits, in its other capacities (s 5). State agencies and Crown entities must therefore act consistently with the prohibition.
• "Public authority" is given the same meaning as in the Environment Protection Act 1993 (s 4). The Act empowers such public authorities to remove contravening facilities and take remediation measures (s 11).
• The public money prohibition (s 13) constrains government spending and appropriation decisions. Budget officers, ministers, agencies and grant-making bodies must ensure that public funds are not used to encourage or finance construction or operation of a nuclear waste storage facility, subject to the specific carve-out in s 13(2).

Courts and Parliament

• Courts have jurisdiction under the Act to impose penalties, order remedial work, require publicity and order payment of costs and compensation (s 12). This creates a judicial enforcement path that can transfer remediation costs to convicted offenders.
• The Environment, Resources and Development Committee of Parliament is required to inquire and report if the Commonwealth grants relevant authority (s 14). This parliamentary committee becomes a forum for state-level scrutiny and stakeholder engagement where the Commonwealth intervenes.

Private persons and communities who suffer injury or loss

• The courts may order compensation to any person who has suffered injury, loss or damage to property as a result of a contravention, or who incurred costs to prevent or mitigate such effects (s 12(1)(c)(ii)). This provides a private-action remedy tied to criminal conviction proceedings.

Actors engaged under other statutes

• The Act explicitly excludes some activities where storage or disposal has been authorised under the Radiation Protection and Control Act 1982 or where radioactive material has been used or handled under that Act and storage/disposal has been authorised accordingly (s 6). Licenced activities under that Commonwealth-linked instrument are therefore carved out from the Act’s application to the extent expressed in s 6.

Procedural and compliance officers

• Entities responsible for procurement, grant-making, finance and intergovernmental engagement must adjust procedures to comply with the public money constraint (s 13). Compliance, legal, and environmental health and safety officers in corporations and public agencies will need to interpret the Act in operational contexts.

Incentives and behavioural effects

• The statutory penalties and director-level liability create incentives for corporate governance practices aimed at prevention, documentation and oversight.
• Public funding limits remove a potential source of support for any proposal to locate a nuclear waste storage facility in the State, which affects proponents’ financing strategies.
• The requirement for parliamentary inquiry if the Commonwealth grants authority introduces a state-level political and administrative oversight step that can affect project proponents’ timelines and reputational risk.

This Act therefore affects a wide range of actors from project developers and transporters to government funders, public authorities, corporate directors and local communities, by imposing criminal prohibitions, exposing management to personal liability, enabling public remedial action and constraining public financing and intergovernmental engagement.

The Act is primarily prohibitory but does create specific duties for public authorities, procedural rights for persons within criminal proceedings, and a limited set of carve-outs. The key statutory duties and rights are:

Prohibitory duties on persons

• Duty not to construct or operate a nuclear waste storage facility (s 8). This is an absolute statutory duty of conduct bounded only by the exceptions in s 6 and by any authorisation under the Radiation Protection and Control Act 1982.
• Duty not to bring nuclear waste into the State or transport it within the State for delivery to a nuclear waste storage facility (s 9).

Corporate governance and director duties

• Directors and persons concerned in management of a body corporate face derivative liability for offences committed by the corporation (s 10(1)). The statute places on those individuals a defensive evidentiary duty to prove they exercised reasonable diligence to prevent the offence if they are to avoid being convicted personally (s 10(1)-(2)). That shifts the compliance duty into board-level risk management and record-keeping.

Duties and powers of public authorities

• Public authorities may remove a nuclear waste storage facility constructed or operated in contravention of the Act, make good any environmental harm resulting from the construction or operation of that facility, and prevent or mitigate future environmental harm from such a facility (s 11). These are permissive powers framed as enabling action; they operate to place remediation burdens on public agencies but also allow recovery of reasonable costs via court orders (s 12(1)(c)(i)).
• The Act’s binding of the Crown (s 5) creates a duty on the State to abide by the prohibitions to the extent of its legislative power.

Court powers and judicially imposed duties

• If a defendant is convicted of an offence under the Act, the court may order the defendant to take specified action to remove the facility, remediate environmental harm, or prevent/mitigate future harm (s 12(1)(a)(i)-(iii)). The court may fix periods for compliance and impose requirements necessary for enforcement (s 12(2)).
• The court may also order that the defendant publicise the contravention and its environmental and other consequences and any other orders made (s 12(1)(b)).
• The court may order the defendant to pay the reasonable costs and expenses incurred by a public authority in taking remedial action or to pay compensation to persons who suffered injury or loss as a result of the contravention (s 12(1)(c)(i)-(ii)). These orders convert criminal outcomes into civil financial obligations.

Limitations and rights created by exceptions

• The Act does not apply to nuclear waste lawfully stored in the State before its commencement (s 6(a)). That creates a protected status for pre-existing lawful storage arrangements.
• The Act does not apply to nuclear waste derived from radioactive material that has been used or handled in accordance with the Radiation Protection and Control Act 1982 pursuant to a licence, permit or other authority granted under that Act, and the storage or disposal of which has been authorised by or under that Act (s 6(b)(i)-(ii)). This exception places rights on licence-holders under that Act to continue authorised storage or disposal despite the State prohibition.

Public money restrictions and limited rights to engage

• The Act forbids appropriation, expenditure or advancement of public money for the purpose of encouraging or financing activity associated with construction or operation of a storage facility in the State (s 13(1)). This creates a duty for officials to refuse or block funding support for such activities.
• The Act preserves a narrow right for public funding where the monies are for maintenance or sharing of information or to enable the State to engage with other jurisdictions (s 13(2)). That carve-out allows certain state functions to proceed, such as information exchange and engagement, while maintaining the financing ban.

Parliamentary oversight duty

• If the Commonwealth grants a licence, exemption or other authority to construct or operate a facility in the State, the Environment, Resources and Development Committee has a statutory duty to inquire into, consider and report on likely environmental and socio-economic impacts for the State (s 14). This creates a procedural right for the committee to scrutinise the matter and a corresponding obligation to produce a report.

Priority of the Act

• The Act has effect despite any other Act or law (s 7). This provision gives the Act priority in the hierarchy of State law insofar as provisions of other State Acts might otherwise permit or regulate the prohibited conduct.

Evidence and due diligence

• The director liability provision establishes a burden on management to demonstrate the exercise of reasonable diligence to prevent offending (s 10(1)). That has practical implications for compliance systems, monitoring, and record-keeping to create admissible evidence of reasonable diligence should prosecution occur.

Taken together, the duties are largely prohibitory and preventive: do not construct, operate, import, or transport for delivery to a nuclear waste storage facility, do not use public money to encourage or finance such activities, and ensure corporate governance systems that can establish reasonable diligence. Rights are limited to exceptions for prior lawful storage and authorised activities under the Radiation Protection and Control Act 1982, and court-ordered compensation rights for injured persons where contraventions have occurred.

The Act creates a combined criminal-penal and remedial enforcement framework, with explicit maximum penalties, extensions of liability to corporate officers, powers for public authorities to act and statutory mechanisms for the courts to impose remedial orders and cost recovery. The statutory shape of enforcement is as follows.

Criminal penalties

• The Act prescribes maximum penalties for the principal offences:
  • For a natural person who constructs or operates a nuclear waste storage facility, or brings nuclear waste into the State or transports it within the State for delivery to such a facility, the maximum penalty is $500 000 or imprisonment for 10 years (ss 8 and 9).
  • For a body corporate committing either offence, the maximum monetary penalty is $5 000 000 (ss 8 and 9).
• These maximum penalties are statutory ceilings. The Act does not provide a sentencing scale or aggravation/mitigation factors beyond the courts’ general sentencing discretion.

Officer liability and evidentiary burden

• If a body corporate commits an offence, each director or person concerned in its management is guilty of an offence and liable to the same penalty as is prescribed for the principal offence when committed by a natural person unless it is proved that the person could not, by the exercise of reasonable diligence, have prevented the commission of the offence by the body corporate (s 10(1)).
• A person prosecuted under s 10 may be convicted whether or not the body corporate itself has been prosecuted or convicted (s 10(2)). This singles out management for potential parallel proceedings.

Administrative and remedial powers of public authorities

• Public authorities may remove a nuclear waste storage facility constructed or operated in contravention of the Act; make good environmental harm resulting from the construction or operation; and prevent or mitigate future environmental harm (s 11). Those powers are framed as enabling and can be exercised in the public interest to address contraventions.
• While s 11 describes powers exercisable by public authorities, s 12 enables courts, upon conviction, to order defendants to perform specified remedial actions and to pay for costs incurred by public authorities in taking remedial steps, and to pay compensation to injured persons (s 12(1)(a)-(c)). This provides a cost-recovery path to reimburse public authorities for remediation expenses.

Court orders and enforcement mechanics

• Orders made under s 12 may include specified actions to remove facilities, remediate environmental harm and prevent or mitigate future harm (s 12(1)(a)). The court may also order publicity about the contravention and its consequences (s 12(1)(b)).
• The court can fix a period for compliance with court-ordered actions and impose other enforcement requirements it considers necessary or expedient (s 12(2)). The statute does not specify enforcement mechanisms for failure to comply with such orders beyond the court’s general enforcement powers, but the ability to set compliance periods and additional requirements gives courts latitude to tailor remedies.

Financial exposure for convicted defendants

• The court may order convicted defendants to pay reasonable costs and expenses incurred by public authorities that took remedial action as a result of the contravention, and compensation to persons who suffered injury, loss or damage or incurred costs to prevent or mitigate injury or loss (s 12(1)(c)(i)-(ii)). Those orders convert criminal culpability into quantifiable financial liabilities.

Public money restrictions as an enforcement lever

• Section 13(1) prohibits use of public money to encourage or finance construction or operation of a nuclear waste storage facility. That prohibition constrains state-level financing and may reduce the financial feasibility of proposals that would require public funding support. The Act further permits public money for maintenance, information sharing or interjurisdictional engagement (s 13(2)), creating an exception that must be monitored in practice.

Procedural consequences

• Conviction under the Act triggers the court’s power to make remedial and compensatory orders. The Act does not create a separate civil cause of action independent of a criminal conviction; rather s 12 links court-ordered payments and remedial obligations to findings of guilt in proceedings for an offence under the Act.

Limits and implementation questions

• The Act’s enforcement regime relies on prosecution for criminal offences and on judicial orders tied to conviction. The statutory text does not set out investigatory powers, administrative penalties, or a specific enforcement agency. It does give public authorities power to act in remediation (s 11) and entitles courts to recover reasonable costs paid by public authorities after they incur them (s 12(1)(c)(i)). The absence of specified administrative enforcement pathways places emphasis on criminal prosecution and court-ordered remedies as the principal enforcement mechanisms.

In sum, penalties are high and extend to corporate officers; public authorities have powers to remediate and to seek cost recovery through the courts; and the public funding prohibition functions as an additional enforcement mechanism by constraining financing options for proposed facilities.

The Act cross-references, limits or interacts with several other statutory instruments and external documents, producing a structured relationship with existing regulatory frameworks and with Commonwealth authorisations. These interactions determine where the Act’s prohibitions apply and where other laws provide rights or authorisations that remove the Act’s application.

Cross-references in definitions

• The Act adopts certain definitions from other State Acts. "Environmental harm" has the same meaning as in the Environment Protection Act 1993 and "public authority" also has the same meaning as in that Act (s 4). That linkage means the Act’s remedial powers and references to public authorities should be read with the interpretive context of the Environment Protection Act 1993 definitions.
• The Act takes the definition of "ionizing radiation" from the Radiation Protection and Control Act 1982 (s 4). More substantively, s 6(b) provides that the Act does not apply in relation to nuclear waste that results from radioactive material which has been used or handled in accordance with the Radiation Protection and Control Act 1982 pursuant to a licence, permit or other authority under that Act, and the storage or disposal of which has been authorised by or under that Act (s 6(b)(i)-(ii)). This creates a statutory carve-out where the Radiation Protection and Control Act 1982 provides authorisation for storage/disposal. The interaction therefore leaves licenced activities under that Act outside the prohibitions of this Act to the extent specified.

Incorporation of external technical guidance

• The Act incorporates the 1992 Code of Practice for the Near-Surface Disposal of Radioactive Waste in Australia (the Code of Practice) into the definition of "nuclear waste" (s 4). This makes the Code’s categorisation (Category A, B, C) a determinant of statutory scope. Because the Code is an external technical instrument, its content and any subsequent changes or revisions are operative by reference in defining what constitutes the regulated material. The legislative history shows the Code of Practice reference was inserted by amendment (1/2003 s 2(a)).

Priority and potential inter-legislative conflict

• The Act declares that it has effect despite any other Act or law (s 7). Within State law, that places these prohibitions at the top of the local legislative hierarchy, subject to constitutional constraints and to sovereign limits on the State’s legislative competence. The Act also binds the Crown in right of the State (s 5), obliging state agencies to comply. Where another State statute might permit an activity covered by this Act, s 7 controls and preserves the prohibition.

Interplay with Commonwealth authorisations

• The Act recognises the possibility that the Commonwealth may grant a licence, exemption or other authority to construct or operate a facility in the State. Where that occurs, s 14 requires the Environment, Resources and Development Committee of Parliament to inquire into and report on likely environmental and socio-economic impacts. The Act does not itself state that a Commonwealth authorisation overrides the State prohibition; rather it prescribes a parliamentary inquiry as a response. The text therefore contemplates inter-jurisdictional action but does not alter the State prohibition other than by delineating the committee’s role.

Public money and other statutory funding regimes

• Section 13(1) forbids the appropriation, expenditure or advancement of public money to encourage or finance activity associated with constructing or operating such a facility. That interacts directly with State budget and appropriation powers, requiring finance officers and Ministers to ensure that grants and expenditures comply with the statutory prohibition. Section 13(2) permits certain public funding uses, creating a cross-cutting exception compatible with other State obligations for information sharing and interjurisdictional engagement.

Regulatory overlap and administrative practice

• The Act does not establish an administrative licensing regime for nuclear waste storage facilities; instead it establishes a prohibition subject to exceptions derived from other legislation (notably the Radiation Protection and Control Act 1982). The practical effect is that regulatory responsibilities for radiation safety and licencing may continue to be exercised under the Radiation Protection and Control Act 1982, while this Act remains the State-level prohibition on locating waste storage facilities, importing or transporting waste for delivery to such facilities, and using public funds to support them.

Interpretation risk from obsolete references

• The Act’s notes caution that references to other legislation or instruments or to titles of bodies or offices are not automatically updated and may be obsolete. This is relevant where s 4 cross-refers to external Acts and the Code of Practice. Practitioners must therefore check contemporaneous versions of the cross-referenced instruments when interpreting scope or exceptions.

In practical terms, the Act sits alongside the Radiation Protection and Control Act 1982 and the Environment Protection Act 1993, borrowing definitions and providing a general prohibition that coexists with licencing pathways under other legislation. It also imposes limits on State funding and triggers parliamentary scrutiny where Commonwealth authorisation occurs. The text therefore creates a layered legal environment: technical regulation and licencing under radiation and environment statutes; a State-level prohibition and criminal enforcement regime; and procedural constraints on public funding and parliamentary oversight in inter-jurisdictional situations.

The legislative history included in the source sets out the principal Act and subsequent amendments, with dates of assent and commencement and a record of provisions varied. The Act has been amended multiple times since its enactment, and the history in the source lists the key variations and commencement dates.

Principal Act

• Nuclear Waste Storage Facility (Prohibition) Act 2000, No 68 , Assent: 30 November 2000; Commencement: 25 January 2001 (Gazette 25.1.2001 p300).

Amendments recorded in the source

• 2003, No 1 , Nuclear Waste Storage Facility (Prohibition) Amendment Act 2003 , Assent: 27 March 2003; Commencement: 27 March 2003. This amendment inserted the Code of Practice definition and substituted the definition of nuclear waste (see "Provisions amended" in the legislative history: s 4 Code of Practice inserted by 1/2003 s 2(a); "nuclear waste" substituted by 1/2003 s 2(b); s 15 insertion by 1/2003 s 3, though s 15 was later deleted by other amendment).
• 2003, No 22 , Nuclear Waste Storage Facility (Prohibition) (Miscellaneous) Amendment Act 2003 , Assent: 18 July 2003; Commencement: 18 July 2003. This amendment omitted s 2 under the Legislation Revision and Publication Act 2002 on 18 July 2003 and deleted s 15 as indicated in the provisions amended list.
• 2016, No 17 , Nuclear Waste Storage Facility (Prohibition) (Public Money) Amendment Act 2016 , Assent: 21 April 2016; Commencement: 21 April 2016 except s 4 which commenced on 9 May 2016 (Gazette 9.5.2016 p1388). This amendment redesignated s 13 as s 13(1) and inserted s 13(2), creating the public money carve-out for maintenance, information sharing and interjurisdictional engagement (see "Provisions amended": s 13 redesignated as s 13(1) by 17/2016 s 4 on 9.5.2016; s 13(2) inserted by 17/2016 s 4).
• 2017, No 60 , Nuclear Waste Storage Facility (Prohibition) (Public Money) Amendment Act 2017 , Assent and Commencement: 12 December 2017. This amendment further substituted s 13(2) to its current form (see "Provisions amended": s 13(2) substituted by 60/2017 s 3 on 12.12.2017).

Detail of provision-level variations

• s 2 was omitted under the Legislation Revision and Publication Act 2002 on 18 July 2003.
• s 4 was amended in 2003: Code of Practice was inserted by 1/2003 s 2(a) commencing 27.3.2003; the definition of "nuclear waste" was substituted by 1/2003 s 2(b) on the same date.
• s 13 was redesignated and expanded in 2016 and 2017: s 13 was redesignated as s 13(1) by the 2016 amendment, and s 13(2) was inserted in 2016 with a subsequent substitution of s 13(2) by the 2017 amendment.
• s 15 was inserted by the 2003 amendment but deleted by the Miscellaneous Amendment Act 2003 on 18.7.2003.

Reprints and publication

• The legislative history records multiple reprints: Reprint No 1 dated 27.3.2003, Reprint No 2 dated 18.7.2003, and a reprint dated 9.5.2016, reflecting times when consolidated versions were prepared.

Notes and editorial caution

• The source includes a note that references in the legislation to other legislation or instruments or to titles of bodies or offices are not automatically updated as part of the revision and publication program and therefore may be obsolete. Practitioners should therefore check contemporaneous texts of cross-referenced instruments when interpreting the Act.

Taken together, the amendment history shows that the statutory framework has been adjusted to:

• incorporate a technical Code of Practice into the statutory definition of nuclear waste (2003), and
• add, redesignate and refine the public money restriction and its carve-out for maintenance, information sharing and interjurisdictional engagement (2016 and 2017).

The dates of assent and commencement are provided for each amendment, which is material when assessing whether a particular activity fell inside or outside the Act at a given time.

The source does not include any case law, reported decisions or examples of litigation under the Nuclear Waste Storage Facility (Prohibition) Act 2000. The legislative text and the attached legislative history list statutory amendments and reprints but contain no references to judicial determinations, appeals or precedent interpreting the Act. Consequently, there are no named cases in the source to cite or to use as interpretive authority.

Absent source-provided case law, the Act itself identifies the types of judicial proceedings and orders that would arise if prosecutions occur or if courts are asked to exercise their powers under the statute:

• Criminal prosecutions: The Act contemplates prosecutions for contraventions of ss 8 and 9. Conviction would lead to sentencing within the statutory maximums specified and would enable courts to exercise additional remedial powers under s 12.
• Director and management prosecutions: Section 10 contemplates separate prosecution of directors and persons concerned in management for offences committed by a body corporate, with an evidentiary exception where the individual proves they exercised reasonable diligence to prevent the offence. The statute permits conviction of such individuals whether or not the corporate principal has been prosecuted or convicted (s 10(2)).
• Court remedial powers tied to conviction: Section 12 permits the court on conviction to order removal and remediation, publicity of the contravention, and payment to public authorities and injured persons for costs incurred or losses suffered. It also permits fixing periods for compliance and imposing other enforcement requirements.
• Public authorities’ actions and recovery: Section 11 authorises public authorities to remove facilities and mitigate harm. Section 12(1)(c)(i) expressly permits the court to order a convicted defendant to pay to a public authority the reasonable costs and expenses it incurred in taking action of the kind described in s 11 as a result of the contravention.

In practical terms, litigation under this Act would likely involve questions such as:

• whether a particular installation falls within the statutory definition of "nuclear waste storage facility" (s 4);
• whether the material in question constitutes "nuclear waste" as defined, including whether it is captured by the Code of Practice categories or by the enumerated sources in s 4;
• whether conduct falls within the s 6 exceptions for pre-existing lawful storage or storage authorised under the Radiation Protection and Control Act 1982; and
• whether directors or managers can establish the exercise of reasonable diligence to avoid personal liability under s 10.

Because the source does not provide judicial decisions, practitioners must rely on statutory text and any relevant external jurisprudence (not provided in the source) for interpretation in litigation. The Act’s text does not set out evidentiary rules, investigative powers, or administrative enforcement pathways beyond the criminal prosecutions and court powers described; these procedural and evidentiary matters would be matters for courts to decide in any litigation that arises.

The Act is compact, but several points in the text create traps for the unwary or require careful interpretation. These enforceable nuances affect scope, compliance obligations and potential exposure.

Definition-driven scope

• The statutory reach of "nuclear waste" is anchored to the 1992 Code of Practice for the Near-Surface Disposal of Radioactive Waste in Australia and to a list of activities that produce waste (s 4). Because the Act imports the Code by reference, changes in the scientific or regulatory landscape may not be reflected unless the Code itself is updated and the Act is later amended. Practitioners must check the version of the Code and its categories when assessing whether material falls within "nuclear waste".
• "Nuclear waste storage facility" is defined as "any installation for the storage or disposal of nuclear waste" (s 4). The absence of qualifiers such as size, capacity, permanency or technical design means that small, temporary or ad hoc storage installations could nevertheless be captured. A site operator who considers their activity marginal should not assume immunity without legal examination.

Pre-existing lawful storage exception timing

• The Act does not apply to nuclear waste lawfully stored in the State before commencement of the Act (s 6(a)). The precise determination whether particular storage was "lawful" at commencement may require careful factual and documentary evidence. Operators relying on pre-existing status should retain documentary proof of legality and date of storage.

Interaction with Radiation Protection and Control Act 1982

• The s 6(b) carve-out exempts nuclear waste where the radioactive material has been used or handled in accordance with the Radiation Protection and Control Act 1982 pursuant to a licence, permit or other authority and storage/disposal has been authorised under that Act (s 6(b)(i)-(ii)). Operators relying on this exception must ensure their authorisations under that Act explicitly cover the storage or disposal in question. Absent express authorisation, the exemption may not apply.

Public money carve-out nuance

• Section 13(1) prohibits appropriation, expenditure or advancement of public money to encourage or finance activity associated with constructing or operating a nuclear waste storage facility. However, s 13(2) allows public money for maintenance, sharing of information or to enable the State to engage with other jurisdictions. The exception is narrow and does not permit funding that tangibly encourages or finances construction or operation. Agencies must document the objective of any spending that touches on these areas to demonstrate compliance.

Officer liability evidentiary burden

• Directors and managers can be prosecuted for corporate offences (s 10). The statute places on them the burden to prove they could not, by the exercise of reasonable diligence, have prevented the offence. This evidentiary burden requires robust record-keeping, governance procedures, compliance audits and documented interventions. A lack of contemporaneous evidence of due diligence can expose officers to conviction even if the company is also convicted.

Public authorities’ remedial action and cost recovery

• Public authorities may remove contravening facilities and make good environmental harm (s 11). If a public authority undertakes action before or without a conviction, recovering costs may depend on subsequent court orders made under s 12(1)(c)(i). Timing and coordination between remedial action and prosecutorial decisions therefore matter for cost recovery.

No administrative licensing or exemption mechanism in the Act

• The Act does not create an administrative licence or exemption pathway to permit a nuclear waste storage facility. The only statutory exceptions are those in s 6 and authorisations under the Radiation Protection and Control Act 1982. Proponents cannot obtain a State-issued exemption under this Act; any authorisation must come from the Radiation Protection and Control Act 1982 regime or be assessed against the s 6 criteria.

Effect despite other law and Crown binding

• The Act states it has effect despite any other Act or law (s 7) and binds the Crown (s 5). Where other State Acts might permit an activity, this Act’s prohibition applies. However, the precise constitutional or interjurisdictional implications where Commonwealth authorisations are in play are not addressed in the text; that may give rise to procedural complexity if federal authorisations are involved.

Obsolescence of cross-references

• The legislative notes caution that references to other legislation or instruments may be obsolete. Because the Act depends on definitions and cross-references to the Environment Protection Act 1993, the Radiation Protection and Control Act 1982 and the Code of Practice, practitioners must verify the current texts and the present status of those instruments when applying the Act.

Parliamentary inquiry trigger if Commonwealth acts

• If the Commonwealth grants a licence, exemption or other authority for construction or operation in the State, s 14 requires a parliamentary committee inquiry. A proponent should anticipate political and reputational risk, and potential procedural scrutiny, even though the Act does not set out how that inquiry influences the validity of any Commonwealth authorisation.

Broad remedial obligations linked to conviction

• Courts may order removal, remediation and publicity in addition to criminal penalties (s 12). Convicted parties face not only fines or imprisonment but also potentially substantial remediation and compensation obligations. Companies and officers must model those contingent liabilities in risk assessments.

Taken together, these points show that practitioners must examine definitions, authorisations under the Radiation Protection and Control Act, documentary evidence of lawful pre-existing storage, public money use, corporate governance and records, and the timing of public authority remedial steps when advising clients or designing compliance programmes.

Compliance under the Act requires preventive steps that address the statutory prohibitions, director-level exposure, public money restrictions and the interplay with licencing regimes under other Acts. The following practical steps flow directly from the Act’s text and identify necessary actions for different actors.

For prospective developers, constructors and operators

• Do not proceed with construction or operation of any installation intended for storage or disposal of materials that fall within the Act’s definition of "nuclear waste" (s 4, s 8). Obtain legal advice to determine whether the material in question is captured by the statutory definition, including whether it fits Category A/B/C per the 1992 Code of Practice or the enumerated derivations in s 4.
• If the proposal involves importation or transport for delivery to a storage facility in the State, defer or cancel those logistics because s 9 prohibits bringing nuclear waste into the State or transporting it within the State for delivery to a nuclear waste storage facility.
• If a proposal relies on a Commonwealth-authorised pathway (e.g. licences under federal law), anticipate that the Environment, Resources and Development Committee will be required to inquire and report on likely environmental and socio-economic impacts (s 14). Plan stakeholder engagement and submissions to that committee as part of the project timeline.

For corporate boards, directors and senior managers

• Implement and document a demonstrable compliance regime and governance framework to evidence "reasonable diligence" in the event of prosecution under s 10. This should include formal compliance policies, periodic audits, training, defined accountability lines, incident reporting systems, and contemporaneous records that show supervisory oversight and attempts to prevent prohibited conduct.
• Require legal review before any contractual arrangements involving movement, storage, or disposal of materials that could arguably be "nuclear waste". Maintain records of legal advice and internal approvals.

For transporters, shippers and logistics providers

• Establish internal controls to screen consignments to ensure that no shipments are intended for delivery to a nuclear waste storage facility in the State. If transport involves material that may fall within the Act’s definition of nuclear waste, obtain a legal determination before accepting carriage instructions, as transporting such material for delivery to a facility is prohibited (s 9).

For public authorities, ministers and finance officers

• Ensure appropriation, expenditure and advancement of public money are not used to encourage or finance construction or operation of a nuclear waste storage facility in the State (s 13(1)). Document the purpose of any relevant expenditure and ensure that any permitted spending falls strictly within s 13(2) narrow carve-outs: maintenance, sharing of information or enabling the State to engage with other jurisdictions.
• If a contravention occurs, public authorities have statutory powers to remove facilities and mitigate environmental harm (s 11). Keep detailed records of costs and expenses incurred in remediation because courts may order convicted defendants to pay reasonable costs incurred by public authorities (s 12(1)(c)(i)).

For licence-holders under the Radiation Protection and Control Act 1982

• Review your authorisations under the Radiation Protection and Control Act 1982 carefully. The Act exempts from its operation nuclear waste where storage or disposal has been authorised under that Act or where material has been used or handled pursuant to a licence or permit under that Act (s 6(b)(i)-(ii)). Ensure that licences expressly authorise the storage or disposal activities to be undertaken and maintain compliance and licence documentation proving authorisation.

For communities, landowners and persons with existing lawful storage

• If storage pre-existed the commencement of the Act and was lawful at that date, the Act does not apply to that storage (s 6(a)). Preserve evidence demonstrating lawful status as of the commencement date to protect the existing operation.

General compliance and risk management measures

• Maintain up-to-date knowledge of the Code of Practice referenced in s 4 as the statutory definition of "nuclear waste" refers to Category A, B and C classifications in that Code. Where technical classification is uncertain, obtain expert advice from a recognised radiation safety authority and document the technical basis for any classification conclusion.
• Establish a protocol for rapid legal advice where any governmental or interjurisdictional authorisation is sought or issued by Commonwealth authorities, given the statutory requirement for a parliamentary inquiry under s 14 if the Commonwealth grants a licence, exemption or other authority.
• For any organisation with potential exposure, conduct a compliance gap analysis mapping the Act’s prohibitions to operational activities, transport routes, contracts, and supplier and customer relationships. Where gaps exist, cease or suspend activities that could trigger offences until legal clearance is obtained.
• Keep detailed procurement and grant records for any public money spent in areas touching on nuclear waste issues, and ensure the purpose of expenditure fits the narrow s 13(2) exception where applicable.

Preparing for enforcement and remediation exposure

• Model potential remedial and compensatory liabilities that could be imposed by courts under s 12 in addition to criminal penalties. Contingent liabilities may include costs of removal, remediation, publicity campaigns ordered by courts, and payments to public authorities or private persons for costs and losses.
• Where remediation may be required, document environmental monitoring and mitigation plans that demonstrate proactive prevention efforts; that documentation can be relevant to both administrative and judicial assessments of conduct and may support claims of reasonable diligence for directors.

Engaging with the parliamentary inquiry

• If a Commonwealth authorisation is granted, plan engagement with the Environment, Resources and Development Committee of Parliament by preparing submissions and impact assessments focusing on environmental and socio-economic effects as the committee is required by statute to inquire and report on those matters (s 14).

Legal advice and verification

• Given the interaction with other statutes and the potentially wide scope of the definitions, obtain case-specific legal advice before undertaking activities touching on nuclear waste, storage, transport or financing. Ensure contemporaneous verification of the current versions of the Environment Protection Act 1993, the Radiation Protection and Control Act 1982 and the Code of Practice, as the Act’s definitions and exceptions rely on those instruments (s 4, s 6).

These measures, grounded in the Act’s text, are aimed at preventing conduct that would contravene ss 8 and 9, at protecting directors from personal liability by documenting reasonable diligence, at ensuring public money is not used contrary to s 13, and at preparing for parliamentary inquiry obligations under s 14 where Commonwealth actions are taken.