Waste Avoidance and Resource Recovery Act 2001

The Act casts a wide net. The EPA is the central administrator (ss 6, 12, 18, 26, 28, 34, 40). The Minister enters Scheme administration agreements, appoints advisory committees, varies or terminates agreements and requests performance audits (ss 24, 33, 34, 36).

Beverage suppliers—defined broadly as persons carrying on a business that includes supply of beverages in containers (s 20)—face the most direct obligations. They must hold a container approval, enter a supply arrangement with the Scheme Coordinator, ensure refund markings appear on containers, and pay contributions under supply arrangements (ss 38–40). Suppliers of beverages sold through vending machines are deemed to be the lessee or owner of the machine (s 37). Corporations face 4,000 penalty unit maxima for supply offences; individuals 1,000 (ss 38, 39, 44, 47).

Network operators and the Scheme Coordinator are parties to Ministerial agreements that impose performance targets, payment obligations, reporting, audit and anti-discrimination requirements (ss 24–35). Collection point operators (including operators of reverse vending machines) must accept eligible containers and pay refunds, keep records for three years and may require refund declarations or proof of identity in high-volume cases (ss 42–43). Material recovery facility operators (licensed or EPA-approved) may claim processing refunds but must not landfill containers for which refunds have been claimed (s 28).

Local councils are subject to requests for explanations of non-compliance with the State waste strategy (s 14) and are indirectly affected through the EPA’s regional coordination role (s 6(1)(d)). Producers and suppliers of products subject to future EPR regulations will face obligations once schemes are prescribed.

The general public benefits as consumers who can obtain refunds, but may also be regulated when returning containers in bulk (s 43). Advisory committee members, though not core regulated parties, must represent a range of interests (s 36(3)).

The Crown is bound in all capacities (s 52). Commonwealth competition law is disapplied to the extent of authorised conduct (s 45).

Duties fall most heavily on Scheme participants. Suppliers must not supply beverages in containers unless a supply arrangement and container approval are in force and the container bears a refund marking (ss 38–39). Container approval holders must comply with conditions (s 40(8)). Scheme Coordinators must enter supply and network arrangements, pay network operators, and report annually on performance, charges and other prescribed matters (ss 25, 35). Network operators must establish collection points, pay collection point operators and comply with performance targets (ss 25, 30). Collection point operators must pay refunds in cash or an approved manner at the time of acceptance (subject to exceptions in s 42(2)) and retain records for three years (s 43(5)).

The EPA’s duties include developing the State waste strategy (s 12), publishing annual EPR priority statements and reports on submissions (s 18), issuing processing refund protocols (s 28(2)), monitoring compliance, and preparing biennial reports on waste volumes, strategy targets and program success (s 53). In all its functions the EPA must regard the principles of ecologically sustainable development (s 6(3)).

Rights include the statutory right of any person to present an eligible container at a collection point and receive the refund amount (s 42(1)), subject to the operator’s limited discretion to refuse (s 42(2)). Suppliers have a right to apply for container approval (s 40(1)) and to seek NCAT review of refusal, conditions, suspension or revocation (s 40(6)). Scheme participants may make submissions on EPR priority statements (s 18(3)) and are entitled to procedural fairness before non-consensual variation or termination of agreements in certain cases (s 33). Material recovery facility operators have a conditional right to processing refunds once a protocol is issued (s 28(6)).

The Minister may invite applications for Scheme administration agreements, determine fit-and-proper-person criteria by regulation, and extend the Scheme Coordinator agreement twice for up to three years each (ss 24, 32). Advisory committees have the functions the Minister determines (s 36(2)).

The Act creates a tiered penalty regime. Supply of beverages in unmarked or unapproved containers attracts 4,000 penalty units for corporations and 1,000 for individuals (ss 38, 39). The same maxima apply to false refund claims and false or misleading information (ss 44, 47). Lesser penalties apply to collection point operators who fail to pay refunds (100/50 penalty units) and to record-keeping breaches (40 penalty units) (ss 42, 43). Container approval conditions are backed by 200/50 penalty unit offences (s 40(8)).

Scheme administration agreements may include penalty provisions enforceable as debts due to the State (s 30). Breach of a contractual penalty provision creates a civil debt determined in accordance with the agreement; this operates despite any other law.

Chapter 7 of the POEO Act is expressly extended to monitoring and enforcement of Scheme administration agreements and Scheme arrangements (s 31). Authorised officers may therefore exercise entry, inspection, information-gathering and seizure powers for the purpose of determining compliance or obtaining audit information. The EPA may also conduct performance audits and recommend remedial action (s 34).

Ancillary liability (aiding, attempting, conspiring) attracts the same penalty as the principal offence (s 54). Corporate state-of-mind rules attribute an officer’s or agent’s knowledge or intention to the corporation (s 55).

Regulations may create offences with maxima of 200 penalty units (individuals) or 400 (corporations) (s 56(2)). Inconsistent provisions in agreements or arrangements are void to the extent of inconsistency with Division 3 or prescribed regulations (s 29).

The Act is deliberately integrated with the POEO Act. “Waste” takes its meaning from that statute (s 4(1)). EPA functions must assist POEO Act objectives (s 3(h)). Chapter 7 enforcement powers are imported and extended (s 31). Environment protection licences held by material recovery facilities are a gateway to processing refund eligibility (s 20).

The Protection of the Environment Administration Act 1991 supplies the definition of the EPA itself and the principles of ecologically sustainable development (s 4(1)). The Local Government Act 1993 definition of domestic waste management services determines which operators qualify as material recovery facility operators (s 20). The Administrative Decisions Review Act 1997 provides the vehicle for NCAT review of container approval decisions and any other decisions prescribed by regulation (ss 40(6), 46).

Competition law is ousted to the extent of conduct authorised by Scheme administration agreements, Scheme arrangements, container approvals and related negotiations (s 45). The Interpretation Act 1987 applies to undefined terms (s 4(1) note).

Transitional provisions in Schedule 4 interacted with the Waste Minimisation and Management Act 1995 (now repealed), the Public Sector Management Act 1988, the Duties Act 1997 (exempting transfers from duty) and the Environmental Trust Act 1998 (receiving the former Waste Fund). The Subordinate Legislation Act 1989 was disapplied to the first CDS regulation (Sch 4 cl 19).

The Act expressly preserves the validity of regulations even if the Minister’s satisfaction under s 17 was not reached (s 17(2)) and prevents agreements from contracting out of the variation and termination rules in s 33.

The most significant change was the insertion of Part 5 by the Waste Avoidance and Resource Recovery Amendment (Container Deposit Scheme) Act 2016. That reform responded to persistent litter, low recycling rates for beverage containers and the absence of a uniform national scheme. It replaced an earlier, narrower CDS framework with a fully contractual, centrally coordinated system involving a Scheme Coordinator, network operators, supply arrangements and statutory refund obligations.

In 2021 the Waste Avoidance and Resource Recovery Amendment (Reform) Act 2021 substituted s 12, deeming the NSW Waste and Sustainable Materials Strategy 2041—Stage 1: 2021–2027 to be the State waste strategy, and amended the objects in s 3 to strengthen references to resource efficiency, market development and litter prevention. These changes aligned the Act with the 20-year strategy’s targets and gave the EPA clearer statutory footing for ongoing policy work.

Section 35 was amended in 2025 to adjust annual reporting deadlines and content. Earlier amendments (2003, 2005, 2008, 2016, 2018) repealed spent Parts, transferred functions from Resource NSW to the EPA, abolished the Waste Fund, and refined EPR priority-statement procedures.

The changes reflect a policy shift from framework planning to direct industry funding of recovery infrastructure, driven by concerns over visual litter, marine debris, resource loss and the cost burden falling on ratepayers and the environment.

The Act itself contains no detailed codification of past litigation. It does, however, provide for NCAT administrative review of container approval decisions (s 40(6)) and any other class of decision prescribed by regulation (s 46). An application is deemed refused if not determined within 28 days (s 40(7)). These provisions indicate legislative anticipation of disputes over approval conditions, suspensions and revocations.

Section 17(2) prevents regulations implementing EPR schemes from being challenged on the basis that the Minister’s satisfaction was not reached, suggesting an awareness that economic, national-scheme and constitutional criteria could generate controversy.

The competition exemption in s 45 was included to forestall claims under Part IV of the Competition and Consumer Act 2010 (Cth) or the Competition Code, implying that coordinated pricing and market-sharing elements of the CDS were recognised as potentially anti-competitive.

No specific court challenges are recited in the text. Controversies surrounding the CDS have centred on the scope of “beverage”, the refund amount, the geographic reach of corresponding-law containers, the treatment of bulk returns, and the adequacy of collection networks in regional areas. These are addressed through the regulation-making powers in ss 21–23, 27 and 28 rather than through statutory amendment. The requirement for advisory committees to represent a range of interests (s 36(3)) and the public-submission process for EPR priority statements (s 18) are designed to mitigate stakeholder dissatisfaction.

Most practitioners assume the CDS refund obligation is absolute. Section 42(2) contains nine distinct exceptions, including reasonable belief that the container was acquired interstate before the scheme commenced, had already attracted a refund, or had been processed by a material recovery facility. Reverse vending machines are deemed not to accept rejected containers (s 42(5)), creating a practical carve-out that is easily overlooked.

The definition of “supplier” for vending machines (s 37) captures the machine owner or lessee, not the beverage brand owner, which can surprise national brands that thought their supply-chain contracts shifted liability.

Processing refunds for material recovery facilities are unavailable until the EPA issues a Gazette protocol (s 28(6)). The protocol may use audit-based estimates rather than actual counts and can limit eligible operators or container classes. Claims are prohibited if the containers are landfilled (s 28(7)(d)), but proving the negative can be burdensome.

Scheme administration agreements can be varied or terminated without consent if performance targets are missed (s 33(2)(a)). The affected party receives no compensation (s 33(4)) and cannot contract out of this power (s 33(5)). The seven-year initial term with two three-year extensions (s 32) is shorter than many infrastructure contracts, exposing participants to re-tender risk.

Section 29 voids inconsistent provisions in agreements and arrangements, but only “except as provided by the regulations”. The regulations may therefore carve out safe harbours that are not immediately obvious on the face of the agreements.

The EPA’s power to request councils to explain strategy non-compliance (s 14) is framed as a request, yet non-response or inadequate response can be escalated through POEO Act powers once s 31 is engaged. Councils therefore face de facto reporting obligations without the statutory language declaring them as such.

Finally, the Act’s objects were amended in 2021 to include explicit reference to market development for recovered resources (s 3(a), (b)(iv)). This seemingly innocuous change grounds EPA expenditure and regulatory priority on downstream markets, which can catch manufacturers who assumed the legislation was concerned only with collection.

Compliance begins with mapping obligations against organisational role. Beverage suppliers must:

1. Confirm whether their products fall within the s 21 “beverage” definition (excluding any items prescribed out by regulation).
2. Apply for container approval on the EPA-approved form, paying the prescribed fee and supplying labelling evidence that includes a compliant refund marking (s 40).
3. Enter a supply arrangement with the Scheme Coordinator before first supply in New South Wales (s 38).
4. Ensure all containers placed on the market bear the refund marking and are covered by an approval (s 39).

Scheme Coordinators and network operators must negotiate agreements that contain mandatory content on payment methodologies, non-discrimination, performance targets and audit rights (ss 25, 27). They must maintain records sufficient to demonstrate compliance with monitoring and reporting obligations (s 31) and publish annual reports within 90 days after financial year-end (s 35).

Collection point operators must install systems to pay refunds immediately (or as otherwise permitted by regulation), train staff on the nine exceptions in s 42(2), and implement refund-declaration and identity-check protocols when daily or periodic volumes exceed regulatory thresholds (s 43). Three-year record retention is mandatory.

Material recovery facility operators should obtain EPA approval or ensure they hold the requisite environment protection licence, enter arrangements for processing refunds, and maintain segregation procedures to prevent landfilling of refund-eligible containers.

All parties must avoid providing false or misleading information in claims or returns (s 47) and be alert to the corporate state-of-mind rule (s 55).

Organisations should monitor the EPA’s annual EPR priority statement (s 18), participate in public consultations, and review the State waste strategy every five years (s 12(3)). Councils should maintain internal records demonstrating alignment with strategy objectives in case an EPA request is received under s 14.

Legal teams should maintain a register of all Scheme administration agreements, container approvals and processing refund protocols, because s 29 voids any inconsistent internal clauses. Regular fit-and-proper-person self-assessments are prudent given the Minister’s discretion under s 24(5). Finally, because the regulations may adopt documents as in force from time to time (s 56(3)), compliance manuals must be version-controlled against changing standards and protocols.

A robust compliance program will integrate waste hierarchy considerations into product design, procurement and end-of-life planning, treat the CDS as a supply-chain cost rather than an optional levy, and maintain audit-ready records that can be produced to EPA authorised officers exercising Chapter 7 powers.