EPR Packaging Compliance

Extended producer responsibility, usually abbreviated EPR, is a policy approach that makes the organisation that places packaging on the market financially responsible for what happens to that packaging once it becomes waste, rather than leaving the cost of collection, sorting, and recycling to local or national government alone. The mechanics differ by jurisdiction, but the underlying logic is consistent: a producer reports how much packaging it supplies, broken down by material and packaging activity, and pays a fee calibrated to that reported volume and to the environmental characteristics of the materials used.

In the UK, the current EPR for packaging regime is administered jointly by Defra, the environment agencies of England, Scotland, Wales and Northern Ireland, and the scheme administrator PackUK, operating through a Report Packaging Data (RPD) online service 1. In the European Union, packaging producer responsibility obligations are now set within Regulation (EU) 2025/40 on packaging and packaging waste, which entered into force on 11 February 2025 and, as of October 2026, applies from 12 August 2026, having repealed the earlier 1994 Packaging Directive 2. In the United States there is no single federal EPR law; instead a number of states, including Oregon (under SB 582), Colorado, California (under SB 54, the Plastic Pollution Prevention and Packaging Producer Responsibility Act), and others, have each enacted their own packaging EPR statutes with differing scope, timelines, and administering bodies 3.

Under the UK regime, GOV.UK guidance defines a producer of packaging as an organisation that carries out one or more defined packaging activities: supplying filled packaging under its own brand, packing or filling goods into packaging, importing goods that are already packaged, supplying unfilled packaging that it manufactures or imports, hiring or loaning out reusable packaging, operating an online marketplace through which filled or unfilled packaging is supplied into the UK from overseas, or selling filled packaging directly to an end user 1. A business can be a producer for some of its packaging and not for other packaging it merely handles, and the same physical package can involve several different producers at different stages — the brand owner, the co-packer that fills it, and the importer that brings it into the country may each have distinct reporting duties for different components.

GOV.UK guidance is specific that an organisation remains the producer of its branded packaging even when a separate company carries out the import, packing, or manufacturing on its behalf: asking a third party to import filled branded packaging, having another organisation pack or manufacture goods for sale under your brand, or licensing another organisation to manufacture and supply your branded product does not transfer producer status away from the brand owner 1. Where packaging carries more than one brand, the organisation that first supplies the filled packaging in the UK is generally the one that must report it, and if no single brand owner made that first supply, the guidance falls back to whichever brand occupies the largest area of the pack 1.

Being a producer of packaging does not automatically mean an organisation has reporting and fee obligations. UK guidance distinguishes a 'large producer' from a 'small producer' using thresholds tied to annual turnover and the tonnage of packaging supplied in the UK: as of the guidance reviewed, an organisation is an obligated large producer broadly where it carries out a packaging activity, is established in the UK, supplied or imported more than 25 tonnes of packaging in the relevant preceding year, and had worldwide annual turnover of £1 million or more, with a separate, more limited set of duties applying to organisations below those thresholds that still meet lower size tests 1. The precise tonnage and turnover figures, and the reference periods used to calculate them, are updated periodically on GOV.UK, so a producer should always confirm the current thresholds and reporting year on the live guidance rather than relying on a fixed figure.

US state programmes use their own, separately defined producer concepts. California's SB 54 programme, for example, is administered by CalRecycle and is described as regulating several thousand producers of covered material categories, with a dedicated Producer Responsibility Organization (the Circular Action Alliance) submitting a plan to CalRecycle's advisory board 3. Oregon's framework originates in Senate Bill 582, which set out legislative findings about the state's declining recovery rate and established the statutory basis for a modernised, producer-funded recycling system 4. Because each state law defines 'producer', covered material, and reporting obligations independently, a brand that sells into multiple US states should not assume that registering or reporting under one state programme satisfies another.

Even though the legal obligation to register and pay sits with the producer organisation, the underlying data about packaging quantities and composition is frequently generated, or first becomes measurable, inside a warehouse or distribution centre — at goods-in when packaged products arrive, during pick-and-pack when secondary and tertiary packaging is applied, and at despatch when outbound shipments are consolidated. GOV.UK's guidance on collecting packaging data sets out a structured process: first identify which packaging activities apply (supplying under your brand, packing or filling, importing, supplying as empty, hiring or loaning, or supplying through an online marketplace), and only then assess what the packaging is made of and how much it weighs 5.

Translated into warehouse operations, that means a reporting-ready system needs to capture, at minimum: the packaging activity associated with each movement (is this product being packed or filled on-site, imported already packaged, or simply handled as empty packaging material); the material type of each packaging component (for example glass, aluminium, steel, plastic by polymer type, fibre-based composite, paper or card, or wood); the weight of packaging by material, not merely the weight of the product it contains; and the packaging level at which each component sits — primary packaging in contact with the product, secondary packaging such as an outer case or sleeve, or tertiary/transit packaging such as pallet wrap and shipping cartons used to move goods through the supply chain.

• Packaging activity per movement — packed/filled on-site, imported as filled packaging, supplied as empty packaging, or hired/loaned reusable packaging
• Material type per packaging component — distinguishing, for example, rigid plastic from flexible film, and glass or metal from fibre-based materials
• Weight by material, captured at the component level rather than as a single combined pack weight
• Packaging level — primary, secondary, or tertiary/transit — since obligations and, in some schemes, fee treatment can differ by level
• Destination and handling route — including whether packaging leaves the site with the product, is retained and reused internally, or is segregated as site waste
• Brand attribution — which brand or customer the packaging activity relates to, where a facility handles goods for multiple brand owners or co-pack clients

Destination matters because not all packaging a warehouse handles is reportable in the same way. Packaging that is sent out with a product to an end customer is generally treated differently from a facility's own organisational waste packaging — for example pallet wrap or case packaging that the site uses internally and disposes of itself, rather than packaging that travels onward in the supply chain. UK guidance has, in its update history, drawn a distinction around reporting self-managed organisation waste, which is a further reason warehouse teams need to tag packaging data with where and how it exits the facility rather than recording only an aggregate inbound or outbound tonnage 6.

The EU's Regulation 2025/40 adds a further layer relevant to warehousing specifically: it names fulfilment service providers as a distinct category of economic operator and states that they must ensure that handling, warehousing, and dispatching processes do not compromise the compliance of the packaging they handle 2. The Regulation also places separate obligations on packaging waste management operators to report packaging waste data annually to authorities and to producers, specifically to support producers' extended producer responsibility obligations 2. A warehouse operating in the EU, in other words, may sit inside the compliance chain in more than one capacity depending on what services it performs.

In the UK, obligated large producers submit packaging data through the Report Packaging Data service as a structured CSV file, built using terminology, time-period codes, and a file specification published by Defra and updated periodically; the service also accepts submissions from compliance schemes acting on a producer's behalf 1. GOV.UK's own update log for this guidance shows how frequently operational detail can change — for example, clarifications on notifying regulators within 28 days of ceasing to be a producer, updates to nation-of-sale reporting, and a 2026 refresh of the file specification used to build reporting files — which is a practical reason to treat specific fee amounts, tonnage thresholds, and submission deadlines as something to confirm on the live guidance at the time of filing rather than something to hard-code into an internal process.

Fees under UK EPR for packaging are intended to recover the costs of collecting and managing packaging waste and are influenced by eco-modulation: fee structures that adjust the base charge according to how recyclable or reusable a given packaging format is, so that packaging designed for easier recycling or reuse is expected to attract a lower effective charge than packaging that is harder to recycle. The EU Regulation 2025/40 builds a comparable principle directly into its producer obligations, requiring that extended producer responsibility schemes cover the necessary costs of collection, sorting, and recycling, incentivise eco-design and recyclability through modulated fees, and maintain financial transparency and accountability 2. Because eco-modulated fee criteria are set and revised by the relevant scheme administrator or regulator, a warehouse's material-level data — not just total tonnage — is what allows a producer to claim the correct modulated rate for each packaging format it uses.

California's SB 54 programme illustrates how a US state scheme can set funding obligations independently of weight-based fee modulation alone: CalRecycle describes the law as requiring producers to fund a programme intended to run over a ten-year period, alongside minimum recycled-content requirements for single-use packaging and plastic food service ware, with permanent implementing regulations approved by the state's Office of Administrative Law and filed on 1 May 2026 3. As of October 2026, CalRecycle's own programme page continues to publish updated guidance, covered-material-category lists, and extension and exemption criteria, which signals that the operational detail of SB 54 compliance was still being finalised through 2026 rather than fixed at the law's original passage.

A warehouse management system is well positioned to generate EPR-relevant data because it already tracks the attributes needed for the underlying logistics work — item masters, unit-of-measure and pack hierarchies, goods-in and goods-out transactions, and location or customer attribution. Extending that data model to carry packaging-specific attributes lets a WMS produce the inputs a producer needs for reporting, rather than requiring a separate manual survey of packaging each reporting period.

1. Extend the item or pack master to record packaging material composition and weight per component, at each packaging level (primary, secondary, tertiary), so this information travels with every transaction involving that item rather than being reconstructed later
2. Tag each packaging activity against the correct producer or brand owner, particularly in multi-client third-party logistics operations where several brand owners' goods move through the same facility
3. Capture destination and disposition data — product despatched to a customer, packaging retained for internal reuse, or packaging segregated as site waste — so reportable tonnage can be distinguished from a site's own organisational waste
4. Aggregate weights by material and reporting period in a form that maps onto the applicable scheme's reporting categories and file format, reducing the manual reconciliation needed before a filing deadline
5. Maintain an audit trail from the reported totals back to the individual transactions and source records that produced them, so a producer or its compliance scheme can respond to a regulator's query or data verification request

This is primarily a data-capture and traceability role rather than a compliance decision-making one. A WMS can structure and aggregate the packaging data a site generates, and can flag gaps where a packaging component has not been classified by material or weight, but the legal assessment of who is the obligated producer, which thresholds apply, and what fee rate or eco-modulation category a given packaging format falls into remains a producer or compliance-scheme responsibility, informed by current regulator guidance rather than by the warehouse system itself.

A single warehouse frequently supports more than one brand owner, more than one packaging activity, and sometimes more than one jurisdiction's reporting regime at once — for example a third-party logistics site in the UK handling a client's own-brand co-packing alongside straightforward pick-and-pack of pre-packaged goods for another client. In that setting, the warehouse's packaging data needs to be attributable not just by material and weight, but by which client or brand the packaging activity belongs to, because the reporting obligation, the fee liability, and in some cases the applicable scheme all sit with the producer, not with the facility operator.

Operators selling into both the UK and the EU, or into multiple US states, should expect genuinely separate reporting cycles, category definitions, and portals rather than a single harmonised process — GOV.UK's EPR for packaging guidance, the EU's Regulation 2025/40, and state-level US statutes such as SB 54 and SB 582 are independent legal instruments administered by different bodies, and a tonnage figure or material category that satisfies one regime's definitions will not necessarily map cleanly onto another's without reclassification. Building packaging master data with enough granularity from the outset — material, weight, packaging level, and the correct producer and jurisdiction tags — reduces the amount of rework needed each time a new reporting cycle or a new jurisdiction's requirements come into effect.