Circularity costs follow product responsibility and destination rules

The targeted revision of the Waste Framework Directive entered into force on 16 October 2025. It introduces common EU rules for extended producer responsibility (EPR) for textiles and footwear, while requiring every Member State to establish its own scheme. Producers will pay a fee for each product placed on the market, financing collection and subsequent re-use, preparation for re-use, recycling and disposal. The Commission describes eco-modulation that adjusts fees against sustainability criteria, including durability and recyclability. This establishes a mechanism, not a uniform fee that a supplier can insert into every order model.[S15]

The implementation clock has two distinct parts. The Commission states that Member States have 20 months to transpose the revised directive and 30 months to establish textile and footwear EPR schemes. Entry into force is therefore not evidence that registration portals, fee schedules and reporting processes were operational everywhere on that date. A supplier planning a sales route should record the directive milestone separately from the destination scheme's actual legal status, responsible authority, producer definition and opening date.[S15]

The policy context explains the attention given to textiles, but it does not provide an order-level fee. The Commission reports about 12.6 million tonnes of EU textile waste in 2019, with only one-fifth separately collected for re-use or recycling. Those figures describe a historical EU-wide waste stream. They do not measure an African factory's output, predict its future EPR bill or demonstrate that a particular garment is recyclable. A financial model should use verified scheme inputs rather than converting a sector waste total into an assumed charge per garment.[S15]

The revised rules also affect the boundary between used textiles and waste. The Commission states that all separately collected textiles will be considered waste and must undergo sorting before possible shipment. Unsorted textile waste falls within the Waste Shipment Regulation. For a supplier offered returned garments or collected offcuts, the operational question is therefore not answered by calling the material reusable. The record should establish condition, collection route, sorting status, intended shipment and the applicable waste or product classification before movement.[S15]

The milestone sequence in Exhibit 38 keeps the three legal mechanisms visible. It uses an ordered event scale rather than pretending that the intervals are proportional. National EPR implementation remains a separate verification task, while later packaging and unsold-stock provisions must not be collapsed into one circularity deadline.[S14][S15][S20]

A destination register should consequently carry a publication gate. Before a fee or deadline enters the sales model, the reviewer should identify the national legal instrument, the responsible scheme or authority, the covered product category, the obligated entity, the reporting period and the evidence of registration where required. Record the source date and the next review trigger. If only the EU framework has been checked, mark the national row unresolved rather than inserting a placeholder charge that later acquires the appearance of fact.

The same gate applies to eco-modulation. The Commission identifies durability and recyclability as factors, but that does not entitle the supplier to invent a discount for an untested garment. A claim of lower EPR cost needs the actual scheme formula, the product's assessed category and evidence accepted by that scheme. GFT would retain durability tests, material specifications and repair information as potentially useful product records, while keeping any financial effect conditional until the destination rules confirm it.[S15]

The Packaging and Packaging Waste Regulation (PPWR) begins application on 12 August 2026 on a phased basis. It establishes a harmonised framework for packaging and packaging waste across the Single Market. That date should open a packaging applicability review, not trigger every later requirement at once. The supplier and its buyer need to identify the packaging format, its use, the relevant provision, the economic-operator role and the application date before approving a design or declaring conformity.[S20]

The Commission's announcement provides a useful warning against copying headlines between product categories. A restriction on per- and polyfluoroalkyl substances in food-contact packaging is one of the measures entering application, with detailed limits and guidance for that use. An apparel carton, polybag or transport pallet wrapping is not made subject to an identical rule merely because it is packaging. The correct response is to test the actual material and intended use against the operative provisions, not to add a universal apparel PFAS certificate to the checklist.[S20]

Later milestones also need separate rows. The Commission describes harmonised packaging labels for waste sorting from 2028. It describes measures on empty space, certain single-use plastic packaging and re-use targets from 2030, alongside recycled-plastic content and recyclability requirements. These are different design and information questions with different conditions. A packaging register should not summarise them as a single 2030 packaging ban, nor should a current specification be represented as satisfying secondary legislation that remains under development.[S20]

For the factory, the packaging bill of materials should sit beside, but remain distinct from, the garment bill of materials. Record each sales bag, label substrate, hanger, carton, protective sheet, pallet wrap and returnable container where present. For each item, retain the supplier specification, material composition, weight basis, intended use, reuse arrangement and change history. These are GFT's proposed operating records. They do not presuppose that every data field is legally required for every format.

The measurement boundary matters when a buyer asks for a packaging reduction. A lighter polybag may reduce material in one component while a higher damage rate could increase replacement shipments or returns. GFT would therefore review material mass, product protection, expected trips for reusable formats and end-of-route evidence together. This is a design hypothesis to test with actual orders, not a claim that thinner packaging is always environmentally preferable. Any comparative environmental claim also needs the bounded evidence discussed in the claims chapter.

A reusable format needs its own operating proof. The record should identify the owner, the outward and return journeys, the inspection criterion, the cleaning process where relevant, loss rates and the point at which a damaged unit leaves the loop. Do not count a container as reused merely because it was designed for reuse. Equally, do not count all returned packaging as recycled without evidence of the accepted downstream treatment. The actual route and destination evidence must determine what the record can say.

Packaging EPR or registration duties should be checked separately from textile EPR. A single supplier declaration covering both can conceal different obligated parties, product populations and reporting periods. The proposed order register should therefore carry a packaging row with its own legal basis and a textile row with its own basis. Shared product quantities may feed both, but only after the reviewer confirms that the same quantity definition applies.[S15][S20]