Skip to content

How do the European systems differ from one another?

On a map of packaging EPR, Europe is a uniform block: every EU member state has been required to operate a scheme since the end of 2024, and the Packaging and Packaging Waste Regulation now applies the same law directly across all twenty-seven. Beneath that uniformity sit systems that differ more from each other than the European average differs from Canada's — in who owns the compliance body, whether one exists at all, what share of costs producers bear, what a tonne of plastic costs to license, and what the resulting numbers mean. This article maps that variation: the four institutional families Europe actually contains; the cost-coverage spread the directive's derogations permit; the fee dispersion and its causes; the performance distribution and what predicts position within it; the non-EU systems that solved the problem differently; and what the PPWR will and will not homogenise.

1. Four institutional families

The single most useful cut through Europe is not geography but who runs the compliance body.

Competitive private markets. Germany's roughly ten dual systems — most owned by waste-management or compliance groups rather than by producers — compete for producer clients over a shared physical collection layer, with market shares determined quarterly by a registry foundation acting in agreement with the competition authority. Austria opened its market in 2015; Slovakia, Slovenia, Poland, Bulgaria, Romania, Estonia, Latvia and Lithuania run multi-operator markets of varying maturity, generally without Germany's clearing-house apparatus. This family delivers the fee discipline documented in the German article and requires the boundary policing that most of its members have not built.

Producer-owned single bodies. The classic European form: Fost Plus (Belgium), CONAI (Italy, a consortium producers are required by law to join), Ecoembes (Spain), Citeo (France, a société anonyme with mission status), Repak (Ireland), EKO-KOM (Czechia), Valorlux, GreenPak, Green Dot Cyprus. Governance sits with fee-payers, with the structural consequence the French inspectorates stated plainly and this library treats as general (Theme 2).

State funds — no producer organisation at all. Croatia's Environmental Protection and Energy Efficiency Fund and Iceland's Recycling Fund collect producer levies and contract services directly; there is no PRO to govern, and therefore no producer-control problem — and no producer expertise or cost discipline either. Taiwan and Ecuador run analogous models outside Europe.

The state concession. Hungary abolished its PRO market in 2023, granting the entire waste concession — packaging EPR included — to a single state-designated concessionaire. It is the only European jurisdiction moving away from producer organisations, and the direction of travel is the exact opposite of Germany's.

Two further arrangements resist the taxonomy and are treated below: Sweden, which in 2024 inverted the North American direction of travel by returning collection operations to municipalities while producers keep paying (Section 6), and the United Kingdom, which since leaving the EU has dispensed with producer organisations altogether (Section 7).

2. The cost-coverage spread the law permits

"The EU requires producers to pay 100%" is the most common error in European EPR commentary. Article 8a of the Waste Framework Directive sets full net cost as the baseline — but permits member states to drop to 80% for schemes established after 2018 and 50% for pre-2018 schemes serving national-only targets, and the derogations are used. France's household packaging coverage is officially 75% and contested by local authorities at 45–55%; Italy's has historically run near 80%. The European Court of Auditors found in 2025 that producer fees still did not fully cover waste-management costs in Poland and Portugal, years after the obligation took effect, and that schemes were not fully operational for all streams in Greece.

The practical consequence for comparison is large: a French or Italian fee finances roughly four-fifths of a system, while a German or Belgian fee finances all of it. Fee levels are not comparable without knowing the denominator (the fee-levels article) — and neither, more subtly, is scheme "efficiency," since a partial-coverage system's costs are partly invisible in municipal budgets.

3. Fees: a twenty-three-fold spread, and why

The verified schedules assembled for this library show plastics licensing fees ranging across the EU-27 from roughly €71 per tonne in Greece to €1,640 in Sweden — a twenty-three-fold spread within a single legal framework — with glass spanning fifty-eight-fold. Belgium prices nineteen-odd plastic subcategories from €360 per tonne for clear PET to €4,419 for non-recyclable categories; the Netherlands runs a seventy-eight-fold spread inside one tariff, from €17 per tonne for paper to €1,320 for flexible plastics.

Four causes account for most of the dispersion, and none of them is scheme quality. Coverage differs (Section 2). Deposit systems remove the highest-value containers, so a post-deposit fee is levied on a poorer residual basket — which is why Germany's average per-tonne plastics fee is high and its system is not therefore expensive. Cost structures genuinely differ: labour, collection density, landfill pricing and sorting maturity. And structure differs: granular category systems price recyclability that two-category systems average away.

The two major comparative studies — one financed by German dual systems, one produced for the packaging industry by a waste-company subsidiary, both identified as interested in the fee-levels article — converge on the finding that matters most here: fee level does not predict performance. Expensive systems are not better systems, and the correlation the industry study does report runs to fee structure, on a recycling-rate outcome, cross-sectionally.

4. Performance: the distribution, and what sits behind it

The EU recycled 67.5% of packaging waste in 2023, close to the 2030 target of 70% and essentially unchanged in a decade. The distribution beneath that average is wide: seven member states above 70% (Belgium 79.7%, the Netherlands 75.8%, Italy 75.6%, Czechia 74.8%, Slovenia 73.6%, Slovakia 71.9%, Spain 70.5%), against Romania at 37.3%, Hungary 42.8% and Malta 44.4%. For plastics — the material driving the entire policy wave — only Belgium (59.5%) and Latvia (59.2%) exceed 55%, while France sits at 25.7% after three decades of packaging EPR.

Three readings follow. First, scheme presence does not predict performance: every one of those states has had a scheme for years, and France's position is the standing refutation of any simple institutional story. Second, the constraint has moved downstream: the European Court of Auditors found secondary-material prices near zero for glass and paper in audited states, material hauled hundreds of kilometres for want of demand, and facility closures — a rate is ultimately a market outcome. Third, the numbers changed when the counting did: the 2020 calculation-point reform cut the EU plastics figure by three points and Germany's reported aluminium rate from 90.1% to 55.5% with no physical change (the measurement article), which means the pre-2020 and post-2020 European records are different measurement systems and most published time series cross the break unremarked.

5. Central and eastern Europe, where the range is widest

Western systems dominate the comparative literature, and this distorts the picture in one specific way: the EU's best and worst packaging performers are both in the east.

Czechia recycles 74.8% of packaging waste — above Germany, above the Netherlands — with no deposit system at all, on a model built instead around one of the densest municipal container networks in Europe, administered by EKO-KOM, a joint-stock company owned by its member producers and operating on a non-profit basis. Slovenia (73.6%) has been repeatedly identified by the European Environment Agency as one of the few member states on track for both 2025 targets. Slovakia (71.9%) runs a competitive multi-operator market and launched a deposit system in 2022 whose return rate moved from 71% in its first year to 92% in its second.

Romania sits at the other end at 37.3% — the lowest in the Union — despite a legal framework since 2004, multiple licensed producer organisations, and one of Europe's largest deposit launches in 2023; its market has seen repeated licence withdrawals. Poland, the region's largest economy, faced Commission infringement proceedings in 2023 over incomplete transposition of the EPR provisions, had auditors find its producer fees insufficient to cover waste-management costs, and has postponed a full EPR reform repeatedly.

Two things follow, and both matter for how the region is used as evidence.

First, the east–west framing is empirically wrong. The variation within central and eastern Europe is wider than the gap between any regional averages, and Czechia's position is a standing rebuke to accounts that treat performance as a function of national income.

Second — and this is the region's most under-examined feature — several of these states run competitive multi-operator markets without the institutional apparatus that makes competition safe. Bulgaria, Romania, Slovenia and the Baltic states all license multiple organisations, but none has built anything resembling Germany's registry foundation and clearing-house machinery for allocating market shares and policing free-riding. Competitive EPR without a clearing house is precisely the configuration Theme 2 identifies as carrying the highest risk of a race to the bottom on reported tonnage, and it is operating in six member states now.

The Baltics add a further institutional variant worth knowing before comparing fees. Latvia — one of only two member states above 55% for plastics, at 59.2% — structures compliance as exemption from the natural resources tax rather than as a direct fee, an unusual hybrid of fiscal and producer-responsibility instruments that makes its "fee level" not straightforwardly comparable with anyone else's. Lithuania's 2016 deposit launch cut wasted containers from roughly 113 per person a year to 14 within two years.

6. Arrival dates, and why "years since establishment" is a bad variable

Comparative work routinely uses programme age as an explanatory variable. Europe makes that hazardous, because the founding date and the date a system became full producer responsibility can be two decades apart.

Finland is the clean illustration: it is habitually listed among the early adopters, but full producer responsibility arrived only with the Waste Act reform taking effect in 2014, while its deposit-return system — returning close to 97% — long predates and substantially outperforms the packaging scheme it is usually credited to. Sweden, one of the four original 1994 systems, has arguably the most-changed design in Europe: producers still fund, but since 2024 municipalities operate collection again.

At the other end, Denmark is the EU's newest packaging EPR system, repeatedly delayed before finally starting on 1 October 2025, with multiple collective schemes registered with the national producer-responsibility body. It is also about to run an experiment nobody planned: Denmark cut producer fees for 2026, which makes it the rare case where a fee reduction can be observed against retail prices. Almost all pass-through evidence concerns fee increases, and the assumption that the relationship is symmetric has never been tested (the pass-through article). Denmark will test it.

The practical instruction is to date a system by the regime whose effects are being measured, not by the year a producer-responsibility ordinance first appeared. On that basis Europe contains systems ranging from thirty-five years old to under one — inside the same nominal "all member states have had schemes for years."

7. The systems outside the frame

Four non-EU European arrangements are worth holding in view because they answer the same problem differently.

The United Kingdom is now the largest European system outside EU law, and structurally the most unusual in the world: it has no producer responsibility organisation at all. PackUK, a scheme administrator appointed by the four UK governments, sets the fees itself and pays local authorities directly, with the four environmental regulators handling data assurance. Three consequences follow. It is the only major system that publishes its fee methodology, because the body setting fees is a public one (the transparency article). It pays 100% of modelled efficient local-authority costs rather than 100% of actual costs — a design choice made nowhere else, which builds yardstick benchmarking into the payment in the way Maine does in the United States, and which guarantees a permanent dispute about the model. And it obligates packaging only: newspapers are out of scope entirely. Reporting ran from 2023 and the first fees were invoiced in October 2025; a deposit-return scheme is legislated for October 2027. The UK also published two official 2024 recycling rates eleven points apart — 64.1% on the legacy methodology, 75.2% on the new one — in a single release, which is the cleanest illustration anywhere of the point the measurement article makes at length.

Switzerland achieves high recovery — PET beverage bottles above 80%, glass above 90% — with no comprehensive packaging EPR at all: material-specific non-profits run advance recycling fees on beverage containers, aluminium and glass, and dense drop-off infrastructure does the rest. It is the standing counter-example to the assumption that producer responsibility is the only route to high performance.

Norway pairs a producer-owned material-company structure with a deposit system whose incentive is inverted: the environmental tax on producers falls as the return rate rises, so performance itself reduces producer cost — a design feature almost nobody has copied and which contrasts sharply with operators elsewhere that retain unredeemed deposits (Theme 7).

Russia and the post-Soviet systems run state-administered variants: producers meet standards themselves or pay an ecological fee to the state, with a phased path to full coverage under the 2023 reform; Belarus and Kazakhstan use single state operators. These are EPR without a producer organisation, and their reported figures are not comparable to Eurostat's.

8. What the PPWR will homogenise — and what it will not

The regulation ends definitional fragmentation: one producer definition, one national-register format, one recyclability grading, one modulation basis, one label (the PPWR article). From roughly 2029, a fee-modulation criterion will be common across the Union for the first time — the harmonisation the 2018 directive's unused clause failed to deliver.

What it leaves intact is precisely the variation this article maps. Member states keep their scheme designs and ownership structures: Germany's competitive market, Croatia's state fund, Hungary's concession and Citeo's mission company all persist. Fee levels remain national and will continue to reflect genuinely different costs. Cost-coverage derogations are a directive matter, not a PPWR one. And the enforcement capacity on which everything depends stays national — which is why the European Court of Auditors' findings about fees not covering costs and schemes not fully operating are the most predictive evidence in this article about how the PPWR's 2030 deadlines will actually land.

The synthesis for a reader comparing European systems: treat the legal frame as increasingly uniform and the institutions, money and numbers as not comparable without their bases. Europe's value to the field is that it contains almost every institutional answer to the EPR design problem running simultaneously under one directive — and its frustration is that thirty years of that natural experiment have produced, as Theme 6 records, no causal evaluation of any of it.

References

  • Directive 2008/98/EC, Art. 8a(4) — full net cost and the 80%/50% derogations; Directive 94/62/EC as amended, Art. 6 — the 2025 and 2030 targets; Regulation (EU) 2025/40 — the harmonising provisions, with the verification caveats set out in the PPWR article.
  • Eurostat, packaging waste statistics (2023 reference year) — the 67.5% aggregate, the member-state distribution and the plastics figures; Commission Implementing Decision (EU) 2019/665 — the calculation-point reform; European Environment Agency country profiles — the German aluminium series.
  • European Court of Auditors, Special Report 23/2025 (Municipal waste management) — cost coverage in Poland and Portugal, operational gaps in Greece, and the secondary-market findings.
  • Fee schedules and comparative studies: Fost Plus 2026 Green Dot rates; Verpact 2026 rates; adelphi (2025), Efficiency and Performance of Packaging EPR Systems in the EU (financed by nine German dual-system operators); EUROPEN (2026), produced by CIRCPACK by Veolia — both interested-party studies, identified as such in the fee-levels article.
  • Institutional detail: German VerpackG (2019) and the Zentrale Stelle Verpackungsregister's market-share and audit functions; Austrian market opening (2015) and the European Commission's ARA decision (2016); CONAI, Ecoembes, Citeo, Repak, EKO-KOM governance documentation; Croatia's Environmental Protection and Energy Efficiency Fund; Iceland's Recycling Fund; Hungary's 2023 concession; Sweden's 2024 municipal collection reform.
  • Central and eastern Europe: Czech Packaging Act No. 477/2001 and EKO-KOM's corporate form; Slovak Waste Act No. 79/2015 and the 2022 deposit return figures; Slovenian packaging decree and the European Environment Agency's 2025-target assessments; Romanian Law 249/2015 and the 2022 Eurostat figure; Polish packaging act (2013), the Commission's 2023 infringement proceedings and the European Court of Auditors' cost-coverage findings; Bulgarian Waste Management Act; Latvian Packaging Law and Natural Resources Tax Law (the tax-exemption compliance route); Lithuanian packaging law and post-2016 deposit data; Estonian Packaging Act.
  • Arrival dates and the late systems: Finnish Waste Act 646/2011 (full producer responsibility from 2014) and national deposit return rates; Danish packaging producer responsibility from 1 October 2025, and the 2026 fee reduction.
  • United Kingdom: Producer Responsibility Obligations (Packaging and Packaging Waste) Regulations 2024; PackUK's scheme-administrator role and published fee methodology; the modelled-efficient-cost basis; the two 2024 provisional rates (64.1% legacy and 75.2% new-methodology) as published by DEFRA; deposit return scheme legislated for October 2027.
  • Non-EU systems: Swiss beverage-container ordinance and material fee organisations (PET-Recycling Schweiz, IGORA, VetroSwiss); Norwegian environmental tax and deposit structure; Russian Federal Law 89-FZ as reformed in 2023.
  • French cost-coverage dispute: CIFREP annual report (2025) — the official 75% against local-government estimates of 45–55%, as recorded in the regulator-capacity article.

Verification note: the major Western European systems are documented in this library from primary and official sources; the central and eastern European institutional descriptions are compiled overview and carry the lower verification grade. See Sources and method for how the two grades are defined.