Packaging EPR Benchmarks
Sustainable Packaging and EPR KPIs: Recycled Content, Fees, Reuse and Reporting Benchmarks
Recycled content, recyclability, EPR fees, reuse trips, asset recovery, lightweighting and reporting effort: how to measure each KPI, what moves it, and which figures have a cited source.
Sustainable packaging and extended producer responsibility (EPR) programs run on connected KPIs: recycled content, recyclability, EPR fee per tonne, reuse trips, asset recovery, lightweighting realization and reporting effort. Use the ranges below as reference points for spotting a gap worth investigating, not as targets, and re-check them each reporting cycle as fee schedules and thresholds change.
Every figure here shows its basis. A superscript number links to a public source in the Sources list at the end, and the sentence states what that source covers. A figure marked no cited source is kept exactly as originally published because no public source stating it has been identified, so treat it as illustrative.
At a glance
| KPI | Typical | Strong | Basis |
|---|---|---|---|
| Recycled content, portfolio, mass basis | 10 to 25% | 35 to 50% (world-class beverage and rigid programs) | no cited source |
| UK Plastic Packaging Tax threshold | Tax due below 30% recycled plastic | Not stated | HMRC1 |
| Buffer above the binding mandate | Not stated | 3 to 5 points (stable program) | no cited source |
| Recyclability risk priority number | Not stated | Median below 40, none above 200 (mature program) | no cited source |
| EPR fee per tonne, portfolio-weighted | Not stated | $320 to $360 (healthy target) | no cited source |
| Trips per reusable asset | Not stated | 40 to 120 (well-run closed regional loops); above 150 (best-in-class totes) | no cited source |
| Reuse break-even against single-use | 8 to 25 trips | Not stated | no cited source |
| Asset recovery per cycle | Not stated | 96 to 99% (world-class closed loops) | no cited source |
| Asset loss cost, share of annual pool support | Not stated | Under 20% (healthy loop) | no cited source |
| Lightweighting realization | Not stated | 88 to 92% (well-controlled downgauge) | no cited source |
| Reporting hours per SKU per jurisdiction | 1 to 3 hours (common) | Below 1 hour per SKU (world-class) | no cited source |
Method: How the figures in this guide are sourced
A figure with a superscript number is stated by the cited source, listed under Sources with its publisher and access date. The cited figures are regulatory facts from HM Revenue & Customs guidance on the UK Plastic Packaging Tax and the European Commission's page on the EU packaging regulation. A figure marked no cited source is kept exactly as originally published because no public source stating it has been identified. It is illustrative, not measured industry data. Worked examples are arithmetic, not benchmarks.
Recycled content
Track recycled content against the mandate that binds you, not a vanity number. The UK Plastic Packaging Tax, for example, is due on plastic packaging components containing less than 30 percent recycled plastic1, at £228.82 per tonne from 1 April 20262.
In the EU, the Packaging and Packaging Waste Regulation (PPWR), Regulation (EU) 2025/40, has been in force since 11 February 2025 and applies from 12 August 20263. One of its objectives is to make all packaging on the EU market recyclable in an economically viable way by 20304.
PPWR sets rising per-application minimums climbing toward 50 percent and beyond for some contact-sensitive formats by the early 2030s no cited source. Confirm the exact percentages and dates for your formats in the regulation text before you set a target against them.
Typical portfolios today land in the 10 to 25 percent range on a mass basis; world-class beverage and rigid programs clear 35 to 50 percent no cited source.
The lever is supply security. Single-source rPET caps you near the mandate with no margin, so qualifying two certified streams and holding a 3 to 5 point buffer above target no cited source is what separates a stable program from one that fails on a bad supply month.
How to measure
- Divide recycled material mass by total packaging mass, per format and for the portfolio.
- Compare each format with the threshold of every mandate that applies to it.
What moves it
- Two qualified, certified recycled-material streams instead of one.
- A buffer held above the binding mandate.
Track content by format with the Packaging Recycled Content calculator.
Recyclability score
Recyclability, scored as an FMEA risk priority number (RPN), is a ranking rather than an absolute, so benchmark against your own portfolio distribution. Set an internal action line at the 75th to 90th percentile of your scored SKUs no cited source and drive everything above it into redesign.
A mature program keeps its median format below a raw RPN of 40 and carries no SKUs above 200; a neglected portfolio has a long tail of multilayer laminates scoring 150 to 300 no cited source.
The fastest lever is mono-materialization. Moving a laminate to a mono-structure that near-infrared (NIR) sorting can identify typically cuts the occurrence and detection scores together, often halving the RPN in one design pass no cited source.
How to measure
- Score every SKU on the same FMEA scale.
- Plot the portfolio distribution and set the action line from it.
What moves it
- Mono-materialization to NIR-sortable structures.
- Redesign of the laminate tail first.
Score formats with the Packaging Recyclability Score calculator, and cost a switch with the Packaging Material Substitution Cost calculator.
EPR fee per tonne
EPR fee per tonne is the money KPI, and it swings by material band more than by anything you can negotiate. Recyclable mono-materials sit near $300 per tonne in modulated schemes, while hard-to-recycle laminates reach $494 or draw bonus penalties no cited source.
A portfolio-weighted effective rate of $320 to $360 per tonne is a healthy target, and anything above $420 signals a heavy laminate tail no cited source. These dollar figures are not tied to a named scheme or year, so check them against the fee schedule of each scheme you report to.
The lever is band migration. For example, shifting a tonne from the $494 penalty band to the $300 recyclable band cuts $494 minus $300, or $194, of variable fee: roughly $190 per tonne.
How to measure
- Divide total EPR liability by all tonnes placed, including exempt tonnage, so the number reflects the real burden.
What moves it
- Band migration from penalty materials to recyclable ones.
- Fewer laminates in the portfolio tail.
Estimate fees by material with the EPR Fee Estimate calculator.
Reuse trips per asset
For reusable systems the KPI is trips per asset before retirement, because the economics live there. Low-turn or one-way export loops manage only 5 to 15 trips and rarely beat single-use no cited source.
Well-run closed regional loops hit 40 to 120 trips, and best-in-class returnable tote programs exceed 150 no cited source. Break-even against single-use typically lands between 8 and 25 trips, depending on format and asset cost no cited source.
The dominant lever is return rate. A loop losing 8 percent of assets per cycle instead of 2 percent can double effective support cost and push a 1.6-year payback past three years no cited source, so tracking recovery weekly matters more than chasing marginal cleaning savings.
How to measure
- Count trips per asset from first use to retirement.
- Compare the count with the break-even for that format and asset cost.
What moves it
- Return rate.
- Closed regional loops rather than open or export loops.
Asset recovery rate
Asset recovery rate and loss deserve their own KPI because they silently rewrite reusable ROI. World-class closed loops recover 96 to 99 percent of assets per cycle; open or long-haul loops often bleed to 88 to 93 percent no cited source.
Every lost tote is both a capital write-off and a replacement purchase. Benchmark loss cost as a share of annual pool support, and keep it under 20 percent for a healthy loop no cited source.
A two-point gain in recovery rate frequently outweighs any reduction in wash-bay cost no cited source.
How to measure
- Divide assets returned by assets shipped for each cycle, and review it weekly.
- Express loss cost as a share of annual pool support.
What moves it
- Barcode or RFID tracking.
- Deposit schemes.
- Named-account accountability.
Lightweighting realization
Lightweighting realization rate tells you whether paper savings became real savings. Theoretical mass removed is easy to claim; the KPI is the share that survives scrap, giveaway and yield loss.
A well-controlled downgauge realizes 88 to 92 percent, while a rushed change with rising damage rates can slip below 75 percent no cited source and occasionally go negative once returns and rework are counted.
Benchmark damage rate alongside it. If a gauge reduction lifts transit damage from 0.5 to above 1.5 percent, the realization gain is usually erased no cited source.
How to measure
- Divide realized mass savings, net of scrap, giveaway and yield loss, by theoretical mass removed.
- Track transit damage rate before and after the change.
What moves it
- Disciplined transit testing before rollout, not after complaints surface.
Net the savings against redesign and qualification cost with the Lightweighting Savings calculator.
Reporting efficiency
Reporting efficiency is the operational KPI most teams never measure and most consistently overspend on. Data collection commonly runs 1 to 3 hours per SKU per jurisdiction no cited source, dominated by chasing supplier declarations rather than the filing itself.
For example, a filer with 200 SKUs in 8 states, at 1 to 1.5 hours per SKU per jurisdiction, faces 1,600 to 2,400 hours a year: 200 x 8 x 1 = 1,600 and 200 x 8 x 1.5 = 2,400.
World-class programs cut this below 1 hour per SKU no cited source by holding standardized supplier compliance data year-round instead of scrambling at deadline. Payback on a supplier data portal is usually under a single reporting cycle.
How to measure
- Log hours per SKU per jurisdiction for each reporting cycle.
- Split the hours between data collection and the filing itself.
What moves it
- Supplier data quality.
- Certified supplier declarations on file ahead of the reporting window.
Read the KPIs as one scorecard
Read these KPIs as a connected scorecard, not a list. A portfolio can hit 35 percent recycled content no cited source and still carry a punishing fee per tonne if its recyclability tail is full of laminates, because content and recovery are independent axes.
Rank improvement projects by cost per point moved. Band migration usually buys the cheapest fee reduction, mono-materialization the cheapest recyclability gain, and return-rate work the cheapest reuse ROI.
How to build your own baseline
- Pick one KPI, write its definition down, and keep it fixed.
- Measure on a mass basis.
- Set targets that carry a buffer above the binding mandate.
- Re-benchmark each reporting cycle as fee schedules and thresholds ratchet upward.
- Compare against your own trend first and published ranges second.
Sources
- Check if you need to register for Plastic Packaging Tax. HM Revenue & Customs (GOV.UK). published February 12, 2026. Opening section on who pays the tax. Accessed September 30, 2026.
- Check if you need to register for Plastic Packaging Tax (rate passage). HM Revenue & Customs (GOV.UK). published February 12, 2026. Rate of the tax. Accessed September 30, 2026.
- Packaging waste (Regulation (EU) 2025/40 on packaging and packaging waste). European Commission, DG Environment. Legislation box (status and application date); objectives list. Accessed September 30, 2026.
- Packaging waste (PPWR objectives). European Commission, DG Environment. Objectives list. Accessed September 30, 2026.
Published 2026-07-01.