Short answer
The answer, before the reasoning
ESRS E5 should be implemented as a controlled physical-flow model, not as a collection of disconnected waste indicators. When resource use and circular economy are material, the undertaking links its policies, actions and targets to resource inflows, product and service outflows and waste outflows.
It identifies key materials, records total and secondary-resource weight, measures durability, repairability and designed recyclability where relevant, reconciles waste by stream and destination, explains boundaries and estimates, and connects material impacts, risks and opportunities to strategy and financial effects through ESRS 2.
ESRS E5 material-flow architecture: identify physical flows, then connect policies, actions, targets, metrics and evidence.
Why this question matters
Resource-use reporting often fails because procurement, operations, product design, logistics, waste contractors and finance hold different parts of the evidence. A recycled-content figure can cover one product family, a waste total can omit leased sites, and a circular-design claim can lack product-level support. ESRS E5 is designed to make these fragments understandable as one controlled system.
The reporting team should therefore start with the physical flow: what key materials enter the undertaking, how they are transformed, what products and services leave, what becomes waste, and where value-chain data or estimates are needed. Policies, actions, targets and financial effects are then attached to this model rather than drafted separately.
Quick orientation
At a glance
- Applies to
- Undertakings for which resource inflows, product/service outflows or waste outflows relate to material impacts, risks or opportunities.
- Primary decision
- How to build a traceable material-flow model and select evidence-ready E5 metrics and targets.
- Core sources
- Revised ESRS E5, ESRS 1 materiality/value-chain provisions and ESRS 2 general disclosure requirements.
- Common confusion
- Treating E5 as waste-only or combining secondary inputs, product design and waste outcomes in one opaque “circularity rate”.
- Technical status
- Commission-adopted revised ESRS dated 3 July 2026; final Official Journal and entry-into-force check required.
In practice
The ESRS E5 disclosure architecture
| DR | Core content | Evidence owner |
|---|---|---|
| E5-1 | Policies and integration of circular-economy principles or eco-design where relevant | Sustainability, procurement, product design |
| E5-2 | Key actions and resources | Operations, engineering, programme owners |
| E5-3 | Outcome-oriented targets and progress | Strategy, sustainability, finance |
| E5-4 | Key materials, total weight, breakdown and secondary resources | Procurement, ERP/material master |
| E5-5 | Product durability, repairability, designed recyclability and waste outflows | Product, quality, EHS, waste contractors |
1. Build the physical-flow model before selecting metrics
A useful flow model is sufficiently detailed to connect material impacts and dependencies to physical quantities, but it is not an unfiltered purchasing or waste ledger. Selection should follow the material IROs, quantities, strategic dependency, environmental pressure, critical-material content and decision-usefulness.
ESRS E5 material-flow architecture: identify physical flows, then connect policies, actions, targets, metrics and evidence.
In practice
| Flow layer | Questions | Control output |
|---|---|---|
| Resource inflows | Which raw materials, components, packaging and other resources are key? Which contain critical or strategic raw materials? | Key-material register with unit, weight, source and boundary |
| Operations | Where are materials transformed, lost, reused, recirculated or stored? | Site/process map and reconciliation |
| Products/services | Which product and packaging populations matter? What design characteristics affect life, repair and recyclability? | Product population and technical methodology |
| Waste outflows | Which waste streams arise, in what original-state weight and to which destination? | Waste destination register and treatment evidence |
| Value chain | Where are material dependencies and impacts upstream or downstream? | Direct-data or estimate decision register |
2. Resource inflows: define key materials with discipline
For each key material, maintain a concise description of its operational role and relevance. Where the distinction between technical and biological materials matters, preserve it. If a key material contains a critical or strategic raw material under the applicable EU classification, identify that content rather than treating only the finished component as the material.
In practice
| Metric field | Control question |
|---|---|
| Material identifier | Can procurement, operations and the reviewer identify the same population? |
| Unit and conversion | Is weight the controlled unit and are density or unit-to-weight conversions documented? |
| Boundary | Which entities, sites, purchases, tolling arrangements and inventory movements are included? |
| Total and breakdown | Does the material breakdown reconcile to total key-material weight? |
| Secondary resources | What qualifies as recycled, reused or other secondary input and what evidence supports it? |
| Critical/strategic content | What classification and component evidence support the statement? |
| Estimates | Which amounts use supplier declarations, engineering estimates or proxies? |
3. Product outflows: measure design characteristics, not aspirations
Depending on materiality and the product population, E5 product information addresses durability, repairability and the rate of products and packaging designed for recyclability. A defensible methodology defines the product population, weighting basis, period and technical test. Revenue-weighted, mass-weighted and unit-weighted results can differ materially, so the selected basis should be explained and consistently applied.
In practice
| Metric | Definition controls | Evidence |
|---|---|---|
| Durability | Expected useful life or durability characteristic, product coverage and test basis | Specifications, reliability tests, warranty data |
| Repairability | Scoring or criteria, parts/information availability and exclusions | Repair manuals, spare-parts systems, design review |
| Designed recyclability | Qualifying design criteria, denominator and weighting basis | Bill of materials, packaging specifications, approval |
| Circular services | Take-back, repair, refurbishment or service population and outcome | Contracts, platform and take-back records |
4. Waste outflows: reconcile stream, weight and destination
Waste reporting should preserve the original-state weight and a controlled stream taxonomy. Contractor labels such as “recovered”, “recycled”, “treated” or “zero waste to landfill” are not automatically reporting categories. Map treatment codes to preparation for reuse, recycling, other recovery, disposal, unknown destination or radioactive waste where relevant, and retain treatment evidence.
In practice
| Control | Risk | Practical test |
|---|---|---|
| Site completeness | Small, leased or project sites are omitted | Reconcile the site list to operations and consolidation |
| Original weight | Treatment changes weight after generation | Use original-state weight or document conversion |
| Destination evidence | Collection invoice does not prove final treatment | Use certificates, declarations, permits and sampling |
| Unknown destination | Recycling is overstated | Retain an explicit unknown category and improvement plan |
| Internal transfer | Waste moved between group sites is counted twice | Use transfer IDs and eliminate duplicates |
5. Policies, actions, targets and the waste hierarchy
E5-1 to E5-3 use the ESRS 2 general disclosure requirements. Policies should show scope, governance and value-chain coverage. Actions should identify interventions—material substitution, design change, efficiency, reuse, repair, take-back or waste prevention—and allocated resources. Targets should define outcome, boundary, baseline, target year, metric, method, milestones and progress. If no target exists, explain how effectiveness is tracked rather than inventing an aspiration for the report.
The waste hierarchy is a useful operating logic: prevention, preparation for reuse, recycling, other recovery and disposal. It helps organise actions and targets but should not be converted into an invented ESRS score or used to hide technical, safety or financial trade-offs.
6. Boundaries, value-chain data and estimates
The reporting undertaking is the same as for the related financial statements, but material sustainability information can extend upstream and downstream. Procurement inflows, product metrics and waste data can therefore use different metric-specific boundaries. Each boundary should be stated and reconciled rather than implied by one generic group statement.
Where direct value-chain data cannot be obtained after reasonable efforts, reasonable and supportable estimates or proxies can be used under ESRS 1. Document the data gap, alternatives considered, proxy, assumptions, uncertainty, coverage and improvement plan. An estimate is not a failure if it is transparent; unexplained precision is.
Metric controls for ESRS E5: every figure needs a defined population, unit, boundary, method, owner and review trail.
7. Link circularity to strategy and financial implications
Material E5 dependencies and changes can affect commodity costs, critical-material access, product-design compliance, extended-producer-responsibility costs, waste liabilities, useful lives, capex, revenue from repair/refurbishment and access to markets. Finance should trace the narrative to budgets, capex plans, procurement forecasts, provisions, product-development gates and ESRS 2 financial-effects analysis. The physical metrics support but do not replace that disclosure.
Eight-step implementation workflow
Confirm material E5 sub-topics and record the IROs.
Map entities, sites, products, materials, suppliers and waste streams.
Create the key-material register and controlled units/conversions.
Define product populations and durability, repairability and recyclability methods.
Create the waste-stream and destination mapping.
Link policies, actions and targets to the physical-flow model.
Reconcile metrics to sources and document estimates, limitations and comparatives.
Connect material dependencies and actions to strategy, financial planning and governance approval.
Hypothetical case: a diversified appliance manufacturer
The undertaking reports controlled key-material weights and secondary-resource shares, limits designed-recyclability and repairability results to product populations with validated methods, and presents take-back outcomes separately. Unverified contractor destinations remain “unknown” until evidence is obtained. Modular-design capex and critical-material exposure are linked to product-development and financial-planning records. The approach is stronger than extrapolating unsupported percentages to the whole group.
In practice
Weak versus stronger reporting
| Weak wording | Stronger structure |
|---|---|
| “Most products are circular and recyclable.” | Define product population, design criteria, weighting basis, result, evidence and limitation; distinguish design from actual recycling. |
| “We diverted 95% of waste from landfill.” | State generated waste, included sites, original weight, destination categories, treatment evidence and unknown destination. |
| “We use recycled materials wherever possible.” | Identify key materials, total and secondary amount/share, definition and evidence. |
| “Circularity reduces costs.” | Identify the IRO, financial transmission channel, time horizon, assumptions and finance evidence. |
In practice
Common mistakes and corrections
| Mistake | Correction |
|---|---|
| Starting with a generic KPI list | Start with material flows and IROs, then select relevant information. |
| Treating spend as weight | Use physical weight or controlled conversions and disclose estimates. |
| Combining input, product and waste measures | Keep the three concepts and denominators separate. |
| Using contractor labels without mapping | Maintain a controlled destination mapping and evidence hierarchy. |
| Omitting unknown outcomes | Disclose unknown destination and a data-improvement plan. |
| One boundary for every metric | Use metric-specific boundary and reconciliation records. |
Readiness
E5 evidence checklist
- Approved E5 materiality/IRO record and sub-topic scope.
- Key-material register, source extracts and weight conversion controls.
- Supplier evidence for secondary resources and critical/strategic classifications.
- Product populations and technical design methodologies.
- Waste stream mapping, tickets, invoices, treatment evidence and eliminations.
- Policy, action, target and resource records linked to IROs.
- Metric sheets with boundary, method, estimates, limitations and changes.
- Finance linkage and governance approval.
In practice
Connections to other ESRS
| Standard | Connection |
|---|---|
| ESRS 1 | Materiality, reporting undertaking, value chain and estimates. |
| ESRS 2 | IROs, strategy, financial effects, policies, actions, targets and metric methodology. |
| E1-E4 | Circularity interacts with emissions, pollution, water and biodiversity but does not replace those disclosures. |
| S3/S4 | Resource extraction, waste and product circularity can create community and consumer impacts. |
Sources
Primary sources
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