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EU Ecolabel, PEF and LCA for electronic products

Guide - EU Ecolabel, PEF and LCA

Public procurement bodies, large retailers and Green Deal regulators increasingly ask electronics manufacturers for a quantified, third-party environmental claim attached to their product. Three instruments dominate the European landscape: the EU Ecolabel under Regulation (EC) 66/2010, a voluntary Type I multi-criteria label awarded above a threshold; the Product Environmental Footprint (PEF) under Commission Recommendation (EU) 2021/2279, a harmonised life cycle assessment methodology that will become enforceable through the Green Claims Directive and ESPR delegated acts; and ISO life cycle assessment, organised by ISO 14040, ISO 14044 and the Type III declaration regime of ISO 14025. This guide explains how the three layers fit together, which electronic product categories are eligible today, what the sixteen PEF impact categories measure, how an Environmental Product Declaration (EPD) is built, and the pitfalls that void a life cycle claim before a public buyer or a market surveillance authority.

European environmental marking rests on three layers that should not be conflated. ISO 14020 organises them into three families, each with its own role, its own verification regime and its own audience.

TypeStandardNatureAudienceVerification
Type IISO 14024Multi-criteria label, pass or failConsumer and procurementThird party, accredited
Type IIISO 14021Self-declared single-attribute claimConsumerSelf-declared, no third party
Type IIIISO 14025Quantified declaration (EPD) on a full LCAB2B, procurement, constructionThird party, programme operator

The EU Ecolabel is the European reference Type I label. The Blue Angel (Germany), the Nordic Swan (Nordic countries) and TCO Certified (electronics) are other Type I labels, with their own criteria. Type II claims (recyclable, biodegradable, low-carbon) are the most legally exposed under the Green Claims Directive proposal: they bear no third-party verification and are, in practice, the main vector of greenwashing. Type III declarations are the most quantitative: they do not state a pass or fail threshold but disclose a full set of life cycle indicators, computed through an underlying LCA, verified and published by a programme operator.

PEF stands across these three layers. It is a methodology, not a label. A PEF study can feed a Type I (e.g. EU Ecolabel criteria when they reference PEF), a Type II (carbon footprint claim) or a Type III (an EPD published by a programme operator). The Green Claims Directive proposal explicitly elevates PEF to the default method for substantiating explicit environmental claims at EU level.

Regulation (EC) 66/2010 of 25 November 2009 sets the legal framework of the EU Ecolabel. It replaced an earlier regulation of 2000 and structures the scheme around four bodies: the European Commission (DG Environment), the EU Ecolabel Board (EUEB) representing Member States and stakeholders, national competent bodies in each Member State (the awarding authorities), and the manufacturers or service providers applying for a licence.

The EU Ecolabel is a Type I label per ISO 14024: multi-criteria, life-cycle-based, threshold-based and third-party verified. Criteria are established product group by product group through a Commission Decision after a multi-year preparatory study coordinated by the JRC (Joint Research Centre) and stakeholder consultation. Each criteria set is generally valid for six years and is revised before expiry.

The product is granted the label if and only if it meets each of the mandatory criteria of the applicable Decision. Each criterion specifies the verification mode: test report from an accredited laboratory, supplier declaration, technical file, on-site inspection. The licence is awarded by the national competent body of the Member State chosen by the applicant; it is valid across the entire Union and remains in force as long as the underlying criteria remain in force, typically three years renewable.

Coverage of electronics by the EU Ecolabel is narrower than for chemicals, paper or textiles. As of 2026, two electronic groups have an active criteria set.

Product groupDecisionStatus
Electronic displays (televisions, monitors, signage)Commission Decision (EU) 2020/1804, 27 November 2020In force, revision scheduled
Personal computers, notebooks, tabletsCommission Decision (EU) 2016/1371In force, revision in progress

Smartphones, networking equipment, audio devices, smart-home electronics, industrial electronics and most embedded systems are not yet covered by a dedicated EU Ecolabel set. For these categories, manufacturers commonly turn to TCO Certified (a generic and influential Type I label for IT and display equipment), to Blue Angel sector-specific sets (RAL-UZ 78c for computers, for instance) or to the Nordic Swan.

Typical criteria for an electronic product

Section titled “Typical criteria for an electronic product”

A criteria set under the EU Ecolabel for an electronic product typically covers seven dimensions, each binding the applicant.

  1. Energy efficiency: typically articulated with the EU Energy Label and Ecodesign Regulation. Compliance with a threshold tighter than the Ecodesign mandatory minimum is required, often the top class of the energy label.
  2. Hazardous substances and material restrictions: aligned with REACH (Substances of Very High Concern) and RoHS Directive 2011/65/EU thresholds, often with stricter limits than the regulatory minimum (e.g. halogen-free plastics, restrictions on flame retardants).
  3. Design for repair and disassembly: minimum number of standardised screws or clips, no structural adhesives on critical components, disassembly time below a target, availability of spare parts over a defined horizon.
  4. Recyclability: design ensuring separation of major fractions, marking of plastics per ISO 11469, minimum recycled content where applicable.
  5. Packaging: recycled fibres, restrictions on heavy metals in printing inks, optimisation of volume-to-weight ratio.
  6. End-of-life take-back: producer obligation linked to the WEEE Directive 2012/19/EU, sometimes reinforced by a manufacturer take-back scheme.
  7. Durability and warranty: minimum commercial warranty over the EU mandatory minimum, software update support over a defined period for connected products.

For the regulatory context on ecodesign and the energy label, see the ESPR guide and the ErP and ecodesign for energy efficiency guide. For the WEEE side, see the WEEE electronics waste guide.

The application file is submitted to a national competent body. The applicant chooses any Member State competent body; the licence is valid across the Union. The file gathers, for each criterion, the evidence required (test reports, declarations, technical documents). On-site verification by the competent body is generally part of the procedure.

Fees are set by each Member State: an application fee and an annual fee proportional to the turnover of the labelled products are levied, with discounts for SMEs and microenterprises. The exact fee schedule is published by the competent body of the chosen Member State. The total procedure (from preparatory dossier to grant of the licence) generally takes several months for an electronic product, depending on the maturity of the technical file and the verification load.

PEF is the European methodology for measuring product environmental performance over the life cycle. It was launched by Commission Recommendation 2013/179/EU and updated by Commission Recommendation (EU) 2021/2279 of 15 December 2021. PEF is built on ISO 14040 and ISO 14044, with EU-specific prescriptive choices to make studies comparable across applicants and across products of the same category.

PEF was initially a recommended methodology, with no obligation to use it. Two regulatory texts are progressively converting it into a binding rule.

The first is the Green Claims Directive, proposed by the Commission in March 2023, expected to be adopted over 2025-2026. Once adopted, any explicit environmental claim made to a consumer in the Union (label, score, statement) will have to be substantiated by a method recognised at EU level. PEF is referenced as the default method for life cycle claims. Type III declarations under ISO 14025 (EPDs) are also referenced, provided they meet a list of conditions equivalent to PEF requirements.

The second is the ESPR Regulation (EU) 2024/1781. The carbon and environmental footprint axis of Article 5 will, for each priority product group, set declaration requirements via a delegated act. The targeted method is PEF where a PEFCR exists, or an equivalent LCA framework. The Digital Product Passport (DPP) is the carrier of these data. See the ESPR guide for the cross-cutting framework.

Product Environmental Footprint Category Rules (PEFCR)

Section titled “Product Environmental Footprint Category Rules (PEFCR)”

A PEFCR is a sector-specific document that fixes, for a given product category, the choices that ISO 14040 / 14044 leaves open: functional unit, system boundary, allocation rules, mandatory data sources, data quality requirements, top hotspot processes, default scenarios for the use phase and end-of-life phase, and the impact category presentation format.

The Commission has published PEFCR for several categories (dairy products, beer, paints, decorative paints, intermediate paper products, leather, photovoltaic electricity generation, household batteries, IT equipment storage, T-shirts, packaged water, pet food, footwear, household detergents, dishwashing detergents, and others). Two PEF studies on the same product category are comparable only if they apply the same PEFCR.

For an electronic product not yet covered by a dedicated PEFCR, two options exist: apply the most relevant existing PEFCR (e.g. household batteries for an embedded battery product, IT storage for a storage device), or conduct an LCA per ISO 14040 / 14044 without a PEFCR, with explicit disclosure that the result is not legally comparable.

PEF reports against sixteen impact categories. The list below also indicates the impact assessment method retained by the Commission for each category.

CategoryMethod
Climate changeIPCC 2013, 100 years GWP
Ozone depletionWMO 2014
Particulate matterFantke et al. 2016 (UNEP)
Ionising radiation, human healthFrischknecht et al. 2000
Photochemical ozone formationLOTOS-EUROS, ReCiPe 2008
Acidificationaccumulated exceedance, Posch et al. 2008
Terrestrial eutrophicationaccumulated exceedance, Seppala et al. 2006
Freshwater eutrophicationEUTREND, ReCiPe
Marine eutrophicationEUTREND, ReCiPe
Ecotoxicity, freshwaterUSEtox 2.1
Land usesoil quality index, LANCA
Water useAWARE method, UNEP 2016
Resource use, fossilsCML 2002
Resource use, minerals and metalsCML 2002
Human toxicity, cancer effectsUSEtox 2.1
Human toxicity, non-cancer effectsUSEtox 2.1

These methods are not interchangeable: a study citing a single climate change category with another method (e.g. ReCiPe Midpoint Hierarchist instead of IPCC 2013) is not PEF-compliant.

PEF covers the five life cycle stages of the product, from cradle to grave.

  1. Raw materials acquisition and pre-processing: extraction, primary processing of metals and plastics, semiconductors, batteries, glass, paper packaging.
  2. Manufacturing: assembly, soldering, surface treatment, electrical and functional testing.
  3. Distribution: transport from factory to point of sale, primary, secondary and tertiary packaging.
  4. Use: in-service energy consumption, ancillary consumables (cables, batteries replaced), maintenance.
  5. End of life: collection, sorting, depollution, materials recovery, energy recovery, residual disposal.

For energy-using electronic products, the use phase generally dominates the climate change category, often above 50 percent of the total. Cutting the boundary before the use phase produces a biased result.

PEF allows the sixteen categories to be aggregated into a single weighted score. The weighting factors are published by the Joint Research Centre under the name Environmental Footprint (EF) weighting factors. They are based on a multi-criteria analysis combining the global mitigation potential and the level of scientific certainty of each category.

The single score is a communication aid, not the result of the study. PEF requires that the sixteen individual categories also be disclosed, and that the weighting factors used be cited. A single-score figure stated without disclosure of the weighting set is not a PEF-compliant communication.

The PEF method is built on the international standards ISO 14040 and ISO 14044, which set the general principles of life cycle assessment.

ISO 14040:2006 sets the principles and framework: iterative method, life cycle perspective, scientific rigour, transparency, sensitivity analysis. ISO 14044:2006, amended in 2017 (AMD 1) and 2020 (AMD 2), gives the requirements and guidelines: definition of goal and scope, life cycle inventory analysis (LCI), life cycle impact assessment (LCIA), interpretation. The amendments tighten the rules on functional unit definition, allocation, and reporting.

A PEF study is, in substance, an ISO 14040 / 14044 LCA with the additional EU-specific prescriptions of the PEF method (impact category choices, weighting factors, PEFCR). An ISO 14040 / 14044 study that does not respect these prescriptions is a perfectly valid LCA but is not a PEF.

ISO 14025:2006 governs Type III environmental product declarations (EPD). An EPD is a quantified communication, based on an LCA performed per ISO 14040 / 14044 and in line with a Product Category Rule (PCR) issued by a programme operator, and verified by an independent third party.

EPDs originated in the construction sector (where they are now widespread: cement, steel, wood, insulation, glazing) and are gaining traction in electronics. The main programme operators are:

  • International EPD System (Sweden), the historic operator with a worldwide reach.
  • IBU (Institut Bauen und Umwelt, Germany), strong in construction products sold in central Europe.
  • INIES (France), the official database for construction products and equipment used in French construction.
  • EPD Norge, EPD Italy, EPD Ireland and other national operators.

For an electronic product, an EPD is generally a B2B vehicle, used to respond to procurement specifications from public buyers, data-centre operators or industrial integrators. It is not a label awarded above a threshold (unlike the EU Ecolabel) but a structured quantitative communication.

The three instruments are complementary, not substitutes. The table below summarises the typical use case for each.

InstrumentAudienceFormatPass or failTypical use case
EU EcolabelConsumer, public procurementLogo on productYes, above thresholdDisplay or computer for retail or public procurement
PEF studyRegulator, B2BMulti-page reportNo, quantitativeSubstantiation of an explicit environmental claim, ESPR DPP carbon axis
EPD per ISO 14025B2B, procurement, data centreStandardised public documentNo, quantitativeBid response for data centre, building integration, large industrial customer
Type II self-declared claimConsumerLogo or textNoSingle-attribute claim (recyclable, low-carbon) at the manufacturer's risk

For a manufacturer of consumer displays seeking visibility in retail and on public procurement, the EU Ecolabel is the most direct vehicle. For a manufacturer of professional equipment sold to public buyers or to data centres, an EPD per ISO 14025 published in an established programme is generally the most relevant route. For internal eco-design steering, the underlying PEF or LCA study is the management tool, with or without external publication.

Other Type I ecolabels relevant to electronics

Section titled “Other Type I ecolabels relevant to electronics”

The EU Ecolabel is one Type I label among several. For electronics, four others are particularly active.

LabelOperatorStrength on electronics
TCO CertifiedTCO Development (Sweden)Dominant on displays, laptops, smartphones in public procurement
Blue AngelFederal Environment Agency (Germany)Strong on IT equipment in Germany and central Europe
Nordic SwanNordic EcolabellingLimited on electronics, strong on detergents and paper
Energy StarEPA (United States)Use phase only, no full life cycle

A note on Energy Star: the EU-US bilateral agreement covering office equipment expired in 2018 for displays and printers. Energy Star remains a US programme; its use in the EU is voluntary and bears no harmonised legal value. It focuses on the use phase only and does not constitute a full life cycle Type I label. See the Energy Star programme guide for the US side.

The pitfalls below are recurrent in PEF, LCA and ecolabel programmes for electronic products. Each is a documentation or scope issue that can void a claim before a public buyer or under the future Green Claims Directive.

PitfallConsequenceAction
PEF without applicable PEFCRResults not legally comparable, claim invalid for the future Green Claims DirectiveApply the most relevant PEFCR; if none, conduct an ISO 14040 / 14044 LCA and disclose absence of PEFCR
Single score reported without weighting disclosurePEF non-compliance, communication invalidDisclose the sixteen categories and the EF weighting set used
Secondary data on top-three hotspot processesInsufficient data quality, study downgraded or non-compliantCollect primary data on the three top hotspot processes (typically semiconductors, PCBA, battery for an electronic product)
Type II claim without backingGreenwashing risk, sanction under the Green Claims DirectiveMove to Type I (Ecolabel) or Type III (EPD) verified by a third party
Energy Label and Ecolabel confusionFalse communication, complaint riskDistinguish: the Energy Label is mandatory per the energy labelling Regulation; the Ecolabel is voluntary per Regulation (EC) 66/2010
LCA boundary cut before use phase for energy-using productDominant impact masked, biased communicationAlways include the use phase for an energy-using product, with a use scenario aligned with the applicable PEFCR
Generic proxy datasets for Asian componentsData quality rating downgraded, study deemed insufficientContractualise environmental data with the supplier at sourcing stage, in line with PEFCR data quality requirements
EU Ecolabel licence not renewedLoss of the right to display the logoPlan renewal twelve months before expiry, track Decision revisions

Articulation with the Green Deal regulatory body

Section titled “Articulation with the Green Deal regulatory body”

PEF and the EU Ecolabel do not stand in isolation. They form part of a coherent body of European law that frames environmental marketing of products. The main interconnections are summarised below.

InstrumentArticulation with PEF / Ecolabel
ESPR Regulation (EU) 2024/1781Carbon and environmental footprint axis (Article 5) implemented via PEF, footprint data hosted in the DPP
Ecodesign Directive 2009/125/EC (ErP)Energy efficiency thresholds aligned with EU Ecolabel criteria
Energy Labelling Regulation (EU) 2017/1369Mandatory information complementary to the voluntary Ecolabel
RoHS Directive 2011/65/EU and REACH Regulation (EC) 1907/2006Mandatory base, often reinforced by Ecolabel criteria
WEEE Directive 2012/19/EUEnd-of-life infrastructure, complementary to the take-back criterion of the Ecolabel
Green Claims Directive (2023 proposal)Future binding regime for explicit environmental claims, PEF as default method
Empowering Consumers Directive (EU) 2024/825Ban on unsubstantiated generic claims (eco-friendly, green) without recognised certification
Construction Products Regulation (EU) 2024/3110EPD per ISO 14025 mandatory for sustainability information on construction products

For the ESPR guide, the Cyber Resilience Act guide and the WEEE guide, see the cross-references. For a complete glossary of the terms (PEF, PEFCR, EPD, PCR, LCA, EF weighting), see the spilma glossary.

Practical steering for an electronics design office

Section titled “Practical steering for an electronics design office”

For an electronics design office that wants to anticipate the convergence of the Green Claims Directive, the ESPR delegated acts and the procurement specifications of large public and private buyers, three operational steps stand out.

  1. Map the eligible categories at the start of the project. Is the product covered by an EU Ecolabel criteria set (display, computer) or by an existing PEFCR (battery, IT storage)? The answer determines the achievable level of formal claim.
  2. Build a data quality programme from the sourcing stage. The three top hotspot processes for a typical electronic product (semiconductor manufacturing, PCBA assembly, battery cell) must rely on supplier-provided primary data and not on generic datasets. This is contractualised at component RFQ stage, with traceable evidence stored alongside the technical file.
  3. Choose the appropriate publication vehicle. A consumer electronic product for retail benefits from a Type I label (EU Ecolabel, TCO Certified, Blue Angel). A professional product in B2B benefits from a Type III declaration (EPD) published with an established programme operator. An ESPR delegated act will, when it covers the product category, set the PEF data to be carried by the Digital Product Passport, independently of the Type I or Type III publication route.

These three steps converge with the general approach to ecodesign now structuring procurement of electronic equipment by public bodies, large groups and integrators.

Sources & references

  1. Regulation (EC) 66/2010 on the EU Ecolabel , EUR-Lex eur-lex.europa.eu/eli/reg/2010/66/oj
  2. Commission Decision (EU) 2020/1804 establishing EU Ecolabel criteria for electronic displays , EUR-Lex eur-lex.europa.eu/eli/dec/2020/1804/oj
  3. Commission Decision (EU) 2016/1371 establishing EU Ecolabel criteria for personal computers, notebooks and tablets , EUR-Lex eur-lex.europa.eu/eli/dec/2016/1371/oj
  4. Commission Recommendation (EU) 2021/2279 on the use of Environmental Footprint methods , EUR-Lex eur-lex.europa.eu/eli/reco/2021/2279/oj
  5. ISO 14040:2006, Environmental management, Life cycle assessment, Principles and framework , ISO www.iso.org/standard/37456.html
  6. ISO 14044:2006, Environmental management, Life cycle assessment, Requirements and guidelines (AMD 1:2017, AMD 2:2020) , ISO www.iso.org/standard/38498.html
  7. ISO 14025:2006, Environmental labels and declarations, Type III environmental declarations , ISO www.iso.org/standard/38131.html
  8. Proposal for a Directive on substantiation of explicit environmental claims (Green Claims Directive) , European Commission environment.ec.europa.eu/publications/proposal-directive-green-claims_en