From Policy to Practice: Challenges of Environmental Data Generation and Digital Product Passport Readiness for Circular Garments Under EU Circular Textile Regulations
Abstract
1. Introduction
- To analyse the current challenges faced by global garment manufacturers—particularly those based outside the EU—in complying with the EU’s emerging sustainability requirements for circular textile products, with a focus on the technical, organisational, and supply chain-related barriers to providing environmental performance data.
- To identify the key barriers and enabling conditions that support effective collaboration between garment manufacturers and their upstream supply chains in generating and managing product-level environmental impact data, specifically in the context of the DPP and its associated LCA-based information requirements.
2. Policy and Legal Context
3. Methods
3.1. Review of EU Policy and Regulation
3.2. Survey of Textile Companies
3.3. Case Study: LCA of Circular Garments
- Upcycled T-shirt: The T-shirt was produced using the UPMADE-certified upcycling method, employing 100% cotton fabric leftovers generated during garment production. No new fabric was manufactured for this product; instead, fabric waste was transformed into a fully functional new garment. This approach reduces the demand for virgin fibre and fabric production and diverts textile waste from disposal.
- Recycled jeans: The jeans were made from fabric developed specifically for this project, combining 50% recycled cotton produced with RECOVER technology and 50% TENCEL™ Lyocell fibres created using REFIBRA™ technology. This fibre mix integrates pre-consumer cotton waste with wood-pulp-based cellulosic fibres to create a high-quality circular fabric. The material is fully bio-based, biodegradable and compliant with the Recycled Claim Standard (RCS).
4. Results
4.1. Industry Perspectives on LCA and DPP Readiness
4.1.1. Level of Sustainability Management
4.1.2. Barriers to Life-Cycle-Based Environmental Impact Assessment
4.1.3. Knowledge and Readiness for DPP Requirements
4.1.4. Enablers for Effective DPP Adoption
- Accessible, user-friendly platforms with authentic and reliable data;
- Greater standardisation and clear implementation frameworks;
- Centralised data management systems;
- Technical and financial support for capacity building;
- Training across all supply chain tiers, particularly among lower-tier suppliers;
- Stronger alignment between brands, suppliers, and technology providers to ensure interoperability and cost-effective adoption.
4.2. Case Study Design and Results
- Scenario 1—Conventional T-shirt: 100% virgin cotton T-shirt produced using standard sourcing and manufacturing practices.
- Scenario 2—Upcycled T-shirt: T-shirt produced entirely from cotton fabric leftovers from conventional garment production.
5. Discussion
5.1. Knowledge and Capacity
- Limited internal expertise. Conducting LCAs requires specialised methodological and software expertise that manufacturers currently lack.
- Insufficient awareness of emerging DPP technical requirements. Although most respondents had heard of the DPP, their understanding of its methodological implications—particularly the possible need for PEF-aligned, product-level environmental data—was incomplete. The generally positive perception of the DPP may therefore reflect familiarity with the concept rather than readiness to meet its data and verification demands.
- Resource constraints. Although most of the surveyed manufacturers were large enterprises, many still reported limited resources for specialised technical staff, LCA software, and external expert support. Scaling LCA across large and diverse product portfolios, potentially covering thousands of stock-keeping units, represents a significant organisational and financial challenge. These constraints are likely to be even more pronounced among small and medium-sized manufacturers, which typically have more limited technical and financial capacity to meet the emerging DPP requirements.
- Lack of structured internal data systems. Many manufacturers do not yet have integrated digital systems capable of capturing production data at the level of granularity required for LCA. Data were frequently stored across multiple departments or formats, making extraction and verification a laborious process.
5.2. Data Availability
- Incomplete or inconsistent upstream data. Many manufacturers rely on suppliers who either lack the capacity or incentives to collect and publish detailed process-level data or LCA results. As illustrated by the case study, even suppliers of advanced recycled or circular materials may not yet provide comprehensive LCI datasets or LCA results. This limits the applicability of PEFCR-aligned methods.
- Variability across regions and production sites. Differences in technology, fuel mix, wastewater management, and chemical use mean that average or secondary datasets may not reflect actual impacts. However, primary data are often unavailable, creating uncertainty in assessments.
- Cultural and communication barriers. Language differences, varying documentation norms, and inconsistent environmental literacy across regions further complicate data collection. These barriers were especially pronounced among lower-tier suppliers, who play a critical role in fibre, yarn, or dyeing processes.
5.3. Methodological Challenges
- Complexity of the PEFCR methodology. While the PEFCR provides necessary harmonisation, it is technically demanding and requires detailed modelling expertise. Stakeholders involved in this study expressed concern that applying PEFCR across product portfolios would exceed their technical and financial capacity.
- Although PEFCR facilitates comparability, it may underestimate the environmental benefits of innovative practices such as upcycling and the use of waste materials.
- Challenges applying CFF. The CFF used in the PEFCR is intended to allocate impacts in circular systems (recycling, upcycling, reuse). However, it is complex to operationalise. Evidence from other product groups (such as batteries) also suggests that first attempts to use the CFF often face severe practical challenges [37].
- Need for pragmatic alternatives. The case study demonstrated that, where primary data remain incomplete, pragmatic approaches such as the cut-off approach for waste-derived materials can provide transparent and scientifically robust environmental assessments. Such approaches are already widely recognised within LCA practice and may represent practical transitional solutions while manufacturers progressively improve data quality and supply chain collaboration.
- In parallel, the Environmental Product Declaration (EPD) system is available for companies to measure the environmental performance of their products. For the apparel sector, this includes the EPD Product Category Rules for Apparel [38]. An EPD is a Type III environmental declaration in accordance with the ISO 14025 standard [39]. Similarly to PEF, an EPD provides third-party-verified information about a product or service throughout its life cycle in a standardised way. There are, however, significant methodological differences between EPD and PEF that can affect the results. For example, the EPD framework does not require the use of CFF, and it allows greater flexibility in using assumptions based on value-chain studies or statistical data at the downstream stage. This may further increase confusion among potential users of the results.
5.4. Result Reporting and Credibility
- Complexity of LCA results. Environmental impacts are multi-dimensional, and LCA outcomes can be difficult for non-expert stakeholders to interpret. In the absence of clear and harmonised methodological guidance and consistent DPP reporting formats, there is a risk of inconsistent interpretation and communication of environmental information.
- Restrictions on comparability under PEFCR. PEFCR allow comparisons only against an established benchmark representing an average EU market product. While this framework enhances methodological consistency, it can mask differences related to geography, technological efficiency, or circular innovations (e.g., industrial-scale upcycling). Although the rationale for using a standardised benchmark is understandable, this restriction on comparability may also have unintended consequences by limiting meaningful comparisons with real market alternatives and potentially obscuring the environmental benefits of innovative circular products.
- Credibility and quality assurance of environmental information. Reliable environmental information will be essential for ensuring confidence in DPPs. Although the specific requirements for quality assurance and verification of environmental information under future DPP systems have yet to be fully defined, manufacturers are likely to face additional efforts related to documenting data sources, ensuring methodological consistency, and demonstrating the robustness of environmental information provided.
- Integration with digital reporting systems. DPPs are expected to integrate environmental information into digital formats that are interoperable across platforms and supply chain actors. Translating LCA results into structured, machine-readable information therefore creates an additional layer of complexity that many manufacturers are not yet prepared to address.
6. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
Abbreviations
| CFF | Circular Footprint Formula |
| EPD | Environmental Product Declaration |
| EU | European Union |
| ESPR | Ecodesign for Sustainable Products Regulation |
| DPP | Digital Product Passport |
| LCA | Life Cycle Assessment |
| LCI | Life Cycle Inventory |
| PEF | Product Environmental Footprint |
| PEFCR | Product Environmental Footprint Category Rules |
| RCS | Recycled Claim Standard |
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| Conventional T-Shirt | ||||
| Type | Activity | Amount | Unit | Ecoinvent Dataset Used |
| Upstream, input | Yarn, produced in India | 0.205 | kg | yarn production, cotton, ring spinning | yarn, cotton | Cutoff, U—IN |
| Upstream, input | Transport packaging material (polyethylene) | 0.002 | kg | market for packaging film, low density polyethylene | Cutoff, U—GLO |
| Upstream, input | Transport to the factory, packed yarn (530 km by road) | 0.11 | t·km | market for transport, freight, lorry, unspecified | Cutoff, U–RoW |
| Upstream, input | Transport to the factory, packed yarn (7344 km by sea) | 1.52 | t·km | market for transport, freight, sea, container ship | Cutoff, U—GLO |
| Manufacturing, input | Acetic acid | 0.001 | kg | market for acetic acid, without water, in 98% solution state | Cutoff, U—GLO |
| Manufacturing, input | Sulfuric acid (for wastewater treatment) | 0.005 | kg | market for sulfuric acid | Cutoff, U—RoW |
| Manufacturing, input | Chemical, inorganic | 0.003 | kg | market for chemical, inorganic | Cutoff, U—GLO |
| Manufacturing, input | Soda ash | 0.003 | kg | market for soda ash, light | Cutoff, U—GLO |
| Manufacturing, input | Sodium sulphate | 0.041 | kg | market for sodium sulphate, anhydrite | Cutoff, U—RoW |
| Manufacturing, input | Lubricating oil | 0.002 | kg | market for lubricating oil | Cutoff, U—RoW |
| Manufacturing, input | Electricity | 5.080 | kWh | market for electricity, medium voltage | Cutoff, U—BD |
| Manufacturing, output | Waste mineral oil | 0.002 | kg | market for waste mineral oil | Cutoff, U—RoW |
| Manufacturing, output | Textile waste | 0.031 | kg | market for waste yarn and waste textile | Cutoff, U—GLO |
| Manufacturing, output | T-shirt (174 g) | 1 | pc | - |
| 2 Upcycled T-shirt | ||||
| Type | Activity | Amount | Unit | Ecoinvent Dataset Used |
| Manufacturing, input | Fabric (cotton) leftovers from the same factory | 0.191 | kg | - |
| Manufacturing, input | Lubricating oil | 0.003 | kg | market for lubricating oil | lubricating oil | Cutoff, U—RoW |
| Manufacturing, input | Electricity | 0.501 | kWh | market for electricity, medium voltage | electricity, medium voltage | Cutoff, U—BD |
| Manufacturing, output | Waste mineral oil | 0.003 | kg | market for waste mineral oil | waste mineral oil | Cutoff, U—RoW |
| Manufacturing, output | Textile waste | 0.017 | kg | market for waste yarn and waste textile | waste yarn and waste textile | Cutoff, U—GLO |
| Manufacturing, output | T-shirt (174 g) | 1 | pc | - |
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Moora, H.; Haljasorg, M.; Pehme, S.; Malik, H.W.; Aus, R. From Policy to Practice: Challenges of Environmental Data Generation and Digital Product Passport Readiness for Circular Garments Under EU Circular Textile Regulations. Sustainability 2026, 18, 7127. https://doi.org/10.3390/su18147127
Moora H, Haljasorg M, Pehme S, Malik HW, Aus R. From Policy to Practice: Challenges of Environmental Data Generation and Digital Product Passport Readiness for Circular Garments Under EU Circular Textile Regulations. Sustainability. 2026; 18(14):7127. https://doi.org/10.3390/su18147127
Chicago/Turabian StyleMoora, Harri, Mariliis Haljasorg, Sirli Pehme, Hira Wajahat Malik, and Reet Aus. 2026. "From Policy to Practice: Challenges of Environmental Data Generation and Digital Product Passport Readiness for Circular Garments Under EU Circular Textile Regulations" Sustainability 18, no. 14: 7127. https://doi.org/10.3390/su18147127
APA StyleMoora, H., Haljasorg, M., Pehme, S., Malik, H. W., & Aus, R. (2026). From Policy to Practice: Challenges of Environmental Data Generation and Digital Product Passport Readiness for Circular Garments Under EU Circular Textile Regulations. Sustainability, 18(14), 7127. https://doi.org/10.3390/su18147127

