EU wants data on textile waste, and we have the answer

Text by Tone Skårdal Tobiasson

The proposal for the Waste Framework Directive, which is currently being read and analyzed by a myriad of companies, NGOs, researchers, policy-makers and interested citizens throughout Europe, handles two major consumer ‘goods’: Textiles and food. We are mainly concerned with the former, however, we have found that food offers us two good guiding principles.

The first one is to eat up what is on your plate. The second is waste audits as a means to gain meaningful knowledge on what gets “eaten up” and what doesn’t. In three separate documents, we ask the EU to heed these two guiding principles and apply them to apparel and other textiles.

One of the documents is our feedback on the textile part of the Waste Framework Directive (read the document here), where the authors have concrete recommendations for ensuring that the policy measures in the WFD can actually contribute to the EU’s ambition of putting fast fashion out of fashion. Currently, the Duration of Service is what is lacking in the available data (how long apparel has been in use and to what level the apparel and textile waste is ‘used up’ ), but even if the background document (#4) states “There is currently no sound method of estimating textile waste (collected and discarded in mixed municipal waste)”, this is just not true. And the two other papers elaborate on exactly this point. Waste audits/waste composition studies – which are very much used when gaining data on food waste – and wardrobe studies – are well-developed methods.

The document Status for developing methods for using waste as a resource for knowledge about the use phase of clothing (read the document here), offers an overview of exactly the current status for these methods, while the document USED, BUT NOT USED UP: Using textile waste to inform textile rating schemes (read the document here) explores how the data-collection methodology using waste audits can underpin several policy measures, such as the Product Environmental Footprint Category Rules, Ecodesign for Sustainable Products Regulation (ESPR), Labelling and Digital Product Passport (DPP), the Green claims directive, as well as EPR and the WFD. We have called the ongoing waste audit method for Targeted Producer Responsibility (TPR), as we originally saw it as a more effective means for levelling a EPR fee, using the Duration of Service as the measuring stick. However, we also now have realized that taking the waste as the point of departure, has many other ramifications that can be leveraged.

The cut-off point for feedback to the WFD keeps being postponed, but we encourage everyone to respond, as a functioning EPR scheme which actually takes the waste hierarchy seriously, can be reality, if we use waste audits as the basis for eco-modulating the fee. What we urgently need is for companies to add the date of production or when the product goes to market to the brand label. Then we can look both upstream, and downstream, from the time apparel and other textiles enter the different waste streams.

Regulating Fast Fashion out of Fashion

Authors: Ingun Grimstad Klepp and Kerli Kant Hvass

Abstract

Among sustainable fashion and textile themes, product durability has recently come into focus within EU policy making. The dominant understanding is that increased textile lifespan will reduce environmental impacts, but this intrinsic link is not supported by research. The volume of clothing produced poses the greatest environmental burdens. Increased clothes availability leads to longer lifespan due to reduced utilization. To reduce the environmental impact of increased textile volumes measures should be expanded to encompass not only product design, life-prolonging, and end-of-life strategies, but also the volume of products to market. This concept paper contributes to the debate on how to address the growing amount of textile waste by applying the knowledge gained from consumer research regarding clothing use and proposing a regulatory measure called Targeted Producer Responsibility (TPR). The central method of TPR is waste analyses which relies on actual use – or non-use – of products as the starting point for eco-modulated fees. TPR reverses EPR and uses waste for overproduction knowledge, thus proposing a tool that can potentially reduce the total environmental impact of textiles.

Click here to download and read the full article.

Click here to download and read the full conference proceedings (aalto.fi)

The plastic elephant in the room: Who dares to talk about it?

In the Consumption Research Norway SIFO report The plastic elephant: Overproduction and synthetic fibers in sustainable textile strategies we examine national, international and corporate strategies for sustainable textiles to understand whether, and if so, how they include the problem of increased production volumes based on synthetic materials that can be referred to as the ‘plastic elephant in the room’.

”It’s time to talk about the elephant in the room.” This is a quote from the 2014 GFA Fashion Summit in Copenhagen, when Livia Firth, founder of the consultancy EcoAge and the Green Carpet Challenge, was on a panel with H&M. She challenged the growth issue where “fast fashion brands justify growth by saying that it is the consumers who demand the wide selection and diversity of fashion styles today”. Firth responded to this claim made by H&M’s Helena Helmersson by saying that her children want candy all the time but that does not mean they should have it, and that as a parent she has “a responsibility in addressing this want”.

In order to find out whether different strategies take seriously the connection between overproduction and the enormous growth in the consumption of clothing and textiles, and the increase in the use of synthetic materials, we asked four questions to the strategies. First, we looked at whether the strategies discuss growth in production volumes and possible measures to stop this growth. Second, we examined whether they address the plastification of textiles. By plastification, we mean the increasing share of plastic fibres used for textile production. Third, we exmined whether they discuss the raw material for plastics, and fourth, plastic waste. The results show that none of these questions that can reduce the environmental impacts of clothing production are given a central role in the strategies. There were three types of strategies that were examined: policy, industry and NGOs’ sustainability strategies.

Important findings

The most interesting findings are related to the reduction of the use of synthetic fibres – the plastification. This is the question that receives the overall lowest scores: none of the strategies present clear, direct measures to halt plastification, though some of the public policymakers indirectly include such a goal, through goals of substituting fossil raw materials in the production with other materials, including bioplastics. Without stating how this tendency is to be reversed, the strategies raise concerns over the increasing volumes of fossil raw materials used in textile production. It is also suggested that synthetic fibres have important qualities that are needed and the strategy of substituting virgin plastics with recycled plastics is particularly present in the strategies of the industry stakeholders.

The Plastic Elephant is a part of the project Wasted Textiles, the goal of which is precisely to reduce the use of synthetic textiles and the amount that goes to waste. It is situated right at the core of the project’s goal and of course, the project is also the reason why our elephant is synthetic textiles (i.e., plastic). At the same time, we are building on work from three other ongoing projects at Consumption Research Norway (SIFO): CHANGE – about quantity, LASTING – about lifetime and REDUCE – about plastics in everyday life; and we thank our good colleagues from all the three projects for fruitful conversations as well as heated debates. We thank in particular Kirsi Laitala, Marie Hebrok, Harald Throne-Holst, Irene Maldini, Kate Fletcher and Kerli Kant Hvass for their thorough reading of the report and constructive comments.

The full report can be downloaded here.

Garbage talk: Easily outdated, but difficult to date

Text by Tone Skårdal Tobiasson

The results from the Wasted Textiles pilot study, executed by four Master-students Camilla Sunde (UiO), Eva Hovda (NTNU), Siri Vestengen (NTNU) and Saeid Sheikhi (Høyskolen Kristiania) has now been published. Avfall Norge and their summer program REdu, were able to get the pilot financed by The Norwegian Retail Environmental Fund, and the results from the pilot where the four students tested out a system for picking analysis that captures vital information on the textiles that mainly had status as garbage is presented in the report.

The analysis conducted in Slemmestad Mepex-center offers valuable insights into the current status of discarded textiles in Norway. The “TPR” (named for the Targeted Producer Responsibility idea) picking analysis results provide us with information regarding the composition of fibres, garment age, country of production, and brand details of the discarded textiles. This data was taken from the care labels on the products. Over a period of 13 days, the team successfully managed to analyze a total of 3024 items using the TPR picking analysis method that they fine-tuned based on a combination of wardrobe studies and classic waste picking analysis.

Picking analyzes are used for other product groups to say something about use. In food, this form of analysis is used to monitor how much edible food is thrown away from private households (see e.g., this study (miljodirektoratet.no)) and to monitor and reduce food waste from institutions. The textiles analysed in the report originated from various waste streams: Mepex’s “Klesbyttedag” (clothing swap day), TRV (Trondheim city pilot project on collecting textiles) and residual waste. Residual waste is the hardest to work with because of smell and humidity making it difficult to weigh the items. In the report, the TRV waste is the largest and most important, representing 91.4 % of the material. Textiles from TRV-pilot are supposed to be damaged textiles. Residents of the pilot area in Trondheim were given instructions and special bags for damaged textiles, clothing and shoes. Residents are encouraged to deliver usable textiles to collection boxes already located in the area and to put the bag with destroyed textiles outside for collection on a fixed day, every four weeks. The interns photographed all the items, gave each textile item a number, and registered information on if the brand could be identified if the care label was intact if there was a year of production or when the product entered the market anywhere on the textile, country of origin, fibre-composition, what state of ‘used up-ness’ the items were in, the weight, etc.

The findings in the REdu project, are based on a small sample, 3024 items all in all. 2564 of 3024 items (the total registered) had the brand present either on the label or a logo visible. 708 distinct brands were identified, but a few dominated, H&M being in the lead, followed by Cubus, Lindex and KappAhl. Out of the 3025 analysed textiles only 95 items had the year of production on their care labels, 2905 did not include this information. Of these clothing pieces 14 of them were from NameIt (a Danish children’s brand), 7 from Vero Moda, 7 from Selected – all three Bestseller brands, and 6 of them were from Bik Bok. For the remaining individual brands, 61 items were with a production year. Some brands have labels with codes that may or may not contain this information, that they would need to explain. Some brands said they are willing to help with this information.

The progress in the TPR picking analysis time efficiency showcases the potential for applying picking analysis and the time it might require. In the TPR approach, they utilised several input parameters and managed to analyse an average of 234 items per day, equivalent to around 79 kg. On the other hand, the “fast TPR method” employed fewer input parameters while still capturing details for each item. With this approach, the average number of items examined within a 30-minute span is 29, equal to 7.6 kg per person. The time used to analyze was affected by the different textiles analysed, whereas multilayer and complicated multi-fibre items were more time-consuming.

In assessing the potential of machine learning in textile waste management, the results are promising, but not without challenges. The initial model focusing on textile type classification achieved significant accuracy, with an accuracy of 82.25 %, emphasizing the practicality of using automation for sorting textiles. However, the usability classification model highlighted the need for comprehensive and quality data inputs to predict an item’s reuse potential. While machine learning presents great promise in enhancing sorting efficiency, determining reusability, and promoting fibre-to-fibre recycling, its successful deployment hinges on several factors. These include the expansion and quality improvement of datasets, the integration of advanced sensing technologies, and a broader assessment of environmental, economic, and social impacts.  Ethical considerations are paramount, especially in ensuring that machine learning models operate effectively and ethically. By partnering with Extended Producer Responsibility (EPR) schemes, feedback loops between producers and waste management can be optimized.

The data gathered from the examined items highlights the possibility of reusing materials in the textile sector that the consumers themselves deem as garbage.  Assessing the level of wear and tear in clothing was relatively easy, factors like pilling, stains, discolouration, damaged zippers, missing buttons, holes, and general signs of use are easy to spot and register. A majority of the items were in a good usability state, where 42% of the textiles scored a condition of 4 (5 being the highest score indicating mint condition, while 1 is not at all reusable), suggesting that the discarded textiles were not “used up”. Also, 21 items were found with their price tags still attached. While some items displayed minor damages, many of these can be fixed effortlessly at home, pointing towards the value of imparting basic repair skills to consumers.  Notably, 17.66% of items had a maximum usability score of 5, indicating a considerable number of nearly new items being discarded. We will remind the reader there that these were supposed to be worn out or «broken» items, as fully usable textiles were supposed to be donated in the donation boxes.  

The data obtained from this analysis holds significant importance in comprehending the possibilities of automated sorting, material reuse, and recycling. It provides a foundation for introducing strategic methods like extended producer responsibility (EPR) and policies focused on waste prevention. Hopefully, the TPR picking analysis can be used to assess eco-modulated environmental fees in an EPR scheme, aiming to ultimately decrease excessive textile production in the fast fashion sector. In 2022, 105 913 tonnes of new textiles which are equivalent to 19.3 kg per capita, were put on the Norwegian market, so future data collection is not in danger of not having materials to study, once textile waste will be collected separately from 2025.

Click here to read the full report (avfallnorge.no).

REdu result seminar

Webinar, Friday 11th of August 2023, 09:00-10:00, Oslo/Zoom.

Four intern students in the Avfall Norge REdu project have worked on the SIFO proposal for TPR (read more about this here), and will present the results from this work at 9 am CET on the 11th August via Zoom. We are eagerly awaiting these results, as this is the first time we will get answers to whether the textiles that end up in various waste streams can be identified by brand, if we can estimate how long their duration of service has been and in what state they are for reuse or recycling.

The seminar is free and open to all and can be accessed via this zoom-link. The meeting ID is 828 0060 9300.

Welcome!

Both Wasted Textiles and the REdu picking analysis project are financed by the Norwegian Retail Environmental Fund.

THE PLASTIC ELEPHANT: Overproduction and synthetic fibres in sustainable textile strategies

Authors: Ingun Grimstad Klepp, Lisbeth Løvbak Berg, Anna Schytte Sigaard, Tone Skårdal Tobiasson and
Lea Gleisberg

Summary

In this report, we examine national, international and corporate strategies for sustainable textiles to understand if and how they embrace the increased production volumes based on synthetic materials, which can be referred to as the ‘plastic elephant in the room’. This is done through a lens of four questions. First, we look at whether the strategies discuss growth in production volumes and possible measures to stop this growth. Second, we examine whether they address the plastification of textiles. By plastification, we mean the increasing share of plastic fibres used for textile production. Third, whether they discuss the raw material for plastics, and fourth, plastic waste. The results show that none of these questions that can reduce the environmental impacts of clothing production are given a central role in the strategies.

Click here to read the full report.

Ecodesign position paper: Textiles and footwear

In a position paper from the Change and Wasted Textile projects, authors Kate Fletcher, Irene Maldini, Ingun Grimstad Klepp, Kirsi Laitala, Jens Måge and Tone Skårdal Tobiasson have addressed the background document from EU’s Joint Research Centre on Ecodesign for Sustainable Products Regulation (ESPR).

The main theme in the position paper, is that the JRC document Preliminary study on new product priorities lays the basis to increase environmental burdens rather than reduce these. Therefore, in the paper, the authors ask that the work with the ESPR incorporates more empirical understanding about ecodesign, clothing consumption, and textile and fashion design. This in order that the directive will have the effect of reduced environmental burdens (including on climate) and will minimize inappropriate or unintended side effects.

The aim in writing the paper is to support the ESPR process for textiles and footwear in fostering deep and lasting environmental change.

The authors applaud the efforts of the EU in regulating the textile and footwear sector and agree in the priority that has been assigned to clothing and footwear on the bases of high consumption volumes in the EU, potential environmental improvements, and lack of previous regulation. However, it is the view of the authors that the current work with the Ecodesign Directive is based on some assumptions that are not in line with the knowledge that is there, nor is it targeted towards the main and interconnected challenges in clothing and textiles: overproduction and the increasing plasticization of the material content of products.

These two factors are interconnected due to the fact that an increase in production is not possible without the cheap, easily available fossil fuel-based raw material for fibres, materials, dyes and other processing chemicals.

It is therefore questionable whether textiles and footwear should actually be the initial priority for ESPR. Perhaps starting with cement would be better.

Microplastics or microfibers: Does anyone really get what this is about?

OPINION: What we do know, is that all synthetic clothing and materials, sooner or later, will become microplastics, a «time-delayed» pollution bomb. And thus, they will ultimately become a problem for seabirds, and us.

A new report on microfibers in waterways is gaining attention, as it claims the results show more natural fibers than synthetic ones, and therefore demonizing microplastics is wrong. However, a very recent study on the intestines of seabirds gives a different conclusion: Fossil-based particles do cause harm.

The recent report from The Microfibre Consortium (TMC), together with the Norwegian Research Center/NORCE has analyzed samples taken along the coast of Kenya and Tanzania, and found that of 2403 textile fibers in the water, 55 per cent were of natural origin, 37 per cent were synthetic and 8 per cent viscose/rayon-based.

To read this op ed, written by Professor Ingun Grimstad Klepp, Founder of Fibershed, Rebecca Burgess and journalist and writer Tone Skårdal Tobiasson, follow this link.

Want Not, Waste Not: Preliminary findings

Author: Anna Schytte Sigaard

Summary

This project note presents preliminary findings from a PhD project looking into textile waste from Norwegian households. 28 households collected textiles that they would have otherwise discarded for a period of six months. The textiles were collected by the PhD candidate during visits to the households where qualitative interviews were carried out. Then, all textiles were registered along with information from the interviews. The findings indicate that most of the discarded textiles are clothes and shoes. However, when broken down into textile categories, household textiles represent the largest group of discarded textiles. In addition, findings show that about one third of the collected textiles were in a very good condition, either like new or with only minor changes. The fiber content of the textiles corresponded with the preliminary findings from work package 2 in Wasted Textiles, as there was an equal distribution between 100% synthetic textiles, 100% non-synthetic textiles and textiles containing a mix of these. It was also found that the largest group of users were adult women, especially when looking at number of textiles discarded. If weight was applied instead, the difference between the genders evened out more. As these findings are preliminary, it is too early to provide any hard conclusions. Instead, the project note is meant to grant insights into the kind of data that will eventually be available and shared with the project group.

Click here to read the full project note.

Questions related to the TPR proposal

The Wasted Textiles team have had many meetings with policy-makers, politicians, NGOs, textile industry representatives and other interested parties regarding our Targeted Producer Responsibility proposal. We have collected questions we have been asked and here you will find the answers to these questions. If you have other questions, feel free to send them to us, and we will answer them as best we can, and make them publicly available.  

Q: How to obtain knowledge about the lifespan of textiles?

A:   Lifetime can be measured in number of years, or the number of times something is used. The proposal is to use the length of the use phase as the most important criterion. We propose that the brand and date of production/import will be made mandatory in the future legislation. In the long term, it will then be possible to measure how long the usage phase is on average per brand. We will also be able to say something about the number of uses. The clothes that have not been used will usually be recognizable, and likewise, clothes that have been used until they are worn out. The main method of TPR will be waste analyses and it is possible to do the analyses of the life span in different ways, also related to the type of textile.

Q: Is it only the quantity and age of the textiles in the waste stream that determine the size of the fee?

A: Our proposal is that the quantity and age of discarded textiles shall determine the fee together with the cost of capturing the End of Life (EoL) value for the products. This means that textiles with a high price on the second-hand market, or based on their material composition are a resource for recycling, will have a lower price or even not generate a fee at all, in accordance with the “polluter pays” principle.

Q: How to guarantee that the product carries information about the garment and the brand?

A: The rules today safeguard this to a certain extent, as the labels or the printed information need to withstand a certain number of laundry cycles. It is often also possible to determine the brand by visible logos or because the clothes are recognizable for other reasons. In practice, some will be unidentifiable, but as the sample pick analysis will give representative numbers, this is not the biggest hurdle. There will be enough waste to make statistical and significant compilations.

Q: With the Digital Product Passport (DPP) work underway to update the rules on what information is mandatory on textiles, is it premature to require that the date of manufacture (or date of placing on the market) must already appear on the label?

A: No. There can be interim solutions on the way to a product passport, and as picking analysis is a known method to gather data from waste streams, this is vital in order to quickly assess how long products have been in use before they are discarded. It is possible to analyse the age of clothes in the waste streams without dating the clothes, but dating will give better accuracy and make the analyses easier. In addition, the dating of clothes will have a number of positive effects for consumers, such as giving consumers a greater opportunity to compare the technical quality of the clothes and determine how long they have been in use. This will strengthen the right to complain which is linked directly to the number of years, thus empowering EU citizens.  It will also be an important link to transparency about production conditions. We, therefore, suggest that product date labelling should be included in the coming revision of the EU Textile Labelling Regulation, independently of EPR/TPR.

Q: Who will do the waste picking analysis?

A: We envision the work being carried out by third-party analysis agencies/research institutions with expertise in picking analyses and apparel, overseen by a public authority to oversee the implementation and ensure transparency.

In the Wasted Textiles project, the analyses are based on a collaboration between an analysis agency, MEPEX, with experience from sorting agents for other waste streams, researchers with experience with textiles, and the largest charity in Norway, along with Consumption Research Norway (SIFO)’s experience with different versions of wardrobe methods. Collectively, a method has been developed to look at the composition of the textile waste. Based on this work, it will be possible to further develop a method that meets the specific requirements of an EPR/TPR system.

Q: How to estimate how old a garment is by looking at waste streams or reuse collection streams?

A: Unused clothes are generally recognized by the fact that they have price tags on them, or that they are found in large quantities of similar clothes (unsold). Age can otherwise be assessed based on style, technical details and wear-and-tear. We are not talking about detailed information, but about broad assessments. Textile waste today consists of textiles produced over many decades and there have been technological and aesthetic changes in apparel over the past 50 years, although apparel has not changed as quickly as e.g., electronics. Accuracy will of course be easier when the date becomes a mandatory part of labelling textiles. Accuracy will also be better if the staff who carry out the analysis have the appropriate textile expertise.

Q: What are the criteria for a TPR fee?      

A: TPR can be used and combined with different varieties of EPR and other political instruments. If it is to have the effect of reducing overproduction and making fast fashion out of fashion, then it depends on the fee being high enough to affect the producers, their business models and downstream decisions. However, it is not the size of the fee that distinguishes TPR from other EPR systems, but the way it is calculated.

Producers would pay different levels of EPR fees depending on:

  • How old the clothing is when going out of use (very old clothing generates no fee, while very new would generate a high fee)
  • How reusable/recyclable the clothing is (clothing types with profitable pathways have a low fee)

TPR will ensure a level playing field for a European-based textile industry, global brands and online producers, so-called ultra-fast-fashion brands.  TPR will catch all textile waste, regardless of where the garment was made or imported from, thus addressing the challenge of online trade/e-commerce and “free-riders”. Further work is needed on the details of how the fees are calculated for each individual producer, for specific product groups or for the industry as a whole.   

Q: Can picking analysis actually underpin the legal validity of fees?

A: The legal foundation, implications and further development of TPR are in the current EU Waste Framework Directive, and in the coming revisions. The current WFD (article 8a) defines minimum requirements for member states and their EPR-systems, f. ex. stating that eco-modulation shall be used when it is possible. But until now we have not seen eco-modulation being used in accordance with the waste hierarchy, nor the polluter pays-principle, when it comes to irresponsible production and consumption, and its waste export, and there are limitations in the current directive when it comes to setting fees that go beyond the waste phase. The EU textile strategy from March 2022 announced that there will be a harmonised producer responsibility in the EU set forth in the coming revisions.

We will rely on legal experts and funding for further work with the legal aspects of TPR. It is likely that the retroactive aspect will be contended. If producers are held responsible for the waste they have produced long before the scheme comes into effect, they will balk. It will, however, only be a temporary problem. It is also possible to use TPR combined with sales/import statistics, so that TPR is used to modulate the fee, but that it is based on the imports/production taking place at the same time. We consider it unlikely that the analysis of the waste itself would not be reliable enough. Picking analyses are used on other waste streams and is a recognized method.

Q: Will TPR be costly to operate?

A: The costs of operating the scheme will be covered by the fee, as is normal for other control schemes for industries. TPR is based on national samples taken annually or every two years, and is assumed to be administered at low cost.

For TPR to work (reduce quantities and thus environmental burdens) it is important that the fees are high enough. This will provide money that can be used for, among other things, the operation of the system. In existing EPR-schemes the fees are often set very low so that there is little room for covering other than minimum administrative costs.

In general, there is too little waste regulation supervision and with many new EU regulations to be followed up, it is necessary to strengthen supervision on national and municipal levels. The knowledge that the picking analysis will provide is important data for monitoring the effect of the EU’s textile strategy and for making the best possible use of textile waste. It is difficult to imagine effective policy and product development without knowledge of the waste.

Q: How can we trust those who will be doing the picking analysis, that the data they collect is good enough to eco-modulate fees based on the findings?

A: In contrast to much environmental work, TPR is not based on information provided by the actors themselves, but by an independent third party with no financial interests in the matter. Why should a research or analysis agency not be trusted? It is, after all, common to use a third party to obtain information precisely to ensure independence. A major problem in the textile industry is that concepts, perspectives and what is perceived as knowledge are often produced by the industry itself and its organisations. Selective analyses, on the other hand, can be carried out by independent analysis agencies/researchers.

Q: Will TPR affect companies that want to invest in circular business models and charities that are dependent on revenues from second-hand trade?

A: Circular BMs, such as repair, rental, etc. are struggling financially today due to the competition with cheap new clothes. By making it more expensive to sell what hardly gets used, the over-production will be impacted and eventually reduced (provided the fee is high enough). This will strengthen the possibility for such BMs. The companies that work with further processing of textile waste (repair, redesign, recycling and all intermediate forms) will be able to receive financial help for product development and support from the EPR system and this subsidy will improve their financial sustainability.

Q: In the EU, 99,9% of the actors in the textile sector are SMEs. How will TPR capture meaningful data about them, and ensure that they are not treated unfairly?

A: For once, we are lucky that the fashion and sports apparel sector are dominated by big, global companies with large volumes. This means that they will dominate in the picking analysis.

Q: How will the collected fees be allocated and used?

A: The allocation of the fee has not been elaborated in the proposal for a TPR system. However, we believe that it is important that the TPR funds will be allocated to support as a minimum (non-exhaustive list):

  • operation of the system (incl. picking analysis and calculations, the logistics)
  • support proper use of collected textiles according to the waste hierarchy, incl. charities, markets for reuse and repair
  • support the work with reducing synthetic textiles, preventing the spread of microplastics and cleaning up the textile waste in developing countries
  • support municipalities that need to build up collection, sorting and treatment facilities
  • support countries, regions, businesses and NGOs in the global south in cleaning clean up landfills and rivers and establish functioning waste management systems
  • stimulate technology innovation, research, development and investments

Q: Can TPR be useful for other policy measures than EPR? 

A: TPR is a way of “capturing” the use phase, which otherwise remains a “black hole” in LCAs. In other words, a very important factor for calculating environmental impact in the whole lifecycle of a product, is not taken into account. TPR will make a valuable contribution to gathering meaningful data – and thus can have an impact on many policy measures, especially the ones based on LCA data.

Q: The EU Textile strategy aims for durable, repairable, recyclable apparel and footwear, that also contains recycled content – does TPR contribute to this, or is it counter to these aims?

A: TPR will contribute by bringing forward knowledge and data on how effective these aims are in delivering on the issues around durability. Through the picking analysis it is possible to collect various information on discarded or donated products, i.e., if the discarded or donated items have been repaired, or other relevant information related to the Textile Strategy aims.

Q: Does the TPR have the potential to address just transition, more local value-chains, eco-design and other issues that the EU are addressing through other strategies and programs?

A: The results from the picking analysis will feed into eco-modulation, and be the opposite of traditional eco-design, which only projects assumptions on lifespan. The data collected will be ‘proof of the pudding’ on what actually has a long lifespan, and cancel part of the eco-design directive, through providing actual data and incentives for making lasting products. TPR will use the market forces, and let the companies themselves decide how they tackle this, but make it costly to make products nobody wants.  This will be valuable for the New European Bauhaus. We also see synergies for Farm to Fork, the EU’s new Soil Mission, and other programs and strategies, for example, the Plastic strategy. We know the EU aims for a more holistic, non-siloed way forward, and TPR offers an opportunity for this, based on how to award apparel that stays in use for a long time (indigenous, traditional, local, etc.) up against low-quality products that have a very short lifespan.

Q: How will TPR help to phase out fast fashion?

A: If the fees are high enough to deter the increased plastification of our wardrobes and for clothing that we keep, use and love for a long time, to be awarded amnesty, then TPR will help phase out fast fashion.

Q: How will this affect the developing countries, who rely on second-hand clothes from the EU and the trade of these clothes?

A: TPR has the potential to affect developing countries in two ways. Firstly, the TPR fee should address the issue of waste colonialism, i.e., quantities of textile waste exported (as mentioned earlier in the paper but needs further study for concrete proposals).

Secondly, in line with the EU’s strategic goal to handle its own textile waste rather than exporting it to the Global South, TRP will indirectly affect this export in the long run, through the expected reduction of fast fashion and the volumes being exported.

TPR is also an opportunity for EPR to reduce quantities imported into the EU and thus if the fee is set high enough, it will affect the quantities that go out of use and thus what is exported to developing countries. This is very important, as it is the Global North that creates the major waste problems, which has been recently documented by EEA, Changing Markets Foundation and The OR Foundation. TPR’s goal is to affect the quantities being produced (fast fashion) and exported as waste and thus reduce negative environmental impacts and the related problems in production, use and disposal. These are environmental problems that particularly affect developing countries in that both the production takes place there and that the waste ends up there.

Q: Can TPR be used in other product areas?

A: Yes. That is a good idea to explore. As far as we know, there are no similar systems for other product groups; however, many products are sold with dates and also information on expected lifespan, which is a good basis for developing a TPR system. It would be possible to install a counter in f. ex. a laundry machine or coffee maker, so that the fee is not only based on years of use, but also laundry cycles or coffee-pots made. Using both years of service life and other available information in the modulation of the fee will contribute to more durable products for many product categories.

See the full briefing paper that was sent to the EU representatives below.