The inside of a slate-grey rain jacket, opened flat. A long cream care label is sewn into an inside seam and hangs straight down past the hem.

Chemicals in products · A rain jacket · October 2026

A jacket, two journeys

One jacket. Six handovers. Can reliable chemical information travel with it?

Illustrative pathway, not a traced shipment

Independent Foresight research, shared ahead of the first International Conference of the Global Framework on Chemicals, Geneva, 16 to 20 November 2026. Research snapshot 23 October 2026.

Generated photograph. Not a specific product.

The record that travels

Only the label is designed to make the whole journey.

A water-resistant jacket starts as a set of decisions about chemistry. A supplier formulates the finish that makes rain bead and roll off. A mill applies it to the fabric. A factory sews the jacket, a brand sells it in France, an owner wears it for years, and a sorter decides what happens to it next.

Each of them needs to know something different about that finish. Much of what they could learn may stay behind on paper: a safety data sheet at the mill, a test report on a buyer's desk, a declaration in a supplier portal.

One record is sewn into the jacket and goes wherever it goes. The law decides what it must say.

Required on the product

A batch number

Since December 2024, a consumer product must bear a type, batch or serial number. The law does not say whether on this label or a tag. Evidence: LAW-35

Required on the product

Who answers for it

The manufacturer’s name and address and, for an import, the importer’s. It is the jacket’s route back to the business that holds its records. Evidence: LAW-35

No line

The finish

Fibre composition is worked out without “impregnating products” and other processing products. No rule we found asks the label to name a water-repellent finish. In a survey of outdoor jackets on sale in 2015 and 2016, no care label did. Evidence: LAW-03TECH-28

What the label must carry

On the labelWhat the law asksEvidence
Fibres and percentages, for each main partRequired. In French for sale in France, and visible before purchase, online too.Evidence: LAW-01LAW-02LAW-04
A batch number, and who placed it on the marketRequired on the product. A type, batch or serial number, with the manufacturer’s and importer’s names and addresses. The law does not say whether on the label or a tag.Evidence: LAW-35
Care instructionsNot required by EU law. France is not among the member states reported to require them.Evidence: LAW-05LAW-06
Country of originNot required on the label. Larger producers give the countries of weaving, dyeing and making-up on an online product sheet instead.Evidence: LAW-05LAW-28
The membraneVoluntary. Some labels name it. In one survey, some gave a polytetrafluoroethylene (PTFE) membrane as a share of the composition.Evidence: TECH-28
The water-repellent finishNo line. Left out of the fibre composition by design. We found no rule that asks for it anywhere else on the label.Evidence: LAW-03TECH-28

The label says polyester. It is not asked to say what the polyester was finished with.

The finish

In this jacket, the PFAS question sits in the finish.

A rain jacket is built in layers. This one has a woven polyester face, a polyurethane membrane that keeps water out, and a knit lining bonded behind it. At the finishing mill, the face fabric is coated with a durable water-repellent (DWR) finish and cured in an oven at up to 180 °C. Evidence: TECH-03TECH-05

PFAS, per- and polyfluoroalkyl substances, are a group of fluorinated chemicals. Fluorine can reach a jacket in two ways: through a membrane of polytetrafluoroethylene (PTFE), a fluoropolymer, or through a finish made with side-chain fluorinated polymers. This jacket’s membrane is polyurethane, so the question is the finish. Fluorine-free finishes make water bead too, so the beads cannot say which kind it has. Evidence: TECH-04TECH-01TECH-09

The jacket's shell drawn as three separated sheets: dark grey face fabric with beads of water on it, a thin white membrane, and a grey knit lining.

The shell, layer by layer

  1. The finish. A durable water-repellent (DWR) finish, cured onto the fibres at the mill. It is too thin to see. The beads show that it works, not what it is made of. Evidence: TECH-05TECH-09

    On the labelNo lineEvidence: LAW-03

  2. Face fabric. Woven polyester, the outside of the jacket.

    On the labelShell 100 % polyesterEvidence: LAW-01

  3. Membrane. The waterproof layer, polyurethane in this jacket. Many jackets use PTFE instead, which is itself a PFAS. Evidence: TECH-03TECH-01

    On the labelNo lineEvidence: TECH-28

  4. Lining. A polyester knit, bonded behind the membrane.

    On the labelLining 100 % polyesterEvidence: LAW-01

Illustrative render, made for this investigation. Layers are not drawn to scale.

Limits in parts per billion. Disclosure from 0.1%.

Two kinds of rule now reach that finish. Restrictions cap what the jacket may contain. Since 1 January 2026, France has banned PFAS in clothing for consumers, above residual values as low as 25 parts per billion for any single PFAS. Since 10 October 2026, the EU has capped PFHxA, an acid that fluorinated finishes can contain or break down into, at the same level. Evidence: LAW-21LAW-22LAW-16TECH-06

Neither restriction asks anyone to tell the next business. France asks only for proof, given to the authorities on request, once total fluorine passes 50 mg per kg. The duties to tell the next business start at 0.1% by weight, which is 1,000,000 parts per billion. They cover only substances on the EU’s Candidate List of substances of very high concern, and PFHxA is not on it. Evidence: LAW-22LAW-12LAW-08LAW-11

What the jacket may contain, and when someone must say so

Concentrations by weight, in parts per billion (ppb). Each step on the tape is ten times the last. 1,000 ppb is one part per million (ppm).

Limits

  1. 25 ppb

    • France: any single PFAS Evidence: LAW-21LAW-22
    • EU: PFHxA and its salts Evidence: LAW-16
    • EU: long-chain acids, C9 to C14 Evidence: LAW-13
  2. 250 ppb

    • France: targeted PFAS added together Evidence: LAW-22
  3. 1,000 ppb

    • EU: substances related to PFHxA Evidence: LAW-16
  4. 50 ppm (50,000 ppb)

    • France: all PFAS, polymers included Evidence: LAW-22

40,000 times from the lowest limit, 25 ppb, to the first duty to tell the next business, 0.1% Evidence: LAW-12

Duties to pass information on

  1. 50 mg of fluorine per kg

    • France: prove to the authorities, if they ask, whether the fluorine is PFAS Evidence: LAW-22
  2. 0.1% (1,000,000 ppb)

    • Name the substance to business customers Evidence: LAW-08
    • Notify SCIP, the EU’s database of substances of concern in products, open to waste operators Evidence: LAW-14
    • France: state it on the product sheet Evidence: LAW-26

    Only for substances on the EU Candidate List. PFHxA is not on it. Evidence: LAW-11

A jacket can break the limit long before anyone has to say what is in it.

Two journeys

Six handovers, five things to know

Between the drum of finishing agent and the sorting line, the jacket changes hands six times. At each handover we followed five things to know about what it is made of, and asked whether each one reaches the next person and helps them decide what they have to decide.

We keep four kinds of evidence apart. What a law or programme requires to pass. Whether the recipient can get it. Whether it answers their question. And what this investigation can show for this case. An open seam means we found no route, not that none exists.

Illustrative pathway, not a traced shipment

How much to read

Handover 1 of 6Short route

Chemical supplier to finishing mill

A drum of water-repellent finishing agent

What is in this drum, and how should our workers handle it?

Asked by the finishing mill
A finishing mill's bench, seen from above: a square of slate ripstop fabric with beads of water on it, a small unlabelled plastic bottle, a glass dropper and a stapled safety data sheet.

On the finishing mill's bench

  1. Finishing agent. A sample from the drum. The drum's label must name the product and its composition, in Vietnamese. Evidence: VN-04

  2. Safety data sheet. Names hazardous ingredients above cut-offs. An unclassified polymer need not appear. Supplier information has described an ingredient only as “an unknown functionalized polymer”. Evidence: TECH-13TECH-16TECH-12

  3. Test swatch. Water beads on the finished fabric. Fluorine-free finishes repel water too, so the beads are not evidence of PFAS. Evidence: TECH-09

Illustrative photograph, generated for this investigation.

What the rules supply
Viet Nam's law asks the most at this handover. Every chemical must be classified and labelled in Vietnamese. A seller of a hazardous chemical must hand over a safety data sheet. Workers have a right to hazard information, and training every two years. Evidence: VN-01VN-02VN-04VN-08VN-09
What we could not establish
Whether the finish is fluorinated. A safety data sheet need name only hazardous ingredients above a threshold, and trade-secret rules take priority. Suppliers have described ingredients as “an unknown functionalized polymer”. A report from the industry programme Zero Discharge of Hazardous Chemicals (ZDHC) says the agent meets its voluntary PFAS limits, not what it contains. Evidence: VN-03TECH-12TECH-16VN-21
Still unresolved
Whether a finishing agent goes through Viet Nam's chemical import declaration, the one place a Vietnamese safety data sheet is expressly required. We read its tariff heading as outside it. Evidence: VN-05VN-06
  1. Component identityDrum label

    Recipient access
    Demonstrated
    Legal basis
    Applicable duty
    Decision usefulness
    Supports the named decision
    Case evidence
    Documented general practice

    The label must name the product and its composition, in Vietnamese. A ZDHC QR code, where printed, adds the product ID and status. Evidence: VN-01VN-04VN-22

  2. Chemical identity or groupSafety data sheet

    Recipient access
    Conditional or restricted
    Legal basis
    Applicability unresolved
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Documented general practice

    A safety data sheet must name hazardous ingredients above cut-offs. A polymer that is not classified need not appear, and confidentiality can withhold the rest, so the sheet may not show whether the finish is fluorinated. Evidence: VN-02VN-03TECH-13TECH-14TECH-16TECH-12

  3. Concentration or test resultZDHC ChemCheck report

    Recipient access
    Conditional or restricted
    Legal basis
    Voluntary provision
    Decision usefulness
    Supports the named decision
    Case evidence
    Documented general practice

    ZDHC certifiers test the formulation against PFAS limits in parts per billion. The mill receives a conformance level. It answers whether the agent meets the buyer's list, but it is not a measured value. Evidence: VN-19VN-20VN-21

  4. Hazard and handlingDrum label and safety data sheet

    Recipient access
    Demonstrated
    Legal basis
    Applicable duty
    Decision usefulness
    Supports the named decision
    Case evidence
    Illustrative assumption

    We assume the drum carries the hazard label the law requires. Training is required too, and warning signs for listed substances must be in the workers' language. Public evidence cannot show whether either happens at a given mill. Evidence: VN-04VN-08VN-09

  5. Evidence type and dateCertificate or QR code

    Recipient access
    Conditional or restricted
    Legal basis
    Voluntary provision
    Decision usefulness
    Supports the named decision
    Case evidence
    Documented general practice

    A ChemCheck report gives the certification body and certificate dates. Where the supplier uses OEKO-TEX's ECO PASSPORT, the agent is certified and the formulation stays confidential. Evidence: VN-21VN-22GFC-30

Next The mill cures the finish onto the fabric at up to 180 °C. From here on it travels as part of the fabric, not as a chemical.

Link to this handover

Handover 2 of 6

Finishing mill to garment factory

Rolls of finished, laminated fabric

What was this fabric finished with?

Asked by the garment factory
What the rules supply
No legal duty we found carries the finish with the fabric. Viet Nam's list of chemicals to disclose in products has ten entries, none a textile or a PFAS. Its textile regulation covers formaldehyde and azo dyes. Industry guidance asks the mill to say what type of treatment it used. Evidence: VN-15VN-17VN-24
What we could not establish
What the factory receives. The mill's monthly chemical report goes to brands on the ZDHC Gateway. The factory that sews the fabric is not a named recipient. A certificate says the fabric passed limits, without the values. Evidence: VN-26VN-31
Still unresolved
Whether Viet Nam's general duty to tell “users” about hazardous content in products reaches a mill selling treated fabric. We found no guidance that settles it. Evidence: VN-07
  1. Component identityFabric specification

    Recipient access
    Conditional or restricted
    Legal basis
    No duty identified
    Decision usefulness
    Supports the named decision
    Case evidence
    Illustrative assumption

    We assume the factory buys to a written specification naming the face fabric and the membrane. The finish goes on the face fabric whichever membrane is used. Evidence: TECH-03

  2. Chemical identity or groupTreatment notice

    Recipient access
    Conditional or restricted
    Legal basis
    Voluntary provision
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Documented general practice

    AFIRM, a group of apparel and footwear brands, asks mills to say whether a material is water-repellent and by what type of treatment. A treatment type is not a chemical identity, and “no PFAS-based finish” cannot rule out a PFAS membrane. Evidence: VN-24VN-32VN-15

  3. Concentration or test resultCertificate

    Recipient access
    Conditional or restricted
    Legal basis
    Voluntary provision
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Documented general practice

    Certified fabric has passed limits of 25 ppb for each PFAS and 50 mg of total fluorine per kg. The certificate states that it passed, not what was measured. Evidence: VN-30VN-28VN-31

  4. Hazard and handlingNone found

    Recipient access
    Not demonstrated
    Legal basis
    Applicability unresolved
    Decision usefulness
    Not assessed
    Case evidence
    Not established

    Viet Nam's general duty to inform “users” about hazardous content may reach treated fabric. We found no guidance either way. Evidence: VN-07

  5. Evidence type and dateZDHC InCheck, to the brand

    Recipient access
    Not demonstrated
    Legal basis
    Voluntary provision
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Documented general practice

    The mill's InCheck report covers its whole chemical inventory each month and goes to connected brands. The factory is not a recipient, and the report does not follow a roll. Evidence: VN-26

Next The factory cuts the fabric, sews and tapes the seams, and sews in the label the brand has specified.

Link to this handover

Handover 3 of 6Short route

Garment factory to brand

Finished jackets, shipped from Viet Nam to France

Can we sell this jacket in France?

Asked by the brand or importer
A brand's desk, seen from above: the folded rain jacket with its long care label lying flat, a clear polybag and a pencil on one side, and on the other a test report, a supplier declaration and a certificate.

On the brand's desk

  1. Sewn-in label. Fibre composition, by law. Ours also carries a batch number that leads back to the importer. Nothing about the finish. Evidence: LAW-01LAW-35

  2. Test report. Checks a list of targeted PFAS. In one study, 13 of 15 water- or grease-proofed textiles contained fluorine while every targeted PFAS was below 165 ppb. Evidence: TECH-25TECH-22

  3. Supplier declaration. Says what is absent. In the EU, the chemicals regulation REACH requires a listed substance to be named only above 0.1% by weight, 40,000 times the French limit. Evidence: LAW-08LAW-34

  4. Certificate. Shows which criteria applied, for one year. Anyone can check its number online. Evidence: VN-31

Illustrative photograph, generated for this investigation.

What the rules supply
The rules that decide the sale are limits, not information duties. France has banned PFAS in consumer clothing since January 2026, from 25 ppb for any one PFAS. The EU's PFHxA limit has applied since 10 October 2026. Once the jacket is in the EU, REACH asks suppliers to name a listed substance only above 0.1% by weight, 40,000 times higher. Evidence: LAW-21LAW-22LAW-16LAW-08LAW-12
What we could not establish
Whether the finish is fluorinated, from what reaches the brand. Brands rely on supplier declarations, contract terms and certificates that say what is absent. No single test shows compliance with every PFAS rule. Evidence: LAW-34VN-33VN-34
Still unresolved
How France will use its total fluorine trigger. Above 50 mg of fluorine per kg, the seller must be able to show the authorities, on request, whether it comes from PFAS. The EU-wide PFAS restriction is still a proposal. Evidence: LAW-22LAW-17
  1. Component identitySewn-in label

    Recipient access
    Demonstrated
    Legal basis
    Applicable duty
    Decision usefulness
    Supports the named decision
    Case evidence
    Illustrative assumption

    The fibres and percentages of each main part, worked out without the finish. The brand writes the label and the factory sews it in. Evidence: LAW-01LAW-02LAW-03

  2. Chemical identity or groupSupplier declaration

    Recipient access
    Conditional or restricted
    Legal basis
    No duty identified
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Documented general practice

    REACH binds suppliers in the EU, not the factory in Viet Nam. From the importer on, it requires the name of a listed substance above 0.1% by weight, far above a finish residue that breaks the French limit. Brands rely on declarations that a substance is absent. Evidence: LAW-08LAW-12LAW-34VN-34

  3. Concentration or test resultTest report or certificate

    Recipient access
    Conditional or restricted
    Legal basis
    Voluntary provision
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Documented general practice

    In one study, total fluorine was found in 87% of water-repellent textiles whose targeted PFAS were all below 165 ppb. A clean targeted test can sit beside a high total fluorine result. Evidence: TECH-25TECH-22VN-33LAW-34

  4. Hazard and handlingCare symbols

    Recipient access
    Demonstrated
    Legal basis
    No duty identified
    Decision usefulness
    Not assessed
    Case evidence
    Illustrative assumption

    Our label carries care symbols because brands put them there. EU law does not require them, and France is not among the states reported to. Evidence: LAW-05LAW-06

  5. Evidence type and dateCertificate

    Recipient access
    Conditional or restricted
    Legal basis
    Voluntary provision
    Decision usefulness
    Supports the named decision
    Case evidence
    Documented general practice

    A certificate number lets anyone check which criteria applied, and a certificate lasts a year. In France the date of manufacture now matters too: the sell-off for older stock ends on 31 December 2026. Evidence: VN-31LAW-24

Next The brand sells the jacket in France, with the label sewn in and a product sheet online.

Link to this handover

Handover 4 of 6

Brand to owner

One jacket, bought in France

What is this jacket made of, and how should I look after it?

Asked by the owner
What the rules supply
The label must give the fibres of each main part, in French, and a buyer must see them before paying, online too. The jacket must also bear a batch number and the importer's address, though the law does not say on which label or tag. Larger producers publish a product sheet online, with the countries where the jacket was woven, dyed and made up. Evidence: LAW-01LAW-02LAW-04LAW-35LAW-25LAW-28
What we could not establish
What the jacket was finished with. A product sheet names a hazardous substance only above 0.1%, and France's list adds no PFAS. A buyer can ask about substances of very high concern and wait up to 45 days. Evidence: LAW-26LAW-27LAW-09
Still unresolved
What a digital product passport will carry. The EU's ecodesign rules allow substance data on or through the product, but the textile act is not expected before 2027. Evidence: LAW-31LAW-32
  1. Component identitySewn-in label

    Recipient access
    Demonstrated
    Legal basis
    Applicable duty
    Decision usefulness
    Supports the named decision
    Case evidence
    Illustrative assumption

    Fibres and percentages for each main part, in French, visible before purchase. Evidence: LAW-01LAW-02LAW-04

  2. Chemical identity or groupOn request, or the product sheet

    Recipient access
    Conditional or restricted
    Legal basis
    Applicable duty
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Documented general practice

    A substance is named only above 0.1%, and France's list adds no PFAS. In a survey of outdoor jackets on sale in 2015 and 2016, no care label named the finish. Evidence: LAW-09LAW-26LAW-27TECH-28

  3. Concentration or test resultNone found

    Recipient access
    Not demonstrated
    Legal basis
    No duty identified
    Decision usefulness
    Not assessed
    Case evidence
    Not established

    No rule we found gives a buyer a test result. The French ban and the EU limit are enforced on the seller. Evidence: LAW-21LAW-16

  4. Hazard and handlingCare symbols and product sheet

    Recipient access
    Conditional or restricted
    Legal basis
    Applicable duty
    Decision usefulness
    Supports the named decision
    Case evidence
    Documented general practice

    Care symbols are voluntary in France. Larger producers' product sheets must say that a mostly synthetic garment releases microfibres when washed. Evidence: LAW-05LAW-29LAW-25

  5. Evidence type and dateBatch number and importer

    Recipient access
    Demonstrated
    Legal basis
    Applicable duty
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Illustrative assumption

    The batch number and importer's address lead back to the business that holds the records. On their own, they say nothing about the finish. Evidence: LAW-35

Next The owner wears the jacket for years and washes it. The label goes with it.

Link to this handover

Handover 5 of 6Short route

Owner to collector and sorter

A used jacket, in a collection bag

What is this jacket, and where should it go next?

Asked by the collector and sorter
A sorting table, seen from above: the worn jacket lies open on a heap of used clothes, its care label greyed and frayed. To one side are a label cut out of another garment and a pair of scissors.

At the sorting table

  1. The care label. The only product record shown to reach the sorter. Sorters use labels “when they are not removed or faded”. Evidence: LIFE-12

  2. A cut-out label. In a study of 10,901 used garments, 24% had no label, counting labels visibly cut out. Only 59% of readable labels matched the fibres found. Evidence: TECH-29TECH-30

  3. The finish. Nothing on the jacket says what its finish is. Testing a used textile for PFAS is “expensive and generally not feasible”. Evidence: LIFE-21

Illustrative photograph, generated for this investigation.

What the rules supply
Nothing has to travel with it. By 2028, EU law will require producer schemes to collect used textiles “regardless of … material composition”. France's scheme traces where sorted tonnage goes, not what a jacket contains. Evidence: LIFE-02LIFE-06LIFE-07
What we could not establish
Anything about the finish. The label is the only product record shown to reach the sorter. By this point, the European Environment Agency finds, PFAS information “has usually been lost”. Evidence: LIFE-12LIFE-21
Still unresolved
Whether France's PFAS ban reaches used clothing that is exported for re-use, especially once the sell-off for older stock ends on 31 December 2026. Evidence: LIFE-29
  1. Component identitySewn-in label, if it survives

    Recipient access
    Demonstrated
    Legal basis
    No duty identified
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Documented general practice

    Sorters use the label “when they are not removed or faded”. In a study of nearly 11,000 used garments, 24% had no label, and 59% of readable labels matched the fibres found. Evidence: LIFE-12TECH-29TECH-30LIFE-02

  2. Chemical identity or groupNone found

    Recipient access
    Not demonstrated
    Legal basis
    No duty identified
    Decision usefulness
    Not assessed
    Case evidence
    Documented general practice

    Collection rules name no substance information and leave tracking to future ecodesign acts. The re-use decision is made by eye. Evidence: LIFE-04LIFE-21LIFE-11

  3. Concentration or test resultNone found

    Recipient access
    Not demonstrated
    Legal basis
    No duty identified
    Decision usefulness
    Not assessed
    Case evidence
    Documented general practice

    Testing a used textile for PFAS is “expensive and generally not feasible”. Water repellency is visible, but it is not evidence of PFAS. Evidence: LIFE-21TECH-09

  4. Hazard and handlingNone found

    Recipient access
    Not demonstrated
    Legal basis
    Future duty
    Decision usefulness
    Not assessed
    Case evidence
    Not established

    Once transposed, collectors must screen out items and substances that could contaminate what they collect. Nothing on the jacket says what its finish is. Evidence: LIFE-04

  5. Evidence type and dateBatch number, if the label survives

    Recipient access
    Demonstrated
    Legal basis
    Applicable duty
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Illustrative assumption

    If it is on the sewn-in label, the batch number could lead back to the importer's records. We found no route by which a sorter uses it. Evidence: LAW-35TECH-29

Next The jacket goes to a sorting line, where trained people judge it by eye and read its label.

Link to this handover

Handover 6 of 6

Sorter to re-use or recycling

The jacket, graded into a bale for re-use or a stream for recycling

Can this be worn again or recycled, and is anything in it a problem?

Asked by the re-use buyer or recycler
What the rules supply
Each bale shipped for re-use will carry a record of the clothes inside, including “material composition”, and the sorter's name and address. Waste operators already have a legal right to the EU's database of substances of very high concern in products. Evidence: LIFE-33LIFE-23
What we could not establish
Whether this jacket can be recycled. A study for the Commission treats laminated jackets as non-recyclable, with no business case for taking them apart. Most were exported for re-use, and the fate of exported textiles is “highly uncertain”. Evidence: LIFE-15LIFE-34
Still unresolved
Whether the EU's PFHxA limit and France's PFAS ban apply to a second-hand jacket sold again or shipped abroad. The texts do not say. Evidence: LIFE-32LIFE-29
  1. Component identityBale record and label

    Recipient access
    Conditional or restricted
    Legal basis
    Future duty
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Documented general practice

    Near-infrared scanners read only the surface and “cannot detect the underlying materials” under coatings or layers. The label is cut off before mechanical recycling. Evidence: LIFE-13LIFE-18LIFE-15LIFE-33

  2. Chemical identity or groupSCIP database

    Recipient access
    Conditional or restricted
    Legal basis
    Applicable duty
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Documented general practice

    The database holds listed substances above 0.1%, so it is not a PFAS register. None of 10 recyclers interviewed used it regularly, and the Commission has proposed ending new notifications. Evidence: LIFE-23LIFE-24LIFE-25

  3. Concentration or test resultNone found

    Recipient access
    Not demonstrated
    Legal basis
    No duty identified
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Documented general practice

    Mechanical recycling does not destroy PFAS. A result from manufacture would be years old. In four stored jackets, one PFAS fell to a fifth of its first level or less, while perfluorooctanoic acid (PFOA) rose. Evidence: LAW-20LIFE-22TECH-26

  4. Hazard and handlingNone found

    Recipient access
    Not demonstrated
    Legal basis
    No duty identified
    Decision usefulness
    Not assessed
    Case evidence
    Documented general practice

    Europe's recyclers' trade body says they cannot be held responsible for “unknown chemical content”. One Swedish recycler said it cannot accept deliveries whose content it cannot ensure. Evidence: LIFE-19LIFE-20

  5. Evidence type and dateBale record

    Recipient access
    Conditional or restricted
    Legal basis
    Future duty
    Decision usefulness
    Insufficient for that decision
    Case evidence
    Documented general practice

    The bale record names the sorter and has no chemical field. It goes with the consignment to the first buyer, and no further. Evidence: LIFE-33LIFE-34

Next The bale record stops at the first buyer. After that, the label is the only record left, if it is still there.

Link to this handover

Second life

At the sorting line, people decide by eye and by label.

In 2025, France’s textile scheme collected 272,479 tonnes of used textiles. Its sorting centres sorted 216,264 tonnes: just over half for re-use, a quarter for recycling, and the rest for wiping rags and fuel. Evidence: LIFE-09

Automated secondary sorting handled one thousandth of what left those centres. Evidence: LIFE-14

No fixed list defines a garment fit to wear again. In a study of sorters in Italy, Czechia and Romania, they judged brand, condition, trend and colour by eye. Evidence: LIFE-11 A second study finds that sorters may rely on the care label for fibres, when it has not been removed or faded. Evidence: LIFE-12

So we asked what a sorter can read about this jacket, and what they pass on.

What left French sorting centres in 2025

0.1%: automated secondary sorting

Each square is one thousandth of the material leaving sorting. Evidence: LIFE-14

The care label

A quarter had no label. Of readable labels, 59% matched the fibres.

A 2019 study for the Dutch government counted labels on 10,901 used garments. Most recyclers it consulted said they do not rely on labels, partly because so many are gone or illegible by the time material reaches them. Evidence: TECH-29

Where a label could be read, it matched the fibres a sorting machine found in 59% of garments. The more fibres a garment mixed, the less often its label was right. The study checked fibres only. Evidence: TECH-30

10,901 used garments

  • 24% had no label, counting labels visibly cut out
  • 76% had a label

Readable labels that matched the fibres found

  • All 7,749 readable labels59%
  • By fibres in the garment
  • One fibre77%
  • Several fibres41%
  • Cotton and polyester23%
Netherlands, 2019. Single-layer garments only. A match was judged against a sorting machine’s reading, not a laboratory.

Sorting machines

They read the surface, not the layers beneath it.

The main automated method, near-infrared spectroscopy, measures light reflected from the visible surface. Refashion’s 2026 review of sorting technology lists multilayered items and surface treatments, waterproofing among them, as problematic: the method “cannot detect the underlying materials”. Evidence: LIFE-13

The machine in the Dutch study could sort only garments made of one material all the way through. A laminated jacket is not one of them. Evidence: TECH-31

What the light reaches

  1. The finish. A surface treatment. The review lists finishes and waterproofing as “problematic” for the method.

  2. Face fabric. The surface the light reaches. Near-infrared identifies the polymer it is made of.

  3. Membrane. Bonded between the two fabrics. Out of reach from either side.

  4. Lining. The jacket’s other face. Read only if it faces the sensor.

Illustrative cross-section of this jacket’s shell, not to scale.

The EU database

Of 10 recyclers asked, none used it regularly.

Since 2021, suppliers of products containing a substance of very high concern above 0.1% by weight have had to notify the EU’s SCIP database. Waste operators have a right to search it. It is the one EU channel built to carry chemical information to the waste stage. Evidence: LIFE-23LAW-14

In a study for the Swedish Chemicals Agency, one recycler that searched it found the results “not useful”, because it could not filter by material. Evidence: LIFE-24 SCIP lists only substances on the Candidate List, so a jacket missing from it is not shown to be free of PFAS. A Commission proposal from December 2025 would end new notifications. Evidence: LIFE-25

10 recyclers and the SCIP database

  • Interviewed10
  • Aware of SCIP4
  • Used it at least once2
  • Use it regularlyNone
Sweden, interviews from 2022 to 2023.

The bale record

Each bale will name its material, not its chemistry.

Once the 2025 amendment to the Waste Framework Directive is in national law, every bale shipped as fit for re-use must carry a record of what is inside and who sorted it. A copy travels with the consignment. Evidence: LIFE-33

It is the first record written for the jacket’s second life. Its material composition will come from care labels and a sorter’s eye, and it stops at the first buyer. Exports are the greatest share of the re-use market, the directive notes, and the fate of exported textiles is “highly uncertain”. Evidence: LIFE-33LIFE-15LIFE-34

A bale record

Record of sortingFit for re-use

Type of clothes
Rain jackets, adult
Size
Mixed, S to XL
Colour
Dark
Gender
Mixed
Material composition
Polyester
Final sorting
Sorter’s name and address

ChemicalsNot asked forEvidence: LIFE-33

Illustrative record, with the examples the directive gives.

The questions about PFAS carry on past the sorting line. France’s ban lets recycled fibre bring PFAS into new clothing, in proportion to the recycled share. The European Environment Agency wants textiles containing PFAS kept out of recycling, and finds them “very challenging” to identify by eye. Evidence: LIFE-30LIFE-21

The question about the finish reaches the sorting line. We found no record shown to carry the answer that far.

What would carry it

A record could carry the answer, if each reader can open it and use it.

The Global Framework on Chemicals (GFC), adopted in 2023, is voluntary. Its Target B2 is the closest it comes to this piece’s question, and it leaves the question open. Evidence: GFC-01GFC-02

The framework’s first International Conference, in Geneva from 16 to 20 November 2026, may adopt indicators for B2. The drafts count countries and stakeholders that have information systems. None counts whether a field reaches a recipient. Evidence: GFC-07GFC-08

So we asked the question one handover at a time: what already carries the finish’s chemistry, what a record would need to hold, who could open it and what they would need to use it. The measures and the package are our proposal, not GFC indicators or legal requirements.

Target B2, Global Framework on Chemicals

By 2030, stakeholders make available, to the extent possible, reliable information on chemicals in materials and products throughout the value chain.

  1. Stakeholders. The only actor named. The target names no sender, no recipient and no field. Evidence: GFC-02

  2. The qualifier. How far is possible, and for whom, is what this piece tests at each handover.

  3. Reliable. Not defined. The secretariat says its data do not yet show whether shared information is reliable. Evidence: GFC-02GFC-09

  4. The value chain. The framework covers chemicals through products and waste, so it reaches the sorter. Evidence: GFC-03

Indicators drafted for the conference

B2.1
Countries with measures on [globally] harmonised digital information systems
B2.2
Stakeholders using a [globally] harmonised standard, tool or platform to share information
B2.3
Countries making [globally] harmonised data publicly accessible

None countsA field reaching a recipientEvidence: GFC-08

Target as adopted in 2023. Indicators as drafted, with “[globally]” still in brackets.

What exists

Of six channels on this route, three reach past the owner.

Upstream, the finishing agent is the best-served point on the route. Viet Nam’s law requires a Vietnamese label on the drum, with its composition and hazards, and a safety data sheet if it is classed as hazardous. Evidence: VN-01VN-02VN-04

Two industry programmes screen the agent. Both say whether a chemical product passed. Neither says what remains in the finished fabric. Evidence: GFC-30VN-23GFC-31VN-21

Past the owner, the break is structural. In the words of the UN Environment Programme (UNEP), “Recyclers are outside the business-to-business information exchange because their connection to the data is interrupted by consumers.” Evidence: GFC-16

Three channels reach past that break. One is in force: the EU’s SCIP database, open to waste operators. None of 10 recyclers interviewed in Sweden used it regularly, and the Commission has proposed ending it. Evidence: LAW-14LIFE-24LIFE-25 One is a recommendation to governments from the UN Economic Commission for Europe (UNECE). The last, the EU’s digital product passport, waits for its textile rules, indicated for 2027. Evidence: GFC-20GFC-29

How far each channel reaches

  1. Viet Nam’s chemical and labelling lawBinding on the supplier Applicable duty. Reaches from the chemical supplier to the finishing mill.

  2. OEKO-TEX ECO PASSPORTVoluntary certification Voluntary provision. Reaches from the chemical supplier to the finishing mill.

  3. ZDHC GatewayVoluntary industry programme Voluntary provision. Reaches from the chemical supplier to the garment factory.

  4. UNECE Recommendation No. 46Recommendation to governments Voluntary provision. Reaches from the chemical supplier to the re-use buyer or recycler.

  5. EU digital product passportTextile rules indicated for 2027 Future duty. Reaches from the garment factory to the re-use buyer or recycler.

  6. EU SCIP databaseIn force. Repeal proposed Applicable duty. Reaches from the brand or importer to the re-use buyer or recycler.

  • Applicable duty
  • Voluntary provision
  • Future duty
Shaded: the owner, where UNEP places the break. Two channels in the table below are left off: the International Labour Organization (ILO) convention is not ratified on this route, and we found no textile use of the electronics standards.
What each channel can and cannot establish
ChannelCan improveCannot establishEvidence
Viet Nam’s chemical and labelling lawBinding on the supplierA Vietnamese label on the drum with composition, identification code and hazards, and a safety data sheet the mill must ask for and keep.Anything about the fabric after the mill. The safety data sheet is due only for a chemical classed as hazardous, and PFAS not classed as hazardous might not appear on one.Evidence: VN-01VN-02VN-04VN-24
OEKO-TEX ECO PASSPORTVoluntary certificationThe mill’s confidence that the finishing agent passed screening and testing.The finish’s identity: the formulation stays with OEKO-TEX. Whether the treated fabric meets STANDARD 100: the mark does not guarantee it.Evidence: GFC-30VN-23
ILO Convention No. 170 and Recommendation No. 177Binds 24 countries, not Viet Nam or FranceWorkers’ right to the finishing agent’s identity, hazards and handling, on labels and safety data sheets they can understand.A duty on this route, where neither country has ratified it. Anything about the fabric after the mill. An ingredient’s specific identity can be protected as confidential.Evidence: GFC-32GFC-33GFC-34GFC-35
ZDHC GatewayVoluntary industry programmeA record that a chemical product, or a facility’s chemical inventory, conforms to the ZDHC Manufacturing Restricted Substances List.The agent’s chemical identity: a ChemCheck report gives a product name and a conformance level, with no composition or Chemical Abstracts Service (CAS) numbers. What remains in the finished fabric.Evidence: GFC-31VN-21
UNECE Recommendation No. 46Recommendation to governmentsHarmonised traceability data across the garment chain, and minimum data behind composition claims, where governments act on it.Any duty on a company. We could not check whether its specifications define chemical fields.Evidence: GFC-20GFC-21GFC-22
EU digital product passportTextile rules indicated for 2027Substance name, location, concentration, safe use and end-of-life information, on the jacket or through a data carrier, with recyclers among those given access.The type and date of the evidence. Whether the data carrier survives wear, or a sorter can act on a chemical name.Evidence: GFC-26GFC-27GFC-28GFC-29
EU SCIP databaseIn force. Repeal proposedThe name of a Candidate List substance above 0.1% by weight, notified by the EU supplier and open to waste operators, and to consumers on request.Most PFAS, which are not on the Candidate List. A finish residue also sits far below 0.1%. The jacket carries no SCIP number, so a sorter has to look it up.Evidence: LAW-14LIFE-23LIFE-24LIFE-25
IEC 62474 and IPC-175xVoluntary, from electronicsComposition declarations passed between businesses in a standard data format.Process chemicals, which IEC 62474 excludes. We found no textile use.Evidence: GFC-24GFC-25

A minimum package

The EU’s list covers four of the five things to know. It has no slot for the evidence.

The package is the five things this piece follows through the journey, each kept with its record: who issued it, what kind of record it is, and when. A “PFAS-free” statement, a pass on a screening test and a measured value answer different questions. Only the record tells them apart. Evidence: GFC-14LIFE-22

Records in textile supply chains are mostly safety data sheets and test reports. A study for the Nordic Council of Ministers found that test reports may not state their method or detection limit, and that most information concerns what is absent. Evidence: VN-34

The EU’s Ecodesign for Sustainable Products Regulation (ESPR) sets the minimum that future product rules must track for substances of concern. It covers four of the five, and asks nothing about the type or date of the evidence. UNEP’s guidance says the date “would also be useful to provide”. Evidence: GFC-26GFC-17

A minimum package, against the EU’s list

What to knowESPR Article 7(5)Proposed access
Component identityWhich part, and what it is made of.(b) Where the substance sits in the productLegitimate interest
Chemical identity or groupThe finish's chemistry, as a named substance or a defined group.(a) Its name or numerical codePublic
Concentration or test resultA measured value, with its method and reporting limit.(c) Its concentration, maximum or rangeNo method or reporting limitPublic
Hazard and handlingWhat a person handling it should know and do.(d) Instructions for safe usePublic
(e) Information for re-use, recycling and end of lifeLegitimate interest
Evidence type and dateWho issued the record, what kind it is, and when.No slot
Our proposal. Article 7(5) is the minimum for future EU product rules. The access levels are a proposal in a study for the EU’s Joint Research Centre (JRC), not law. Evidence: GFC-26LAW-33

The key

A key helps only if it survives, the reader may open it, and the record is right.

Since December 2024, the jacket has had to carry a type, batch or serial number, with the name and address of its manufacturer and importer. That leads back to the business that holds its records. Its technical documentation goes to authorities, on request. Evidence: LAW-35

An EU passport would put the jacket’s chemistry behind a key like this one: on the product, or through a data carrier on it. A study for the European Commission’s Joint Research Centre (JRC) names the conditions. The information must be “really accurate so that the sorters can rely on it”, and the carrier “available and permanently attached to garments”. Evidence: GFC-27LIFE-27

The care label is already designed to make the whole journey, so it is the key we can test.

What a key needs, tested on the care label

  1. It survives. In a Dutch study of 10,901 used garments, 24% had no label. Evidence: TECH-29LIFE-27

  2. The reader may open it. The importer’s technical documentation goes to authorities, on request. Who may open a passport is left to each product group’s rules. Evidence: LAW-35GFC-28

  3. The record is right. In the same study, 59% of readable labels matched the fibres found. Evidence: TECH-30LIFE-27

Illustrative label for this investigation. The importer is fictional.

Reading it

Each reader would need more than access.

Information that reaches someone is not yet information they can use. The GFC treats skills as part of the work: Target B5 asks for training on chemical safety by 2030. Evidence: GFC-05

For smaller businesses taking up traceability tools, UN/CEFACT, the UN’s trade facilitation centre, finds the main obstacles are often cost and access, then language and a lack of training. Evidence: GFC-23

On the conference route, each reader needs something different.

What each reader would need

  • A square of slate ripstop fabric, pinked at the edges, with beads of water on it.

    At the millHandover 1

    • The label and safety data sheet in forms and languages workers easily understand. Evidence: GFC-35
    • Training in how to obtain and use them, which Viet Nam requires every two years. Evidence: GFC-33VN-08
    • A right to the chemical’s identity. Convention No. 170 gives one where ratified. Evidence: GFC-33GFC-34
  • The finished jacket folded flat, its long care label laid down the front, a pencil beside it.

    At the brandHandover 3

    • Test reports that state their method and detection limit. Evidence: VN-34
    • Staff who can read a certificate’s scope and the criteria that applied. Evidence: VN-31
    • A standard format for suppliers’ declarations, as electronics has. Evidence: GFC-24GFC-25
  • The jacket, worn and faded, on a pile of used clothes, its label still attached.

    At the sorting lineHandover 5

    • A data carrier still attached, and equipment to read it. Evidence: LIFE-27LIFE-26
    • Access rights, set by each product group’s rules. Recyclers are named; sorters are not. Evidence: GFC-28
    • The knowledge to interpret a substance’s name. Evidence: GFC-27
Illustrative images, made for this investigation.

Information is one target among several. Beside B2, the framework asks stakeholders to prioritise safer alternatives in consumer products. For consumer clothing, jackets included, a draft assessment of the EU’s proposed PFAS restriction lists fluorine-free finishes in general practical use. A record can tell the next reader what the finish is. It cannot make the finish safer. Evidence: GFC-06LAW-19

The jacket already carries a key to its records. Whether a sorter will find the finish behind it is still being decided.

What we found

We did not find the finish’s chemistry travelling as far as the jacket.

We asked whether information about the chemicals in a product can travel as far as the product. For one illustrative jacket, we followed five things to know across six handovers. We kept four questions apart: what requires each to pass, whether the next person can get it, whether it answers their question, and what this investigation can show.

Some information does travel. In Viet Nam, the law puts the finishing agent’s composition and hazards on the drum, in Vietnamese. The main fibres reach the owner, in French. A batch number and the importer’s address must be on the jacket. On the sewn-in label, they go the whole way, if it survives. Evidence: VN-04LAW-02LAW-35TECH-29

The finish is the weak thread. At the mill, the safety data sheet may not show whether it is PFAS-based. Once the jacket is in the EU, a listed substance is named only above 0.1% by weight, and an owner gets the name only by asking. From the owner on, none of the five answers the next person’s question on its own. Evidence: VN-03LAW-08LAW-09

Where each thing to know answers the next question

  1. Component identitySupports handovers 1 to 4 Supports the named decision at handovers 1 to 4. Insufficient for that decision at handovers 5 and 6.

  2. Chemical identity or groupSupports no decision Insufficient for that decision at handovers 1, 2, 3, 4 and 6. Not assessed at handover 5.

  3. Concentration or test resultSupports handover 1 Supports the named decision at handover 1. Insufficient for that decision at handovers 2, 3 and 6. Not assessed at handovers 4 and 5.

  4. Hazard and handlingSupports handovers 1 and 4 Supports the named decision at handovers 1 and 4. Not assessed at handovers 2, 3, 5 and 6.

  5. Evidence type and dateSupports handovers 1 and 3 Supports the named decision at handovers 1 and 3. Insufficient for that decision at handovers 2, 4, 5 and 6.

  • Supports the named decision
  • Insufficient for that decision
  • Not assessed
Decision usefulness, one of the journey’s four lenses: whether a field, once received, answers the next person’s question. Whether it arrives is a separate lens. Not assessed: the field does not bear on that question. Shaded: the owner.Open the journey in this lens
  1. Hypothesis 1

    Information useful for chemical handling may differ from information useful for assessing a finished article.

    What we found

    The record that protects a worker is not the record that describes the jacket.

    What supports it

    • The drum’s label gives the agent’s composition and hazards, for the people who handle it. Evidence: VN-04
    • A safety data sheet need name only ingredients classed as hazardous, above cut-offs. An unclassified polymer need not appear. Evidence: TECH-13
    • Where ratified, the International Labour Organization (ILO) chemicals convention reaches the drum, but generally not the finished fabric. Viet Nam and France have not ratified it. Evidence: GFC-32GFC-34
    • The fibre label is worked out with the finish left out, by law. Evidence: LAW-03
    • Even electronics’ declarations exclude process chemicals. They say what is in a product, not what was used to make it. Evidence: GFC-24

    What runs against it

    • AFIRM, a group of apparel and footwear brands, asks mills to pass safety data sheets and technical data sheets on to their customers. Evidence: VN-24
    • Under bluesign’s rules, a finished article at or above 50 mg/kg total fluorine sends the reviewer back to the formulation and its safety data sheet. Evidence: VN-28
    • The EU’s list for future product rules puts instructions for safe use beside a substance’s name and concentration, in one record. Evidence: GFC-26
  2. Hypothesis 2

    Information available to one actor may not be available or usable by the next.

    What we found

    Past the drum, what one business holds mostly stays with it. The care label is the exception.

    What supports it

    • If the supplier uses OEKO-TEX’s ECO PASSPORT, the formulation goes to OEKO-TEX in confidence and the mill receives a certificate. Evidence: GFC-30
    • The mill’s monthly chemical inventory report goes to brands. The garment factory is not a recipient, and the report covers the whole inventory, not a fabric roll. Evidence: VN-26
    • The importer’s technical documentation goes to authorities, on request. We found no route to the owner or the sorter. Evidence: LAW-35
    • The UN Environment Programme (UNEP): recyclers are outside the exchange between businesses, because consumers interrupt their connection to the data. Evidence: GFC-16

    What runs against it

    • The fibres of the main parts must reach the owner, on a durable label. Evidence: LAW-01LAW-02
    • On the sewn-in label, the batch number and importer’s address reach the sorter if the label survives. In one Dutch study, 24% of used garments had no label. Evidence: LAW-35TECH-29
    • In Viet Nam, a hazardous chemical’s safety data sheet must pass to the buyer. Trade-secret rules can still keep its composition off the sheet. Evidence: VN-02VN-03
  3. Hypothesis 3

    An identifier or digital record may help continuity without establishing accuracy, safety or practical access.

    What we found

    The keys we found lead to records. None shows the record is right, or gives a sorter the finish’s chemistry.

    What supports it

    • The jacket’s batch number leads back to the importer. It carries no chemical information. Evidence: LAW-35
    • In the Dutch study, 59% of readable labels matched the fibres a sorting scanner found. Evidence: TECH-30
    • Zero Discharge of Hazardous Chemicals (ZDHC) calls its ChemCheck report “an individual product passport”. Its listed contents give a product name and a conformance level, and no composition. Evidence: GFC-31VN-21
    • That EU database holds listed substances above 0.1% by weight. None of 10 recyclers interviewed used it regularly. Evidence: LIFE-23LIFE-24
    • The GFC secretariat says its data cannot yet show whether shared information is reliable. Evidence: GFC-09

    What runs against it

    • A certificate number lets anyone check online which criteria applied. Evidence: VN-31
    • Since November 2025, where a formulator prints one, a ZDHC code on the drum lets a mill worker check the agent’s conformance without logging in. Evidence: VN-22
    • Waste operators have a legal right of access to the EU’s database of substances in articles. Evidence: LAW-14

By role

What each reader could ask next.

The questions are our suggestions, drawn from the evidence above. Each links to where the piece covers it.

If you areAskStart at
Government delegates and regulatorsCould a B2 indicator count a named field reaching a named recipient, beside the systems that exist? Should sorters be named among those who may open a textile passport? Evidence: GFC-08GFC-28Target B2
Manufacturers, brands and buyersCan you connect the mill’s finishing record to this jacket’s batch, not only to the mill’s monthly inventory? Evidence: VN-26LAW-33Handover 2
Worker representatives and civil societyDo the people who handle the finishing agent receive its label and safety data sheet in their language, with the training Viet Nam requires? Evidence: VN-04VN-08GFC-35Handover 1
Sorters, reusers and recyclersWhich would change your decision on a water-repellent jacket: the finish’s chemical group, a total fluorine result, or the date of either? Evidence: LIFE-27LIFE-16A minimum package
Funders and implementation partnersWhich handover could one investment make work: training at the mill, a standard declaration format for brands, or carriers and readers at the sorting line? Evidence: GFC-23GFC-25LIFE-26Reading it

A gap here means we found no route. It does not mean there is none.

The evidence

Every claim, with its passage

175 claims from 104 sources, checked on 23 October 2026. Open a claim to read the passage it rests on, what it covers and where it stops.

Evidence registerRead the whole record.

Assessments

Five things to know at six handovers, each assessed in four lenses. The journey’s score draws these states.

Thing to knowRecipient accessLegal basisDecision usefulnessCase evidenceEvidence
Handover 1Chemical supplier to finishing mill
Component identityDrum labelDemonstratedDutySupportsPracticeEvidence: VN-01VN-04VN-22
Chemical identity or groupSafety data sheetConditionalUnresolvedInsufficientPracticeEvidence: VN-02VN-03TECH-13TECH-14TECH-16TECH-12
Concentration or test resultZDHC ChemCheck reportConditionalVoluntarySupportsPracticeEvidence: VN-19VN-20VN-21
Hazard and handlingDrum label and safety data sheetDemonstratedDutySupportsAssumptionEvidence: VN-04VN-08VN-09
Evidence type and dateCertificate or QR codeConditionalVoluntarySupportsPracticeEvidence: VN-21VN-22GFC-30
Handover 2Finishing mill to garment factory
Component identityFabric specificationConditionalNone foundSupportsAssumptionEvidence: TECH-03
Chemical identity or groupTreatment noticeConditionalVoluntaryInsufficientPracticeEvidence: VN-24VN-32VN-15
Concentration or test resultCertificateConditionalVoluntaryInsufficientPracticeEvidence: VN-30VN-28VN-31
Hazard and handlingNone foundNot shownUnresolvedNot assessedNot establishedEvidence: VN-07
Evidence type and dateZDHC InCheck, to the brandNot shownVoluntaryInsufficientPracticeEvidence: VN-26
Handover 3Garment factory to brand
Component identitySewn-in labelDemonstratedDutySupportsAssumptionEvidence: LAW-01LAW-02LAW-03
Chemical identity or groupSupplier declarationConditionalNone foundInsufficientPracticeEvidence: LAW-08LAW-12LAW-34VN-34
Concentration or test resultTest report or certificateConditionalVoluntaryInsufficientPracticeEvidence: TECH-25TECH-22VN-33LAW-34
Hazard and handlingCare symbolsDemonstratedNone foundNot assessedAssumptionEvidence: LAW-05LAW-06
Evidence type and dateCertificateConditionalVoluntarySupportsPracticeEvidence: VN-31LAW-24
Handover 4Brand to owner
Component identitySewn-in labelDemonstratedDutySupportsAssumptionEvidence: LAW-01LAW-02LAW-04
Chemical identity or groupOn request, or the product sheetConditionalDutyInsufficientPracticeEvidence: LAW-09LAW-26LAW-27TECH-28
Concentration or test resultNone foundNot shownNone foundNot assessedNot establishedEvidence: LAW-21LAW-16
Hazard and handlingCare symbols and product sheetConditionalDutySupportsPracticeEvidence: LAW-05LAW-29LAW-25
Evidence type and dateBatch number and importerDemonstratedDutyInsufficientAssumptionEvidence: LAW-35
Handover 5Owner to collector and sorter
Component identitySewn-in label, if it survivesDemonstratedNone foundInsufficientPracticeEvidence: LIFE-12TECH-29TECH-30LIFE-02
Chemical identity or groupNone foundNot shownNone foundNot assessedPracticeEvidence: LIFE-04LIFE-21LIFE-11
Concentration or test resultNone foundNot shownNone foundNot assessedPracticeEvidence: LIFE-21TECH-09
Hazard and handlingNone foundNot shownFuture dutyNot assessedNot establishedEvidence: LIFE-04
Evidence type and dateBatch number, if the label survivesDemonstratedDutyInsufficientAssumptionEvidence: LAW-35TECH-29
Handover 6Sorter to re-use or recycling
Component identityBale record and labelConditionalFuture dutyInsufficientPracticeEvidence: LIFE-13LIFE-18LIFE-15LIFE-33
Chemical identity or groupSCIP databaseConditionalDutyInsufficientPracticeEvidence: LIFE-23LIFE-24LIFE-25
Concentration or test resultNone foundNot shownNone foundInsufficientPracticeEvidence: LAW-20LIFE-22TECH-26
Hazard and handlingNone foundNot shownNone foundNot assessedPracticeEvidence: LIFE-19LIFE-20
Evidence type and dateBale recordConditionalFuture dutyInsufficientPracticeEvidence: LIFE-33LIFE-34

Claims

Download every claim, with its passage and source (JSON)

EU and French law35 claims

  1. LAW-01

    Under the EU Textile Labelling Regulation (TLR, Regulation (EU) No 1007/2011), a textile product may only be made available on the EU market if it is labelled or marked with its fibre composition, and a label must be durable, easily legible and securely attached. The manufacturer, or the EU importer where the manufacturer is outside the EU, answers for supplying the label and for its accuracy; between businesses in the supply chain, commercial documents may replace or supplement the label.

    LawEUPublications Office of the European Union (EUR-Lex)

  2. LAW-02

    The TLR label must give the name and percentage by weight of every constituent fibre in descending order, and where a product has textile components with different fibre contents, the content of each component. Components that are not main linings and weigh under 30% of the product need not be listed, so a jacket's label covers its outer fabric and main lining but may leave smaller textile parts unstated.

    LawEUPublications Office of the European Union (EUR-Lex)

  3. LAW-03

    When fibre composition is worked out for the TLR label, finishing chemistry is expressly left out: 'impregnating products' and 'other textile processing products' are not taken into account, nor are non-textile parts. The label is designed to say 'polyester', not what the polyester was finished with, so a durable water-repellent (DWR) finish has no place on it by law.

    LawEUPublications Office of the European Union (EUR-Lex)

  4. LAW-04

    Fibre composition must be clearly visible to the consumer before purchase, including when buying online, and the label must be in the official language or languages of the Member State where the jacket is sold to the consumer, unless that state provides otherwise. For a jacket sold in France the label must therefore be readable in French.

    LawEUPublications Office of the European Union (EUR-Lex)

  5. LAW-05

    EU law does not require a textile label to carry care instructions, country of origin, allergenic substances or any electronic labelling. In the TLR these appear only as topics the Commission was asked to examine in a review report due by 30 September 2013.

    LawEUPublications Office of the European Union (EUR-Lex)

  6. LAW-06

    A study for the Commission's Joint Research Centre (JRC) reports, citing the care-labelling association GINETEX (2017), that care instructions are mandatory in 12 EU Member States. France is not among those listed, so the care symbols on a jacket sold in France appear to be voluntary practice rather than a legal requirement.

    InterpretationEU / FranceEuropean Commission, Joint Research Centre (JRC)

  7. LAW-07

    No proposal to revise the TLR had been published by 20 September 2026. The European Parliament's Legislative Train marks the file 'Blocked', citing a revision planned for the second quarter of 2026 that would introduce specifications for physical and digital labelling of textiles.

    ProposalEUEuropean Parliament

  8. LAW-08

    Under REACH Article 33(1), any supplier of an article containing a substance of very high concern (SVHC) on the Candidate List above 0.1% weight by weight must give the recipient enough information for safe use, at least the substance name. The duty runs between EU supply chain actors: 'recipient' means a professional user or distributor and excludes consumers, and the information is only what is 'available to the supplier'.

    LawEUPublications Office of the European Union (EUR-Lex)

  9. LAW-09

    A consumer gets SVHC information only by asking. Under REACH Article 33(2), any supplier of the article must, on a consumer's request, give at least the substance name, free of charge, within 45 days.

    LawEUPublications Office of the European Union (EUR-Lex)

  10. LAW-10

    The Court of Justice ruled in 2015 (Case C-106/14) that the 0.1% threshold applies to each article that forms part of a complex product, not to the product as a whole. For a jacket, each constituent article (for example the outer fabric, the zip) is assessed separately, so dilution across the whole garment does not remove the duty to inform.

    LawEUCourt of Justice of the European Union (via EUR-Lex)

  11. LAW-11

    On 23 October 2026 the REACH Candidate List of substances of very high concern includes several PFAS (per- and polyfluoroalkyl substances): PFOA and its ammonium salt, the C11 to C14 perfluorocarboxylic acids, PFNA, PFDA, PFHxS, PFHpA, PFBS, HFPO-DA, perfluamine and a fluorinated morpholine mixture. PFHxA is not on it, and there is no group entry for PFAS, so the SVHC information duties (Article 33, SCIP, France's AGEC mention) do not reach PFHxA or PFAS in general.

    LawEUEuropean Chemicals Agency (ECHA)

  12. LAW-12

    The information duties and the restrictions work on scales 40,000 times apart. REACH Article 33 (and France's AGEC mention) start above 0.1% by weight, which is 1,000,000 parts per billion (ppb), while the PFHxA restriction starts at 25 ppb. A PFAS residue can make a jacket unlawful to sell long before any information duty would require anyone to name it.

    InterpretationEU / FrancePublications Office of the European Union (EUR-Lex)

  13. LAW-13

    Older restrictions already cap long-chain PFAS in the jacket: since 25 February 2023, REACH Annex XVII entry 68 bars articles containing 25 ppb or more of C9 to C14 perfluorocarboxylic acids (PFCAs) and their salts, or 260 ppb or more of related substances. Like the PFHxA rule, this is a restriction with no information duty attached.

    LawEUPublications Office of the European Union (EUR-Lex)

  14. LAW-14

    Since 5 January 2021, every EU supplier of an article must send the European Chemicals Agency (ECHA) the information it owes under REACH Article 33(1). ECHA holds it in the SCIP database and must give access to waste treatment operators and, on request, to consumers. This is the one route by which SVHC information from the point of sale is meant to reach sorters and recyclers; France transposed it in Code de l'environnement Article L. 521-5 III.

    LawEU / FrancePublications Office of the European Union (EUR-Lex)

  15. LAW-15

    The Commission proposed on 10 December 2025 (COM(2025) 986) to end the duty to submit data to SCIP, saying the database 'is not fulfilling its intended objectives'; data already reported would be kept. At 23 October 2026 the European Parliament's procedure file shows the proposal awaiting a committee decision, with an indicative plenary date of 14 December 2026. Until it is adopted, the SCIP duty still applies.

    ProposalEUEuropean Commission (via Publications Office Cellar)

  16. LAW-16

    Since 10 October 2026, REACH Annex XVII entry 79 (Commission Regulation (EU) 2024/2462) bars placing on the market textiles in clothing for the general public with 25 ppb or more of PFHxA (perfluorohexanoic acid) and its salts, or 1,000 ppb or more of PFHxA-related substances, measured in homogeneous material; the recitals name rain jackets. Jackets already placed on the market before that date are exempt, so the placing-on-the-market date becomes evidence the brand may need. The entry imposes no labelling or information duty.

    LawEUOfficial Journal of the European Union (via Publications Office Cellar)

  17. LAW-17

    The EU-wide 'universal' PFAS restriction is still a proposal. ECHA's Risk Assessment Committee (RAC) adopted its final opinion on 2 March 2026 and the consultation on the Socio-Economic Analysis Committee (SEAC) draft opinion ran from 26 March to 25 May 2026. SEAC is expected to adopt its final opinion by the end of 2026, after which the Commission will propose a restriction for a vote by Member States in the REACH Committee.

    ProposalEUEuropean Chemicals Agency (ECHA)

  18. LAW-18

    Under RAC's recommended conditions, the universal restriction would set limits of 25 ppb for any single PFAS by targeted analysis, 250 ppb for the sum of targeted PFAS, and 50 ppm for total PFAS including polymers, applying 18 months after entry into force. Where total fluorine exceeds 50 mg F/kg, the manufacturer, importer or downstream user would owe proof of the fluorine's origin to enforcement authorities on request. The only consumer statement, 'This product contains PFAS', is reserved for products that keep using PFAS under a derogation, and consumer apparel has none, so for this jacket the proposal would work as a ban without a label.

    ProposalEUEuropean Chemicals Agency (ECHA)

  19. LAW-19

    SEAC's draft assessment names jackets as consumer apparel, lists fluorine-free alternatives in general practical use (dendrimers, hybrid silicone/hydrocarbons, hydrocarbons, polyurethane, silicones), and concludes there is 'overwhelming evidence' against claims that PFAS cannot be replaced in consumer apparel, with high substitution potential at entry into force.

    ProposalEUEuropean Chemicals Agency (ECHA)

  20. LAW-20

    RAC agrees that mechanical recycling does not destroy PFAS and that only mixing with virgin, PFAS-free fibre lowers their concentration in recycled products. It notes that many PFAS-treated consumer textiles may enter normal textile recycling, and that no data exist on PFAS exposure of workers in textile recycling.

    Technical findingEUEuropean Chemicals Agency (ECHA)

  21. LAW-21

    Since 1 January 2026, French law bans the manufacture, import, export and placing on the market of clothing textiles for consumers that contain PFAS (Loi n° 2025-188, Code de l'environnement Article L. 524-1). All textiles follow from 1 January 2030, with listed exceptions. Products below a residual value set by decree are outside the ban.

    LawFranceJournal officiel de la République française, reproduced by AIDA (INERIS)

  22. LAW-22

    France's implementing decree defines PFAS as a group, any substance with at least one fully fluorinated CF3 or CF2 carbon, the same structural definition RAC uses. It sets the residual values at 25 ppb for any single PFAS and 250 ppb for the sum of targeted PFAS (both excluding polymers), and 50 ppm for PFAS including polymers. Where total fluorine exceeds 50 mg F/kg, the person placing the product on the market must prove to the authorities, on request, whether that fluorine comes from PFAS.

    LawFranceJournal officiel de la République française, reproduced by AIDA (INERIS)

  23. LAW-23

    France exempts clothing and footwear containing at least 20% recycled material from post-consumer waste, provided any PFAS in the finished product is limited to the recycled fraction. The exemption only works if someone can show the recycled share and where the PFAS came from, information that originates at the sorting and recycling stages.

    LawFranceJournal officiel de la République française, reproduced by AIDA (INERIS)

  24. LAW-24

    Clothing containing PFAS that was manufactured before 1 January 2026 may be placed on the French market or exported for at most twelve months from that date. The sell-off window closes on 31 December 2026, and the manufacturing date becomes the evidence that matters.

    LawFranceJournal officiel de la République française, reproduced by AIDA (INERIS)

  25. LAW-25

    Under France's anti-waste law (AGEC, Code de l'environnement L. 541-9-1 and R. 541-227 to R. 541-229), producers and importers with over EUR 10 million turnover and at least 10,000 units a year must publish a free, machine-readable 'fiche produit' for each new consumer product, accessible at the time of purchase. Information on hazardous substances may instead be given through an app designated by ministerial order, and the sheet must stay available for two years after the last unit is placed on the market.

    LawFranceAIDA (INERIS), consolidated reproduction of the Code de l'environnement

  26. LAW-26

    Where a hazardous substance is present above 0.1% by mass, the French product sheet must state 'contient une substance dangereuse' or, for a Candidate List substance, 'contient une substance extrêmement préoccupante', followed by the name of each substance. This turns REACH's on-request consumer right into published information for in-scope products.

    LawFranceAIDA (INERIS), consolidated reproduction of the Code de l'environnement

  27. LAW-27

    France's 'hazardous substances' for AGEC are the Candidate List SVHCs plus substances of comparable concern listed by ministerial order. The only order found (30 August 2023) adds two substances, DIOP and resorcinol, so French consumer disclosure adds no PFAS beyond those on the Candidate List.

    LawFranceJournal officiel de la République française, reproduced by AIDA (INERIS)

  28. LAW-28

    For clothing sold in France, the AGEC product sheet must name the country where each of three steps mainly took place: weaving, dyeing and printing, and making-up. For this jacket that would show Vietnam (in the scenario), but finishing, including the water-repellent treatment, is not a named step, so the place where the DWR chemistry was applied need not be disclosed.

    LawFranceAIDA (INERIS), consolidated reproduction of the Code de l'environnement

  29. LAW-29

    Where synthetic fibres make up more than 50% of a garment's mass, the French product sheet must carry the statement 'rejette des microfibres plastiques dans l'environnement lors du lavage' (releases plastic microfibres into the environment when washed). A polyester rain jacket meets that condition.

    LawFranceAIDA (INERIS), consolidated reproduction of the Code de l'environnement

  30. LAW-30

    A French law of 8 July 2026 (Loi n° 2026-602) requires the places of manufacture of clothing sold online to be shown clearly on the platform, in type the same size as the price and next to it.

    LawFranceJournal officiel de la République française, reproduced by AIDA (INERIS)

  31. LAW-31

    The Ecodesign for Sustainable Products Regulation (ESPR, Regulation (EU) 2024/1781) requires future product rules to let 'substances of concern' be tracked through the product's life: name, location in the product, concentration or range, safe-use instructions and end-of-life information, given on the product or through a data carrier on it. 'Substance of concern' is wider than the Candidate List, covering certain hazard classes, persistent organic pollutants and substances that hinder reuse and recycling. None of this binds a jacket until a textile delegated act is adopted.

    LawEUPublications Office of the European Union (EUR-Lex)

  32. LAW-32

    The Commission's first ESPR working plan (April 2025) ranks textiles and apparel first among final products, with indicative adoption of the delegated act in 2027, and says its information requirements will work with the Textile Labelling Regulation, then under review.

    ProposalEUEuropean Commission (via Publications Office Cellar)

  33. LAW-33

    A study for the JRC (13 May 2026) recommends that a textile digital product passport (DPP) give substance-of-concern data per batch, covering all chemicals for every colour in the batch. The substance identity and concentration would be public, while the substance's location in the garment and end-of-life handling information would be limited to actors with a 'legitimate interest'. Substances not intentionally added and absent from the final product would be exempt. It is a recommendation, not a draft act, and it does not mention PFAS.

    ProposalEUEuropean Commission, Joint Research Centre (JRC)

  34. LAW-34

    Stakeholders interviewed for the JRC study report that apparel brands and retailers rely on supplier declarations, contract terms and third-party certification to support claims that regulated substances are absent. OEKO-TEX Standard 100 is the most cited mechanism and works as a pass or fail against thresholds. Substance-level concentration and location data are not reported and, they say, are not available in a form that could be disclosed reliably.

    Reported practiceEU (reported practice across global supply chains)European Commission, Joint Research Centre (JRC)

  35. LAW-35

    The General Product Safety Regulation (GPSR, Regulation (EU) 2023/988), applying since 13 December 2024, requires a consumer product to carry a type, batch or serial number, and the name, postal and electronic address of the manufacturer and, for imports, of the importer, on the product or, where that is not possible, on packaging or an accompanying document. This gives the jacket an identity key back to the operators who hold its records, though it carries no chemical information, and technical documentation goes to authorities only on request.

    LawEUPublications Office of the European Union (EUR-Lex)

Viet Nam, and the programmes that reach its mills35 claims

  1. VN-01

    Viet Nam's Law on Chemicals requires every producer or importer of a chemical, not only of a hazardous one, to classify it under the Globally Harmonized System of Classification and Labelling of Chemicals (GHS) and label it before it is used or sold. Information also has to travel back up the chain: any business handling the chemical that finds a new hazard must promptly tell the producer or importer so that it reclassifies and relabels.

    LawViet NamVăn phòng Quốc hội (Office of the National Assembly), via Government e-documents portal

  2. VN-02

    A Vietnamese seller of a hazardous chemical must give the buyer a safety data sheet (SDS, 'phiếu an toàn hóa chất'), and the buyer must ask for it and keep it where the chemical is stored. The law also says the SDS and the chemical's trade name cannot be kept confidential. The SDS duty attaches only to chemicals that meet the legal definition of hazardous, so a finishing agent with no GHS hazard class carries no statutory SDS duty.

    LawViet NamVăn phòng Quốc hội (Office of the National Assembly), via Government e-documents portal

  3. VN-03

    For a mixture such as a DWR emulsion, the Vietnamese SDS template asks only for the identity and concentration range of hazardous components above the set thresholds, and says trade-secret (confidential business information, CBI) rules take priority when listing composition. A non-hazardous fluorinated or fluorine-free polymer need not appear, so the SDS a mill receives may not show whether the finish is PFAS-based.

    LawViet NamBộ Công Thương (Ministry of Industry and Trade, MOIT), Công báo (Official Gazette) No. 319

  4. VN-04

    A drum of finishing agent sold in Viet Nam must carry a Vietnamese-language label showing, among other items, its composition or quantitative composition, its chemical identification code if any, hazard pictograms, signal word and hazard statement if any, precautions and instructions for use and storage.

    LawViet NamChính phủ (Government of Viet Nam), via the Official Gazette site

  5. VN-05

    Viet Nam's import declaration for chemicals, which requires the SDS to be filed through the National Single Window before customs clearance, covers only goods in chapters 28 and 29 of the tariff nomenclature (inorganic and organic chemicals). Mixtures classed outside those chapters are exempt even if they contain chapter 28 or 29 chemicals.

    LawViet NamChính phủ (Government of Viet Nam)

  6. VN-06

    Interpretation: a DWR emulsion sold as a textile finishing preparation would ordinarily fall under Harmonized System (HS) heading 38.09 'finishing agents ... of a kind used in the textile ... industries' (or chapter 39 if presented as a polymer in primary form), not chapters 28 or 29. If so, its import into Viet Nam is exempt from the chemical import declaration, so the Vietnamese-language SDS field on that declaration does not reach it.

    InterpretationInternational (HS nomenclature) applied to Viet NamWorld Customs Organization (WCO)

  7. VN-07

    The Law on Chemicals separately obliges anyone engaged in chemical activities to give the authorities and users full and accurate information on the content of hazardous chemicals in chemicals and in products containing them. This is a general information duty towards users, but the law does not say how, when or in what form it is met.

    LawViet NamVăn phòng Quốc hội (Office of the National Assembly), via Government e-documents portal

  8. VN-08

    Workers who handle chemicals directly must receive chemical safety training at least every two years, with a first cycle of at least 8 hours. The training must cover the hazardous properties and SDSs of the site's hazardous chemicals, classification and labelling, and practice in recognising hazardous chemicals by their labels and pictograms.

    LawViet NamChính phủ (Government of Viet Nam), via the Official Gazette site

  9. VN-09

    Under Viet Nam's Occupational Safety and Health (OSH) Law, workers have a right to full information about hazardous and harmful factors at the workplace and the preventive measures, and to OSH training. Employers must inform workers about those factors, and manufacturers must supply safety information with products that may be unsafe at work. Warning signs and instructions for substances with strict safety requirements must be in Vietnamese and in the language the workers commonly use, placed where they are easy to read and see.

    LawViet NamVăn phòng Quốc hội (Office of the National Assembly), Công báo Nos 1169+1170 and 1171+1172

  10. VN-10

    Viet Nam lists PFOS (perfluorooctane sulfonic acid, with its sulfonates, sulfonamides and sulfonyls) and PFOA (perfluorooctanoic acid) and PFHxS (perfluorohexane sulfonic acid), each with salts and related compounds, as Group 2 'specially controlled chemicals' under the Stockholm and Rotterdam conventions. A mixture is specially controlled if it contains more than 1% by weight of one of them. These are the only per- and polyfluoroalkyl substances (PFAS) entries we found; there is no PFAS group listing.

    LawViet NamChính phủ (Government of Viet Nam), via the Official Gazette site

  11. VN-11

    Viet Nam registered a Stockholm Convention specific exemption for PFOA in 'textiles for oil and water repellency for the protection of workers from dangerous liquids'. The register shows it expired on 3 December 2025. Viet Nam's only active PFOA exemption is for perfluorooctyl iodide used to make perfluorooctyl bromide, so no PFOA exemption for textiles remains open to it. In the same register, the Government of Viet Nam gave as its reason that PFOA was still used in Viet Nam in several fields including textiles (an undated government statement, not measured data).

    LawInternational (Viet Nam entry)Secretariat of the Basel, Rotterdam and Stockholm Conventions

  12. VN-12

    The Stockholm Convention's listing of long-chain perfluorocarboxylic acids (PFCAs, C9 to C21), their salts and related compounds (decision SC-12/12) was communicated to Parties on 16 December 2025. Under Article 22 it enters into force one year after that communication for every Party that has not refused it or made an Article 25(4) declaration, which on the current record would include Viet Nam. Viet Nam's chemical lists do not yet include these substances.

    LawInternational (applies to Viet Nam)United Nations Treaty Collection

  13. VN-13

    Viet Nam's Law on Environmental Protection bans producing, exporting, importing and using persistent organic pollutants (POPs) in Stockholm Annex A, and goods containing them above the legal maximum, unless an exemption is registered. It also requires source control, information disclosure, labelling and conformity assessment for POPs and for goods containing them.

    LawViet NamQuốc hội (National Assembly), Công báo Nos 1185+1186 (25 December 2020)

  14. VN-14

    Viet Nam's environmental decree requires anyone importing, producing or trading goods containing POPs to label them with the POP's name and content, or with compliance with a relevant international standard. That duty is keyed to a national technical regulation on POP limits in goods, which we could not confirm has been issued. Whether it binds a PFOA-treated fabric today is unresolved.

    LawViet NamBộ Nông nghiệp và Môi trường (Ministry of Agriculture and Environment)

  15. VN-15

    Viet Nam has a product-level disclosure regime for hazardous chemicals in goods, but the Ministry of Industry and Trade's list of chemicals whose presence in products must be disclosed has 10 entries (acetone, cadmium, chromium VI compounds, formaldehyde, hydrochloric acid, lead, mercury, methanol, sulphuric acid and toluene), each tied to products such as glue, cleaners, plywood, batteries and electronics. No textile product and no PFAS is listed.

    LawViet NamBộ Công Thương (Ministry of Industry and Trade, MOIT), Công báo (Official Gazette) No. 319

  16. VN-16

    Where the product-disclosure regime does apply, it requires positive information: before sale, the producer or importer declares for each lot the product name, the hazardous chemical's name, its hazard, its content and the field of use on the national chemicals database, and publishes composition and content on its website or at the point of sale and on the product label.

    LawViet NamChính phủ (Government of Viet Nam)

  17. VN-17

    Viet Nam's technical regulation for textiles, QCVN 01:2017/BCT as amended in 2026, limits formaldehyde (30, 75 or 300 mg/kg by product group) and each aromatic amine released from azo dyes (30 mg/kg) in textile products before they go on the Vietnamese market. It sets no limit or information duty for PFAS or water-repellent finishes.

    LawViet NamBộ Công Thương (Ministry of Industry and Trade)

  18. VN-18

    Viet Nam's labelling decree sends export goods to the importing country's rules. Labels on exported goods follow the law of the importing country, contracts and treaties, and goods made only for export need not meet the rules for goods sold in Viet Nam. The Vietnamese textile label (composition, specifications, warnings, use and care instructions, year of manufacture) is therefore not required on a jacket made only for France.

    LawViet NamChính phủ (Government of Viet Nam), via the Official Gazette site

  19. VN-19

    The Zero Discharge of Hazardous Chemicals (ZDHC) Manufacturing Restricted Substances List (MRSL), version 3.1, does not permit any chemical formulation based on, or including, per- and polyfluoroalkyl substances (PFAS) for fashion, sport or outdoor clothing. A PFAS formulation is always deemed non-conformant, even for technical end uses that may need it, so a fluorinated durable water-repellent (DWR) agent for this jacket cannot be ZDHC-conformant.

    Voluntary standardInternationalZDHC Foundation (copy hosted by Lindex Group)

  20. VN-20

    The MRSL enforces its PFAS rule through a short list of marker substances rather than the whole class. ZDHC-approved certifiers test DWR formulations against limits in micrograms per kilogram of formulation (for example perfluorooctanoic acid (PFOA) 25 µg/kg; 6:2 fluorotelomer alcohol 1000 µg/kg) and may, at their discretion, screen for total fluorine with a quantification limit of 50 mg/kg.

    Voluntary standardInternationalZDHC Foundation (copy hosted by Lindex Group)

  21. VN-21

    The ZDHC ChemCheck report, which ZDHC says chemical formulators should share with customers, identifies a DWR product by organisation, product name, product ID and classification, and states its MRSL conformance level, MRSL version, certification body and certificate dates. Its listed contents include no Chemical Abstracts Service (CAS) numbers or composition: chemical supplier to mill, this channel passes a product name plus a conformance level, not chemical identity.

    Voluntary standardInternationalZDHC Foundation

  22. VN-22

    Since November 2025, chemical formulators can print a ZDHC QR code on drums or packaging. A mill worker who scans it, without logging in, sees product name, product ID, status, expiry, MRSL conformance level, Chemicals to Zero level, substrate and use category, enough to check conformance on delivery. The listed fields include no composition and no hazard or handling information.

    Voluntary standardInternationalZDHC Foundation

  23. VN-23

    ECO PASSPORT by OEKO-TEX certifies textile and leather chemicals, colourants and auxiliaries, such as a DWR agent. It is a chemical product certification, not a digital product passport. ZDHC recognises it as MRSL 3.1 conformance level 1, or level 2 with an on-site visit. However, formulation details given to OEKO-TEX stay confidential, and the mark does not guarantee that treated fabric will meet STANDARD 100.

    Voluntary standardInternationalOEKO-TEX AG

  24. VN-24

    AFIRM's PFAS phase-out guidance asks material suppliers, such as a finishing mill, to tell downstream customers when a material is water-repellent and what type of treatment (finish, coating, membrane or other) is used, and to collect and share safety data sheets (SDSs) and technical data sheets (TDSs). Because PFAS not classified as hazardous might not appear on an SDS, it recommends written confirmation from chemical suppliers that formulations are not PFAS-based.

    Voluntary standardInternationalAFIRM Group

  25. VN-25

    AFIRM publishes its 2026 RSL and its PFAS phase-out guidance in Vietnamese. The Vietnamese RSL carries the PFAS limits and a note that French Decree No. 2025-1376 on PFAS risks entered into force on 1 January 2026, so the French market rule is signposted in the mill's own language at the production end of the chain.

    Voluntary standardInternational (Vietnamese edition; refers to France)AFIRM Group

  26. VN-26

    A finishing mill's monthly ZDHC Performance InCheck report summarises the MRSL conformance of its whole chemical inventory, and brands connected to the mill on the ZDHC Gateway can review it. This channel runs straight from mill to brand. It reports facility-wide inventory conformance, not which chemicals went into a given fabric roll, and the garment factory is not a named recipient.

    Voluntary standardInternationalZDHC Foundation

  27. VN-27

    In June 2026 ZDHC said PFAS have no place in standard manufacturing and that its immediate focus is intentionally used PFAS in inputs. It acknowledged that newer test methods and broader definitions now find PFAS in some finished articles made with formulations previously considered compliant. ZDHC promised MRSL-related updates and a fuller PFAS communication, including how information should be communicated, for October 2026. None was found on ZDHC's news page on 23 October 2026.

    Voluntary standardInternationalZDHC Foundation

  28. VN-28

    For finished articles, the BSSL (bluesign System Substances List) bans intentional use of PFAS. It checks this against 50 mg/kg total fluorine (TF), a limit that also covers fluoropolymers such as PTFE (polytetrafluoroethylene), and against 25 µg/kg per substance and 250 µg/kg in sum for non-polymer PFAS. A TF result at or above 50 mg/kg requires a review of the chemical formulation, safety data sheet (SDS), technical data sheet (TDS) and other supply-chain records.

    Voluntary standardInternationalbluesign technologies ag (an SGS company)

  29. VN-29

    The bluesign system is run by bluesign technologies ag, an SGS company. In 2026 it replaced bluesign APPROVED and bluesign PRODUCT with one mark, bluepass, whose claims 'refer to processes, not to the product itself being certified'. A chemical supplier may give brands the hangtag wording 'bluepass fluorine-free water repellent'. The brand must verify the certified component by its bluesign Guide ID, and cannot call the jacket bluepass certified unless every component meets the thresholds.

    Voluntary standardInternationalbluesign technologies ag (An SGS Company)

  30. VN-30

    OEKO-TEX's current restricted substances list (RSL, version 03.2026) marks PFAS 'n.i.u.' (no intentional use). It also sets test limits for STANDARD 100 in every product class: 25 µg/kg for each PFAS, 250 µg/kg for their sum and 50 mg/kg total fluorine. For water repellents certified under ECO PASSPORT, the limits are 50 mg/kg total fluorine and 25 µg/kg for PFAS, and 'restrictions are not possible'.

    Voluntary standardInternationalOEKO-TEX

  31. VN-31

    A STANDARD 100 certificate covers only the articles and components described in its scope, in their as-produced state, for one year. The mark 'is not a quality label', and the certificate number lets anyone check online which criteria applied. From 2026, renewal requires every supplier that does wet or chemical processing, such as the DWR finishing mill, to hold a certificate for that product, and requires upstream certificates from the direct supplier. Both rules have a transition period until June 2027.

    Voluntary standardInternationalOEKO-TEX (OEKO-TEX Service GmbH)

  32. VN-32

    AFIRM separates claims about water-repellent products. 'Water-resistant, -repellent, or -proof' means the product may contain PFAS. 'No PFAS-based DWR finishing' cannot rule out a PFAS membrane such as polytetrafluoroethylene (PTFE). 'No intentional use of PFAS' allows contamination to be detected. Only 'no intentional use of PFAS, and PFAS not detected' covers both, and AFIRM strongly discourages 'free' claims.

    Voluntary standardInternationalAFIRM Group

  33. VN-33

    AFIRM says no single test both shows compliance with all PFAS rules and proves PFAS were not intentionally used. Total fluorine screening cannot distinguish PFAS from inorganic fluorine, and its best common detection limit is about 20 ppm. Targeted analysis of named PFAS is no guarantee that PFAS were not used. Untreated apparel can show several hundred ppm total fluorine, compared with several thousand ppm typically seen after intentional treatment.

    Voluntary standardInternationalAFIRM Group

  34. VN-34

    A Nordic Council of Ministers study, submitted to the Strategic Approach to International Chemicals Management (SAICM, predecessor of the Global Framework on Chemicals), drew on interviews mainly with brand owners. It found that textile supply-chain chemical information is mainly SDSs and test reports of variable quality, and mostly 'negative information' about absence rather than which chemicals were used. Exact composition is often withheld as a trade secret, test reports may not state methods or detection limits, and inventories cannot show per-batch use.

    Reported practiceInternationalSAICM secretariat; study funded by the Nordic Council of Ministers, submitted by Sweden

  35. VN-35

    In 2025 Vietnam was the second-largest supplier from outside the EU, after China, of synthetic-fibre anoraks and wind-jackets imported into the EU (CN 6201 40 and 6202 40). Those imports were worth €733 million, about 12% of extra-EU imports of these goods, against about 6% of all woven apparel (CN chapter 62). France imported €67 million of these goods directly from Vietnam.

    Technical findingEUEurostat (Comext)

Finishes, membranes and tests35 claims

  1. TECH-01

    The waterproof membrane laminated into many rain jackets is polytetrafluoroethylene (PTFE), often in expanded form (ePTFE). The Swedish Chemicals Agency (KEMI) classes PTFE as a fluoropolymer within the per- and polyfluoroalkyl substances (PFAS) group, so a jacket can contain PFAS in its membrane whatever chemistry is used for the durable water-repellent (DWR) finish.

    Technical findingInternationalSwedish Chemicals Agency (KEMI)

  2. TECH-02

    EU law already uses the Organisation for Economic Co-operation and Development (OECD) structural definition of PFAS: any substance with at least one fully fluorinated methyl (CF3) or methylene (CF2) carbon atom. PTFE, built from repeating CF2 units, and side-chain fluorinated DWR polymers both fall within it. The definition names a group, not an exact substance.

    LawEUEuropean Commission (Official Journal of the European Union)

  3. TECH-03

    The waterproof layer of a rain jacket can be a microporous membrane of PTFE or polyurethane (PU), or a non-porous hydrophilic membrane of PU or polyester. A DWR finish is applied to the outer fabric of all shell garments whichever membrane is used, so the finish and the membrane raise separate chemical questions.

    Technical findingInternationalUniversity of Leeds (White Rose eTheses Online)

  4. TECH-04

    In all-weather clothing, fluorine can come from two places: a porous PTFE membrane and an outer nylon or polyester fabric treated with side-chain fluorinated polymers (SFPs). KEMI reports that the volatile fluorotelomer alcohols (FTOHs) found in clothing come from the SFP finish, not the membrane, and puts PFAS at about 2 to 3 per cent of fibre weight in treated textiles.

    Technical findingInternationalSwedish Chemicals Agency (KEMI)

  5. TECH-05

    The DWR finish is applied at the finishing mill, after dyeing or printing and before garment making, as a thin film by a pad-dry-cure process together with other finishing auxiliaries, then cured in an oven at up to 180°C. The mill is therefore the last actor in the chain to handle the finish as a chemical mixture; from H2 onwards it travels as part of a treated fabric.

    Technical findingInternationalDanish Environmental Protection Agency

  6. TECH-06

    A chain-length description such as 'C6' describes the intended chemistry of an SFP product, not its full content. KEMI reports an industry figure of under 0.01 per cent C8 residue in C6 products alongside studies finding large contents of C8 and longer chains in products marketed as 'C6', and notes that SFPs can contain or degrade to FTOHs and to perfluorinated carboxylic acids such as perfluorooctanoic acid (PFOA) and perfluorohexanoic acid (PFHxA).

    Technical findingInternationalSwedish Chemicals Agency (KEMI)

  7. TECH-07

    Fabric coated with an SFP-based DWR can carry unreacted residues and impurities, the DWR emulsion itself mixes polymers with shorter and longer side chains, and ageing of coated fabric increased the measured perfluoroalkyl acids (PFAAs). The chemistry on a jacket at sale or at collection is not the same as the chemistry in the finishing bath.

    Technical findingInternationalEnvironmental Science & Technology (American Chemical Society)

  8. TECH-08

    Researchers comparing DWR chemistries coated their own fabrics because, for commercial outdoor clothing, it is often unknown which DWR chemistry and other additives were applied. Even specialists could not rely on information travelling with commercial garments to tell which finish they carried.

    Technical findingInternationalEnvironmental Science & Technology (American Chemical Society)

  9. TECH-09

    Fluorine-free DWRs can provide water repellency, but a Danish Environmental Protection Agency (Danish EPA) survey found none that repel oil, alcohol or oil-based dirt as PFAS-based finishes do. Water repellency is therefore not evidence of PFAS; strong oil repellency points towards fluorinated chemistry but is not a test for it.

    Technical findingInternationalDanish Environmental Protection Agency

  10. TECH-10

    'Fluorine-free' does not mean 'hazard-free'. A 2016 review found that impurities or degradation products of every DWR chemistry reach the environment, ranked hydrocarbon DWRs as the most environmentally benign followed by silicone and then SFP-based chemistries, and found hazard data lacking for dendrimer and nanoparticle finishes. This is a hazard ranking, not a product-specific exposure or risk conclusion.

    Technical findingInternationalEnvironment International (Elsevier)

  11. TECH-11

    The Danish EPA found the compositions of alternative water-repellent agents mainly confidential, with some containing isocyanates, dipropylene glycol, metal salts or other unspecified substances. It found hardly any information on the trace raw materials, intermediates and degradation products left in finished textiles.

    Reported practiceInternationalDanish Environmental Protection Agency

  12. TECH-12

    Supplier information for alternative water-repellent agents summarised by the Danish EPA described ingredients only as 'an unknown functionalized polymer' or 'an unknown organic silicon compound' with concentration ranges, and producers' statements that products need no environmental classification could not be verified. A record like this tells the mill a polymer is present but not what it is.

    Reported practiceInternationalDanish Environmental Protection Agency

  13. TECH-13

    Under the UN Globally Harmonized System of Classification and Labelling of Chemicals (GHS), a mixture's safety data sheet (SDS) must give the identity and concentration of ingredients that are hazardous within GHS and present above cut-off levels: 1 per cent for most classes, 0.1 per cent for sensitisers, carcinogens, reproductive toxicants and category 1 mutagens. Listing non-hazardous ingredients is optional, and the cut-off table has no class for persistence, so an unclassified polymer need not appear.

    LawInternationalUnited Nations

  14. TECH-14

    GHS lets national rules on confidential business information override ingredient identification on an SDS, provided this does not compromise the health and safety of workers or consumers or the protection of the environment. Where identity is withheld, the SDS should say that composition information was omitted.

    LawInternationalUnited Nations

  15. TECH-15

    In the EU, the SDS for a mixture that is not itself classified must still list substances hazardous at 1 per cent or more, and substances at 0.1 per cent or more that are persistent, bioaccumulative and toxic (PBT), very persistent and very bioaccumulative (vPvB), on the Candidate List of substances of very high concern, or endocrine disruptors. Unclassified substances, including most polymers, may be listed but need not be.

    LawEUEuropean Commission (Official Journal of the European Union)

  16. TECH-16

    Taken together, an SDS for a DWR agent does not necessarily reveal whether the finish is fluorinated. Polymers are exempt from REACH registration, SDS rules require only classified ingredients above cut-offs to be named, and confidentiality rules can withhold identity, so an unclassified side-chain fluorinated polymer, or residual PFAS below cut-offs, can be absent from SDS section 3.

    InterpretationInternationalEuropean Environment Agency

  17. TECH-17

    EU classification rules gained new hazard classes in 2023, including persistent, mobile and toxic (PMT) and very persistent, very mobile (vPvM). Substances placed on the market before 1 May 2025 must be classified against them by 1 November 2026, and a mixture containing 0.1 per cent or more of a PMT or vPvM component must be classified from 1 May 2026, or by 1 May 2028 if already on the market.

    LawEUEuropean Commission (Official Journal of the European Union)

  18. TECH-18

    The European standard EN 17681-1:2025 measures a defined target list of PFAS in textiles by liquid chromatography with tandem mass spectrometry (LC-MS/MS). It does not measure side-chain fluorinated polymers directly: alkaline hydrolysis releases degradation products such as PFOA or fluorotelomer alcohols, from which the polymers' contribution is inferred against limits for PFOA and C9 to C14 PFCA-related substances.

    Voluntary standardEUEuropean Committee for Standardization (CEN), via the Estonian Centre for Standardisation (EVS) catalogue

  19. TECH-19

    Its companion, EN 17681-2:2022, uses gas chromatography for selected volatile PFAS such as fluorotelomer alcohols, and both parts are needed to cover PFOA-related substances. The standard notes that deciding whether side-chain polymers are intentionally present may need an alkaline hydrolysis step that it does not yet include.

    Voluntary standardEUEuropean Committee for Standardization (CEN), via the Estonian Centre for Standardisation (EVS) catalogue

  20. TECH-20

    Total fluorine methods find fluorine that targeted tests miss but cannot say what it is. Combustion ion chromatography (CIC) cannot distinguish organic from inorganic fluorine or identify compounds, and can lose volatile compounds; particle-induced gamma-ray emission (PIGE) measures a surface at sensitivities of 68 to 238 parts per million and also cannot separate organic from inorganic fluorine. There are no standard methods for total fluorine or total organic fluorine in environmental samples.

    Technical findingInternationalAnalytical and Bioanalytical Chemistry (Springer)

  21. TECH-21

    Other screening methods have blind spots too. Extractable organic fluorine (EOF) is underestimated when compounds are lost during solid-phase extraction. The total oxidisable precursor (TOP) assay converts only some precursors into measurable acids, leaves terminal acids unchanged and gives no speciation, and high-molecular-weight fluoropolymers are often missed by both LC-MS/MS and the TOP assay. Each method answers a different question, and none alone establishes 'PFAS-free'.

    Technical findingInternationalAnalytical and Bioanalytical Chemistry (Springer)

  22. TECH-22

    When papers and textiles treated with PFAS were measured for total fluorine by PIGE, targeted volatile and ionic PFAS accounted for at most 2.2 and 0.41 per cent of it, and most fluorine stayed in the material after solvent extraction. A clean result on a targeted list can therefore coexist with substantial non-extractable fluorine.

    Technical findingInternationalEnvironmental Science & Technology (American Chemical Society)

  23. TECH-23

    In multi-layer firefighter garments, the PTFE moisture-barrier film carried by far the highest total fluorine (122,000 milligrams of fluorine per kilogram), and researchers needed layer-by-layer testing plus pyrolysis gas chromatography-mass spectrometry (py-GC/MS) to tell PTFE film from SFP-finished fabric. By analogy, a total fluorine result on a whole laminated rain-jacket fabric cannot say whether the fluorine comes from the DWR or the membrane.

    Technical findingInternationalEnvironmental Science & Technology (American Chemical Society)

  24. TECH-24

    Reporting limits differ by orders of magnitude between methods. In a study of 93 children's products, total fluorine screening had a detection limit of 10 parts per million and is biased low for heavily fluorinated material, while targeted PFAS had quantification limits of 1.11 to 26.6 nanograms per gram (parts per billion). The authors also found that products labelled waterproof may contain PFAS even where a physical barrier gives the water resistance, and that 'green' assurances did not reliably indicate absence of PFAS.

    Technical findingInternationalEnvironmental Science & Technology (American Chemical Society)

  25. TECH-25

    In a 2026 study of products mainly from the Swiss market chosen for water- or grease-proofing, total fluorine was detected in 87 per cent of 15 textiles while every targeted PFAS was below 165 parts per billion. A modified TOP assay, which converts oxidisable precursors including side-chain fluorinated polymers, raised targeted PFAS in textiles by a factor of 1,300 on average and, across all products, showed a significant share of samples with precursors yielding PFHxA above a 1,000 ppb threshold that direct targeted testing did not reveal.

    Technical findingInternationalChemosphere (Elsevier)

  26. TECH-26

    Sixteen outdoor jackets bought in 2011 and 2012 contained PFAS at 0.03 to 719 micrograms per square metre, with PFOA in all of them. After 3.5 years of sealed storage, four jackets kept only 10 to 20 per cent of their initial 8:2 FTOH while PFOA rose, so a test result describes the garment on the day it was tested.

    Technical findingInternationalChemosphere (Elsevier)

  27. TECH-27

    Until 2025 there was no certified reference material (CRM) for PFAS in textiles. The first, for 18 PFAS in an outdoor textile, was produced by Germany's Federal Institute for Materials Research and Testing (BAM) for quality control of methods such as EN 17681-1, so laboratories had no certified textile benchmark for these results before then.

    Technical findingInternationalAnalytical and Bioanalytical Chemistry (Springer)

  28. TECH-28

    On the care labels of 17 outdoor jackets on sale in 2015 and 2016, none stated the DWR chemistry. Some named the membrane, as a fabric 'with a PTFE membrane' or as an ePTFE or PTFE percentage in the fibre composition, so membrane identity can travel on the label while finish chemistry does not. Swing tags were left out because they are easily removed after purchase.

    Reported practiceUnited Kingdom and Germany (jackets sampled in shops)University of Leeds (White Rose eTheses Online)

  29. TECH-29

    In a 2019 study for the Dutch government of 10,901 post-consumer garments, 24 per cent had no label, a figure that counted visibly cut-out labels as 'no label'. Most recyclers consulted said they do not rely on label composition declarations, partly because labels are often no longer present or legible when material reaches them.

    Reported practiceNetherlandsCircle Economy, for the Netherlands Ministry of Infrastructure and Water Management (published as parliamentary annex blg-930139)

  30. TECH-30

    In the same study, only 59 per cent of readable labels matched the fibre composition found: 77 per cent for single-fibre garments, 41 per cent for multi-fibre garments and 23 per cent for cotton-polyester blends. Accuracy was judged against the sorting machine's near-infrared (NIR) categorisation, not laboratory analysis.

    Reported practiceNetherlandsCircle Economy, for the Netherlands Ministry of Infrastructure and Water Management (published as parliamentary annex blg-930139)

  31. TECH-31

    Because it relies on NIR, the Fibersort automated sorting system used in the Dutch study can sort only monomaterial garments, meaning those with a composition homogeneous across the whole product, and therefore only single-layer garments. A laminated rain jacket falls outside what such a system can sort by fibre.

    Technical findingNetherlandsCircle Economy, for the Netherlands Ministry of Infrastructure and Water Management (published as parliamentary annex blg-930139)

  32. TECH-32

    NIR recognition reads the surface facing the analyser. In an automated sorting-line study, coatings and finishes caused mismatched recognition depending on which side faced the NIR analyser, very thin fabrics let NIR pass through, and ageing changed spectra. NIR identifies fibre type; it is not a test for DWR chemistry, and for a laminate the reading may depend on which face is scanned.

    Technical findingInternationalRecycling (MDPI)

  33. TECH-33

    In a 2025 study of 1,682 post-consumer textile items from residual waste in Catalonia, quantitative fibre composition by NIR agreed with the ISO 1833 laboratory method in only 37.9 per cent of cases, which the authors attribute to the limits of automated techniques for fibre blends.

    Technical findingSpainTextiles (MDPI)

  34. TECH-34

    The European Environment Agency (EEA) finds that by the end-of-life stage any information on PFAS content in a textile has usually been lost, that chemical analysis to find PFAS-containing textile waste is expensive and generally not feasible, and that visual inspection does not work. It suggests sorting based on digital product information or X-ray fluorescence (XRF), at high cost if done at scale.

    Technical findingEUEuropean Environment Agency

  35. TECH-35

    The EEA reports that, apart from a few PFAS identified as substances of very high concern, information on the presence and type of PFAS in textiles made outside the EU and sold in it is often extremely difficult to obtain. It gives three reasons: REACH registration does not extend to polymers or finished articles; suppliers may lack technical understanding and find requirements hard to pass up the chain; and suppliers hesitate to disclose.

    Reported practiceEUEuropean Environment Agency

Second life35 claims

  1. LIFE-01

    The EU Waste Framework Directive (WFD), as amended in 2018, required Member States to set up separate collection of textiles by 1 January 2025. The duty names a material category only. Nothing about the item's materials or chemistry has to accompany it, so the jacket can enter a textile collection point carrying only its sewn-in label.

    LawEUEuropean Parliament and Council of the European Union (OJ L 150, 14.6.2018, p. 109)

  2. LIFE-02

    The 2025 textile amendment to the Waste Framework Directive (WFD) requires producer responsibility organisations (PROs) under extended producer responsibility (EPR) to collect used textiles 'regardless of their nature, material composition, condition, name, brand, trademark or origin'. Collection is designed so that the person handing over the jacket has to supply no information.

    LawEUEuropean Parliament and Council of the European Union (OJ L series 2025/1892, 26.9.2025)

  3. LIFE-03

    Under the 2025 amendment to the Waste Framework Directive (WFD), separately collected used textiles are 'considered to be waste upon collection'. The exception is an item handed over directly by the end user and professionally assessed as fit for re-use at the collection point by a re-use operator or social economy entity. At H5, the jacket's legal status turns on a trained person's inspection, not on any record that travels with it.

    LawEUEuropean Parliament and Council of the European Union (OJ L series 2025/1892, 26.9.2025)

  4. LIFE-04

    The operative text of the 2025 textile amendment to the Waste Framework Directive (WFD) mentions substances once, in a duty to screen collected textiles 'to identify and remove non-target items or materials or substances that are potential sources of contamination'. A search of the operative articles found no use of 'chemical' or 'hazardous', and no duty for producers to pass chemical information to collectors or sorters. The recitals leave the tracking of substances of concern to the Ecodesign for Sustainable Products Regulation (ESPR).

    InterpretationEUEuropean Parliament and Council of the European Union (OJ L series 2025/1892, 26.9.2025)

  5. LIFE-05

    Once the 2025 amendment to the Waste Framework Directive (WFD) is transposed, sorters must separate items fit for direct re-use 'item-to-item', using 'up-to-date sorting criteria relevant to the receiving market'. Items not suitable for re-use go to remanufacturing and recycling, including fibre-to-fibre recycling 'where technological progress allows'. The criteria named are market criteria. Neither route has a chemical criterion.

    LawEUEuropean Parliament and Council of the European Union (OJ L series 2025/1892, 26.9.2025)

  6. LIFE-06

    France's textile extended producer responsibility (EPR) scheme, called REP TLC (textiles, chaussures, linge de maison) and run by the producer responsibility organisation Refashion, must ensure traceability of used textile waste to final treatment. Its standard contract with sorters must set out the traceability evidence that proves effective final re-use or recovery. Information about where sorted textiles go therefore travels back up the chain. The provisions say nothing about chemical content.

    LawFranceMinistère de la Transition écologique; consolidated text published by INERIS (AIDA)

  7. LIFE-07

    The fee adjustments (eco-modulations) in France's textile extended producer responsibility scheme (REP TLC) reward durability, recycled content and certification by named environmental labels, including Oeko-tex Made in Green, Bluesign, the EU Ecolabel and the Global Organic Textile Standard (GOTS). From 1 September 2026 a durability penalty of 12 euros per coat or jacket, rising to 19.50 euros from 2030, applies where the product's 'score D' is 0.8 or less. The consolidated text has no criterion on hazardous substances, per- and polyfluoroalkyl substances (PFAS) or finishes, and none of these adjustments produces information for sorters.

    LawFranceMinistère de la Transition écologique; consolidated text published by INERIS (AIDA)

  8. LIFE-08

    France's textile extended producer responsibility (EPR) rules set a recycling target for used textiles made of at least 90% synthetic plastic material: 50% from 2025 and 90% from 2028 of the quantity collected, sorted and not re-used. The rules also required a study, due by 1 January 2025, on synthetic products that combine different polymers. If no recycling solution is found, an 'eco-design penalty' for non-recyclability may be proposed. A polyester jacket with a laminated membrane may be such a multi-polymer product, depending on what the membrane is made of.

    LawFranceMinistère de la Transition écologique; consolidated text published by INERIS (AIDA)

  9. LIFE-09

    Refashion's 2025 key indicators report 272,479 tonnes of used textiles collected and 216,264 tonnes sorted (84% in France) by 74 contracted sorting centres that reported, 56 of them in France. Of the sorted tonnage, 54.47% went to re-use, 25.31% to materials for recycling, 11.03% to wiping rags and 8.4% to solid recovered fuel (combustible solide de récupération, CSR).

    Reported practiceFranceRefashion

  10. LIFE-10

    In December 2022 Refashion, the French textile producer responsibility organisation, told its members that no clothing, household linen or footwear product could lawfully carry a 'recyclable' claim under Code de l'environnement Article R.541-221 VI. One reason is that the criteria require 'the absence of elements or substances disrupting sorting, recycling or limiting the use of the recycled material'. Refashion concluded that the environmental product sheet should carry no recyclability information.

    InterpretationFranceRefashion

  11. LIFE-11

    A 2025 study for the European Commission's Joint Research Centre (JRC), based on sorters in Italy, Czechia and Romania, found 'no fixed criteria list' for deciding whether a garment is fit for re-use. Sorters follow facility manuals and judge usability, trend, colour, brand and visible damage. The re-use decision rests on what a trained person can see.

    Reported practiceEU (Italy, Czechia, Romania)Joint Research Centre, European Commission (External Study report; Bakowska, O. et al.; Huygens, D., editor)

  12. LIFE-12

    A 2026 study for the Joint Research Centre (JRC) on digital product passport (DPP) content for apparel finds that, at end of life, sorters and recyclers 'may rely on the information in physical labels' for garment composition, 'when they are not removed or faded'. It also finds that reading labels is slow, and that wear and removal compromise their accuracy and availability. The care label is the main composition record that reaches the sorter, and only if it survives.

    Reported practiceEUEuropean Commission, Joint Research Centre (JRC)

  13. LIFE-13

    Refashion's July 2026 review of sorting technology states that near-infrared (NIR) spectroscopy, the main automated method for identifying fibres, reads only the visible surface. Multilayered items and surface treatments 'such as coatings, finishes, dyes, waterproofing' are problematic because 'the technology cannot detect the underlying materials'. A coated face fabric over a laminated membrane falls squarely in this limitation.

    Technical findingEU (survey of European equipment suppliers)Refashion

  14. LIFE-14

    Refashion's 2026 environmental assessment of the French scheme reports that automated secondary sorting (sur-tri automatisé) was applied to only 0.1% of the material leaving sorting in 2025. Almost all routing decisions in the French system are therefore made by people reading labels and looking at garments.

    Reported practiceFranceRefashion

  15. LIFE-15

    The Joint Research Centre (JRC) textile waste study treated multilayered items as non-recyclable because 'there is no business case for their disassembly in Europe'. Multilayered items such as jackets and coats were 5.2% of its sample, and 'most of them were managed as reusable garments exported outside the EU'. Removing a membrane before recycling is not current practice. A laminated rain jacket that is not re-used in Europe most likely goes to export for re-use.

    Reported practiceEU (Italy, Czechia, Romania)Joint Research Centre, European Commission (External Study report; Bakowska, O. et al.; Huygens, D., editor)

  16. LIFE-16

    The Joint Research Centre (JRC) textile waste study states that its list of recycling disruptors 'lacks more detailed information (such as chemical composition) on various coatings, repellents, laminates or prints'. These probably occurred in the sample but 'were not identified in the data collection process'. Water repellents and laminates reach sorting as unidentified chemistry.

    Technical findingEU (Italy, Czechia, Romania)Joint Research Centre, European Commission (External Study report; Bakowska, O. et al.; Huygens, D., editor)

  17. LIFE-17

    The Joint Research Centre (JRC) textile waste study recommends focusing sorting for recycling on items of little second-hand value made of one layer, or several layers of the same material, and 'not covered in waterproof treatment, coating or excessive accessories'. A laminated rain jacket with a water-repellent finish fails these criteria on its defining features, before any chemical question is asked.

    Technical findingEUJoint Research Centre, European Commission (External Study report; Bakowska, O. et al.; Huygens, D., editor)

  18. LIFE-18

    In the Joint Research Centre (JRC) textile waste study, even garments judged ready for closed-loop mechanical recycling still need 'the care labels' removed before recycling. Near-infrared (NIR) scanning will not recognise elastane below 5% of a blend. The sewn-in label, the record designed to stay with the garment, becomes a disruptor and is cut off at this point.

    Technical findingEUJoint Research Centre, European Commission (External Study report; Bakowska, O. et al.; Huygens, D., editor)

  19. LIFE-19

    In a 2023 evaluation for the Swedish Chemicals Agency (KemI), the textile recycler Re:newcell said it may be offered deliveries, such as face masks, that it cannot accept 'since they cannot ensure its content'. Recyclers interviewed said they benefit from knowing chemical content 'at both item and material level', and one textile recycler accepts only flows labelled with the Nordic Swan Ecolabel. Without content information, recyclers fall back on refusing material or restricting intake to certified flows.

    Reported practiceSwedenSwedish Chemicals Agency (Kemikalieinspektionen), study by Ramboll

  20. LIFE-20

    The European Recycling Industries' Confederation (EuRIC), the trade body for Europe's recyclers, states that 'Recyclers cannot be held responsible for unknown chemical content in post-consumer textiles'. It cites 'the challenges of tracking thousands of substances in post-consumer textiles', and holds that trained sorting operators are best placed to judge reusability. This is an industry position, not a finding.

    Reported practiceEUEuRIC (European Recycling Industries' Confederation)

  21. LIFE-21

    The European Environment Agency (EEA) finds that when textiles reach end of life, 'any available information on PFAS content has usually been lost'. PFAS means per- and polyfluoroalkyl substances. Chemical analysis is 'expensive and generally not feasible', and identifying PFAS-containing textiles by visual inspection is 'very challenging'. The EEA calls for sorting and recycling investment that ensures PFAS-containing textiles are not recycled, and says current practice cannot trace PFAS at the waste stage.

    Technical findingEUEuropean Environment Agency

  22. LIFE-22

    Stakeholders interviewed for the Joint Research Centre (JRC) study on digital product passport (DPP) content 'consistently indicated that substance-level concentration and location data are not reported'. They said such data are 'unavailable in a form that could be disclosed reliably and proportionately'. Chemical verification such as OEKO-TEX Standard 100 works 'on a binary pass/fail basis'. The concentration and location fields that a downstream sorter would need are not generated upstream.

    Reported practiceEUEuropean Commission, Joint Research Centre (JRC)

  23. LIFE-23

    Since 2021 the Waste Framework Directive (WFD) has required suppliers of articles to notify the European Chemicals Agency (ECHA) of the information they must give under REACH Article 33(1). In practice this means Candidate List substances of very high concern (SVHCs) above 0.1% weight by weight. ECHA must give 'waste treatment operators' access to the resulting SCIP database (Substances of Concern In articles as such or in complex objects (Products)). This is the one EU channel built to carry chemical information to the waste stage.

    LawEUEuropean Parliament and Council of the European Union (OJ L 150, 14.6.2018, p. 109)

  24. LIFE-24

    A 2023 evaluation for the Swedish Chemicals Agency (KemI) found that none of 10 interviewed recyclers used the SCIP database (Substances of Concern In articles as such or in complex objects (Products)) regularly: 4 were aware of it and 2 had used it once. The textile recycler Renewcell searched it for substances of very high concern (SVHCs), but the results 'were however not useful' because it could not filter by material. The legal access route exists, but it was not demonstrated to support a textile recycler's decision.

    Reported practiceSwedenSwedish Chemicals Agency (Kemikalieinspektionen), study by Ramboll

  25. LIFE-25

    The Commission's December 2025 'Environmental Omnibus' proposal, COM(2025) 986, would end suppliers' duty to notify the SCIP database (Substances of Concern In articles as such or in complex objects (Products)) and leave the European Chemicals Agency (ECHA) only to 'maintain' data already submitted. The proposed new wording of Article 9(2) drops the sentence that grants waste treatment operators access. On 23 October 2026 the European Parliament's file showed the proposal awaiting committee decision, with an indicative plenary date of 14 December 2026.

    ProposalEUEuropean Commission (via Publications Office Cellar)

  26. LIFE-26

    The Ecodesign for Sustainable Products Regulation (ESPR) requires product-specific delegated acts to make substances of concern traceable 'throughout the life cycle', including their name, 'location … within the product', concentration and information for recycling at end of life. That information must be on the product or reachable through a data carrier on it. 'Substance of concern' includes any substance that 'negatively affects the reuse and recycling of materials'. This is the first EU duty designed to carry finish chemistry to sorters. It applies only once a textiles delegated act is adopted, and none had been adopted at the snapshot.

    LawEUEuropean Parliament and Council of the European Union (OJ L series 2024/1781, 28.6.2024)

  27. LIFE-27

    The Joint Research Centre (JRC) study on digital product passport (DPP) content for apparel defines a use case, 'Data exchange to facilitate sorting', whose primary actor is the end-of-life textile sorter and whose required data are 'Product composition and purity' and 'Substances of concern'. In its proposed access levels, substances of concern are public, but their location in the product is limited to those with a 'Legitimate interest'. It warns that benefits depend on a data carrier 'available and permanently attached to garments'.

    ProposalEUEuropean Commission, Joint Research Centre (JRC)

  28. LIFE-28

    A draft Joint Research Centre (JRC) working document for the ESPR (Ecodesign for Sustainable Products Regulation) textiles study says that if REACH adopts a broad restriction on per- and polyfluoroalkyl substances (PFAS), including in textiles, PFAS 'would, most likely, qualify as' substances of concern under Article 2(27)(d), the category for substances that hinder reuse and recycling. That would bring PFAS into the tracking duty that could carry finish chemistry to sorters.

    ProposalEUJoint Research Centre, European Commission (Delre, A. et al.)

  29. LIFE-29

    France's PFAS law bans from 1 January 2026 the manufacture, import, export and placing on the market of consumer clothing containing per- and polyfluoroalkyl substances (PFAS). Its implementing decree defines placing on the market as supply to a third party 'pour la première fois' (for the first time). Reselling a used jacket within France therefore appears to fall outside the ban, but the separate ban on 'exportation' is not limited to first supply. Whether a sorter may export a used PFAS-treated jacket for re-use is not resolved by the text.

    LawFranceJournal officiel de la République française, reproduced by AIDA (INERIS)

  30. LIFE-30

    France's PFAS decree exempts from the clothing ban garments that contain at least 20% recycled material from post-consumer waste, but per- and polyfluoroalkyl substances (PFAS) are allowed only in that recycled fraction, in proportion to it. French law therefore expects that recycled textile feedstock may carry PFAS and lets recycled content bring some back into new garments.

    LawFranceJournal officiel de la République française, reproduced by AIDA (INERIS)

  31. LIFE-31

    The EU restriction on undecafluorohexanoic acid (PFHxA), its salts and related substances under REACH Annex XVII has applied since 10 October 2026 to clothing textiles for the general public, at 25 ppb (PFHxA and salts) or 1,000 ppb (related substances). It does not apply to articles 'placed on the market before 10 October 2026'. The entry says nothing about second-hand goods, waste or recycled material, and its recitals name 'outdoor clothing like rain jackets'.

    LawEUOfficial Journal of the European Union (via Publications Office Cellar)

  32. LIFE-32

    The EU restriction on nonylphenol ethoxylates (NPE) in textiles states expressly that it does not apply to 'second-hand textile articles' or to new articles made 'exclusively from recycled textiles' without NPE. The undecafluorohexanoic acid (PFHxA) restriction has no such clause. REACH defines placing on the market as any supply to a third party, not only first supply. Whether the PFHxA limits apply when a jacket first sold before 10 October 2026 is resold, or when recycled fibre goes into new clothing, is therefore not settled by the text.

    InterpretationEUEuropean Commission (OJ L 9, 14.1.2016)

  33. LIFE-33

    Once the 2025 Waste Framework Directive (WFD) amendment is transposed, each bale of used textiles shipped as fit for re-use must carry a record, fixed to the packaging, describing the items 'such as type of clothes, size, colour, gender, material composition', and naming the company that did the final sorting. A copy of every bale record must go with the consignment. This is a new information channel from sorter to re-use buyer. It describes bale contents at sorting granularity and has no chemical field.

    LawEUEuropean Parliament and Council of the European Union (OJ L series 2025/1892, 26.9.2025)

  34. LIFE-34

    The European Environment Agency (EEA) reports that EU exports of used textiles reached almost 1.7 million tonnes in 2019: 46% went to Africa and 41% to Asia. The 'fate of used textiles exported from the EU is highly uncertain'. The customs codes used, Combined Nomenclature (CN) 6309 and 6310, include 'no code for textile waste export', and 'classification does not necessarily describe the true state of what is exported'. Trade records do not record whether an item is waste, let alone its chemistry.

    Reported practiceEUEuropean Environment Agency

  35. LIFE-35

    France's environment ministry states that only about 35% of used textiles are collected, the rest going to household waste for incineration or landfill. It also states that the French scheme 'dépend de l'exportation' (depends on export) for both re-use and recycling of used textiles. A jacket that leaves France for re-use or recycling follows the scheme's normal route.

    Reported practiceFranceMinistère de la Transition écologique

The Global Framework on Chemicals35 claims

  1. GFC-01

    The Global Framework on Chemicals (GFC) was established at the fifth International Conference on Chemicals Management (ICCM5) in Bonn in September 2023 and adopted by resolution V/1 as a voluntary framework. None of its targets, including the one on information in products, creates a binding duty on any actor at any handover.

    LawInternationalUnited Nations Environment Programme (UNEP)

  2. GFC-02

    GFC Target B2 reads in full: 'By 2030, stakeholders make available, to the extent possible, reliable information on chemicals in materials and products throughout the value chain.' It names no information fields, no sender and no recipient, and it is qualified by 'to the extent possible'.

    LawInternationalUnited Nations Environment Programme (UNEP)

  3. GFC-03

    The GFC's scope covers the life cycle of chemicals 'including products and waste', and its Strategic Objective B aims for information that is 'accessible to all to enable informed decisions and actions'. On its own terms the framework therefore reaches the collector, sorter and recycler at H5 and H6, not only the factory.

    InterpretationInternationalUnited Nations Environment Programme (UNEP)

  4. GFC-04

    The GFC's hooks for finishing-mill workers at H1 are Target B6 (all governments implement the Globally Harmonized System of Classification and Labelling of Chemicals (GHS) by 2030), Target D7 (effective occupational health and safety 'throughout the supply chain') and paragraph 43, which asks industry to conduct due diligence so that International Labour Organization (ILO) health and safety standards apply 'throughout their value chains'.

    LawInternationalUnited Nations Environment Programme (UNEP)

  5. GFC-05

    The GFC treats skills as part of the work: Target B5 calls for training and public awareness programmes on chemical safety and safer alternatives by 2030, and paragraph 57 says 'All stakeholders should be equipped with the necessary skills, knowledge and resources to implement the Framework.' The framework itself does not assume that available information is usable information.

    LawInternationalUnited Nations Environment Programme (UNEP)

  6. GFC-06

    Alongside information, the GFC sets substitution and sector targets: Target D4 asks stakeholders to prioritise 'safer alternatives to harmful substances in products and mixtures, including in consumer products', and Target D6 calls for sector strategies that identify priority chemicals of concern and reduce 'their input along the value chain'. Information under Target B2 can inform these decisions but does not replace them.

    LawInternationalUnited Nations Environment Programme (UNEP)

  7. GFC-07

    The first session of the International Conference of the GFC (IC1) runs from 16 to 20 November 2026 at the Geneva International Conference Centre, hosted by Switzerland. Under agenda item 4(c) it may consider a draft resolution and proposed indicators for possible adoption.

    ProposalInternationalGlobal Framework on Chemicals secretariat (UNEP)

  8. GFC-08

    Pre-session document UNEP/GFC/IC.1/4 proposes three new indicators for Target B2, each with '[globally]' still in square brackets: countries with measures on harmonised digital products and materials information systems (B2.1), stakeholders using a harmonised standard, tool or platform to share information about chemicals in materials and products 'along the full value chain' (B2.2), and countries making harmonised data publicly accessible (B2.3). They are drafts for possible adoption at IC1, not adopted indicators.

    ProposalInternationalGlobal Framework on Chemicals secretariat (UNEP)

  9. GFC-09

    The secretariat's indicative overview for IC1 finds that practices to provide information on chemicals in products 'are emerging' but that there is 'still a lack of effective systems and mechanisms to collect and share this information along the value chain'. For Target B2 it counts 48 countries with measures on harmonised digital information systems and 38 countries and 211 companies using a harmonised standard or platform, and says the data do not allow a robust assessment of the reliability of the information shared.

    Reported practiceInternationalGlobal Framework on Chemicals secretariat (UNEP)

  10. GFC-10

    The IC1 document on issues of concern keeps 'chemicals in products' and 'managing perfluorinated chemicals and the transition to safer alternatives' on the list. It says that outside sectors with mandatory ingredient labelling, information exchange 'relies primarily on voluntary initiatives by individual sectors or companies', credits textile-sector systems and tools with progress, and says gaps remain in transparency, access to information and uptake.

    Reported practiceInternationalGlobal Framework on Chemicals secretariat (UNEP)

  11. GFC-11

    IC1 is asked to confirm industry sector programmes for four high-impact sectors, including textiles, and a thematic workstream on 'Transparency, traceability and disclosure along value chains (target B2)'. The draft workplan gives the textiles programme 2027 to 2028 for mapping initiatives, knowledge-sharing, raising awareness and piloting, convened by UNEP.

    ProposalInternationalGlobal Framework on Chemicals secretariat (UNEP)

  12. GFC-12

    IC1's programme includes sector exchanges on textiles covering 'data transparency, traceability and disclosure', a 'Fashion for the future' evening event on 16 November, and a high-level conversation titled 'Transparency without overload'. That title names the tension this piece examines: more data is not the same as usable information at each handover.

    InterpretationInternationalGlobal Framework on Chemicals secretariat (UNEP)

  13. GFC-13

    UNEP's 2011 Chemicals in Products (CiP) textile case study found that 'except for fiber content essentially no information system exists for transmitting data on what chemicals are contained in individual products.' Fibre content, which the sewn-in label still carries, was the one field it found travelling with the garment.

    Reported practiceInternationalUNEP Division of Technology, Industry and Economics (DTIE), Chemicals Branch

  14. GFC-14

    The same study separates restricted substance list (RSL) compliance from content disclosure: under an RSL programme the 'negative content' information (what is not in the product) 'does not accompany the product itself', whereas ecolabels attached to the finished article do carry it. A 'PFAS-free' statement is negative-content information in this sense.

    Reported practiceInternationalUNEP Division of Technology, Industry and Economics (DTIE), Chemicals Branch

  15. GFC-15

    UNEP's 2015 CiP guidance says information passed within supply chains should cover selected chemicals above a reporting threshold, include hazards and safe handling instructions where required, and 'should be supplied in the appropriate language for the recipients.'

    Voluntary standardInternationalUNEP for the Strategic Approach to International Chemicals Management (SAICM)

  16. GFC-16

    The CiP guidance states the structural break at H5 directly: 'Recyclers are outside the business-to-business information exchange because their connection to the data is interrupted by consumers.' It lists what waste managers need: hazardous chemicals and their location, how to prevent exposure, and product composition so materials can be sorted and processed.

    Voluntary standardInternationalUNEP for the Strategic Approach to International Chemicals Management (SAICM)

  17. GFC-17

    The CiP guidance defines relevant information by the recipient's decision ('the information that the recipient needs to take an informed purchase or chemicals-management decision or action') and requires it to be 'accessible, clear and understandable'. For disclosure outside the supply chain it asks for attention to language and technical background and says the date the information was produced 'would also be useful to provide'.

    Voluntary standardInternationalUNEP for the Strategic Approach to International Chemicals Management (SAICM)

  18. GFC-18

    UNEP's 2020 global stocktake of the textile value chain says large-scale textile recycling is 'hampered by a lack of traceability, insufficient or absent fibre labelling legislation and mixed materials', and will stay at low levels unless recyclers 'can be confident regarding the source, composition and chemical content of their feedstock'.

    Reported practiceInternationalUnited Nations Environment Programme (UNEP)

  19. GFC-19

    UN General Assembly resolution 92(I) of 7 December 1946 recommends that member states prevent use of the United Nations name, emblem and initials without the Secretary-General's authorisation, 'in particular for commercial purposes by means of trade marks or commercial labels'. Foresight is a commercial company, so the piece should carry no UN, UNEP or GFC logo and no wording that implies endorsement.

    LawInternationalUnited Nations General Assembly

  20. GFC-20

    UNECE Recommendation No. 46, from the UN Centre for Trade Facilitation and Electronic Business (UN/CEFACT), recommends that governments support 'harmonized collection and transmission of data for tracking and tracing materials, products, and processes across an entire value chain' in garments and footwear. It was agreed at UN/CEFACT's twenty-seventh session in April 2021 and is a recommendation to governments, not a duty on companies.

    Voluntary standardInternationalUN Economic Commission for Europe (UNECE), UN/CEFACT

  21. GFC-21

    Recommendation No. 46 identifies the post-consumer stage as the hardest: closing the circle after sale is 'particularly challenging' because of missing collection infrastructure, 'missing or inaccurate information about the composition of goods' and technical barriers to post-consumer traceability.

    Reported practiceInternationalUN Economic Commission for Europe (UNECE), UN/CEFACT

  22. GFC-22

    Recommendation No. 46 asks governments to define 'the minimum data that need to be collected in order to show due diligence and transparency in support of claims regarding the origin, composition and other characteristics' of products. A 'PFAS-free' or 'fluorine-free' finish claim is one such composition claim, and no minimum data set for it is defined in the recommendation.

    Voluntary standardInternationalUN Economic Commission for Europe (UNECE), UN/CEFACT

  23. GFC-23

    UN/CEFACT records the capability barriers for smaller actors: traceability technologies 'may be difficult due to geographical and language barriers as well as costs', and the most important impediments are 'often cost and access, followed by language and a lack of available training'. Its guidelines say tool design should consider 'the language of users'.

    Reported practiceInternationalUN Economic Commission for Europe (UNECE), UN/CEFACT

  24. GFC-24

    Electronics shows a mature model: IEC 62474 sets the procedure, content and form of material declarations passed from suppliers to downstream manufacturers, in two types (declaration for compliance and composition declaration). It excludes process chemicals, so even a mature product declaration describes what is in the product, not what was used to make it.

    Voluntary standardInternationalInternational Electrotechnical Commission (IEC)

  25. GFC-25

    The IPC-175x family from IPC, the electronics industry association, 'establishes a standard reporting format for data exchange between supply chain participants'. IPC-1752A, named in the brief, has been followed by IPC-1752B (July 2020), built to match the EU SCIP database for Substances of Concern In articles as such or in complex objects (Products), and by IPC-1752C (June 2026), the current version.

    Voluntary standardInternationalIPC (Association Connecting Electronics Industries)

  26. GFC-26

    Where an EU Ecodesign for Sustainable Products Regulation (ESPR) delegated act sets information requirements on substances of concern, they must make those substances trackable through the life cycle and include at least: the substance name or code, its location in the product, its concentration (or maximum or range) at product, component or spare-part level, instructions for safe use, and end-of-life information. That covers four of this piece's five fields; the list does not include the type or date of the underlying evidence.

    LawEUEuropean Parliament and Council of the European Union

  27. GFC-27

    ESPR requires substances-of-concern information to be 'given either on the product or be accessible through a data carrier included on the product', in a language easily understood by customers as decided by the member state. For a jacket that points to the label or a carrier attached to it, but the regulation does not by itself ensure that a consumer or sorter can interpret a chemical name.

    LawEUEuropean Parliament and Council of the European Union

  28. GFC-28

    ESPR lists who should have free, easy access to the digital product passport (DPP), including recyclers, professional repairers, refurbishers, trade unions, civil society organisations and authorities, 'based on their respective access rights set out in the applicable delegated act'. Which actor sees which data is left to each product-group delegated act.

    LawEUEuropean Parliament and Council of the European Union

  29. GFC-29

    The Commission's first ESPR working plan (16 April 2025) ranks textiles and apparel first among new product groups, with 2027 as the indicative timeline for adoption, and says information requirements 'will work in synergy with the Textile Labelling Regulation, currently under review'. At the snapshot a textile DPP is planned, not in force.

    ProposalEUEuropean Commission (via Publications Office Cellar)

  30. GFC-30

    OEKO-TEX ECO PASSPORT lets producers of textile chemicals prove their products 'can be used in an ecologically sustainable production'. The supplier discloses the formulation to OEKO-TEX or its testing institute, which holds it 'strictly confidential' and never passes it to third parties, so the finishing mill at H1 receives a certificate, not the formulation.

    Voluntary standardInternationalOEKO-TEX AG

  31. GFC-31

    The ZDHC Gateway's Chemical Module calls itself 'the world’s first verified database of safer chemistry for the apparel and footwear industry'. It generates a ChemCheck Report, 'an individual product passport', for chemical products conformant with the ZDHC Manufacturing Restricted Substances List (MRSL), and InCheck reports show the MRSL conformance of a facility's chemical inventory.

    Voluntary standardInternationalZero Discharge of Hazardous Chemicals (ZDHC) Foundation

  32. GFC-32

    ILO Chemicals Convention No. 170 (1990) requires hazardous chemicals to be labelled 'in a way easily understandable to the workers' and safety data sheets with identity, hazards, precautions and emergency procedures to be provided to employers. It does not apply to articles that will not expose workers under normal or reasonably foreseeable use, so it reaches the mixture at H1 but generally not the fabric roll at H2.

    LawInternationalInternational Labour Organization (ILO), NORMLEX

  33. GFC-33

    Under Convention No. 170, workers and their representatives have the right to information on the identity of chemicals used at work, their hazards and precautions, label information and safety data sheets, and employers must instruct workers how to obtain and use that information. An employer may protect a mixture ingredient's specific identity from competitors in a manner approved by the competent authority.

    LawInternationalInternational Labour Organization (ILO), NORMLEX

  34. GFC-34

    Convention No. 170 has 24 ratifications. Neither Viet Nam nor France is among them; China ratified in 1995. The GFC's proposed indicator D7.1 would count ratifications of up-to-date ILO conventions on chemical risks.

    LawInternationalInternational Labour Organization (ILO), NORMLEX

  35. GFC-35

    ILO Recommendation No. 177 says workers should receive information on classification, labelling and safety data sheets 'in forms and languages which they easily understand', plus workplace-specific instruction and training. It is the clearest international statement that worker access depends on language and training, not only on a document existing.

    LawInternationalInternational Labour Organization (ILO)

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    Văn phòng Quốc hội (Office of the National Assembly), Công báo Nos 1169+1170 and 1171+1172 · 16 September 2024

    Cited by: VN-09
  54. Luật Hóa chất số 69/2025/QH15 (Law on Chemicals), consolidated text 35/VBHN-VPQH (opens in a new tab)

    Văn phòng Quốc hội (Office of the National Assembly), via Government e-documents portal · 14 June 2025

    Cited by: VN-01VN-02VN-07
  55. HS Nomenclature 2022 edition, Chapter 38 (opens in a new tab)

    World Customs Organization (WCO) · 1 January 2022

    Cited by: VN-06

Standards and programmes19 sources

  1. Danh sách các chất bị hạn chế, RSL của AFIRM, năm 2026 (AFIRM RSL 2026, Vietnamese edition) (opens in a new tab)

    AFIRM Group · 2 March 2026

    Cited by: VN-25
  2. Phaseout Guidance for Per- & Polyfluoroalkyl Substances (PFAS), Version 02, 2025 (opens in a new tab)

    AFIRM Group · 31 October 2025

    Cited by: VN-24VN-32VN-33
  3. EVS-EN 17681-1:2025 Textiles and textile products - Per- and polyfluoroalkyl substances (PFAS) - Part 1: Analysis of an alkaline extract using liquid chromatography and tandem mass spectrometry (opens in a new tab)

    European Committee for Standardization (CEN), via the Estonian Centre for Standardisation (EVS) catalogue · 15 May 2025

    Cited by: TECH-18
  4. EVS-EN 17681-2:2022 Textiles and textile products - Organic fluorine - Part 2: Determination of volatile compounds by extraction method using gas chromatography (opens in a new tab)

    European Committee for Standardization (CEN), via the Estonian Centre for Standardisation (EVS) catalogue · 17 October 2022

    Cited by: TECH-19
  5. Materials Declaration Data Exchange Standards Homepage (opens in a new tab)

    IPC (Association Connecting Electronics Industries) · June 2026

    Cited by: GFC-25
  6. IEC 62474:2018+AMD1:2020 CSV Material declaration for products of and for the electrotechnical industry (opens in a new tab)

    International Electrotechnical Commission (IEC) · 7 December 2020

    Cited by: GFC-24
  7. OEKO-TEX® RSL (Restricted Substances List) (opens in a new tab)

    OEKO-TEX · 1 September 2026

    Cited by: VN-30
  8. OEKO-TEX® STANDARD 100, Edition 01.2026 (opens in a new tab)

    OEKO-TEX (OEKO-TEX Service GmbH) · 3 March 2026

    Cited by: VN-31
  9. OEKO-TEX® ECO PASSPORT Standard, Edition 03.2026 (opens in a new tab)

    OEKO-TEX AG · 21 August 2026

    Cited by: VN-23GFC-30
  10. Recommendation No. 46: Enhancing Traceability and Transparency of Sustainable Value Chains in the Garment and Footwear Sector (opens in a new tab)

    UN Economic Commission for Europe (UNECE), UN/CEFACT · 8 February 2021

    Cited by: GFC-20GFC-21GFC-22GFC-23
  11. The Chemicals in Products Programme: Guidance for stakeholders on exchanging chemicals in products information (opens in a new tab)

    UNEP for the Strategic Approach to International Chemicals Management (SAICM) · October 2015

    Cited by: GFC-15GFC-16GFC-17
  12. Boosting Transparency: Introducing QR Codes on the ZDHC Gateway (opens in a new tab)

    ZDHC Foundation · 30 October 2025

    Cited by: VN-22
  13. ChemCheck - Gateway Reports (opens in a new tab)

    ZDHC Foundation

    Cited by: VN-21
  14. Generate a ZDHC Performance InCheck Report (Suppliers Roadmap to Zero, Input, InCheck Reporting) (opens in a new tab)

    ZDHC Foundation · 6 August 2026

    Cited by: VN-26
  15. ZDHC Position in Progress on PFAS (opens in a new tab)

    ZDHC Foundation · 26 June 2026

    Cited by: VN-27
  16. ZDHC Manufacturing Restricted Substances List (ZDHC MRSL) V3.1 (opens in a new tab)

    ZDHC Foundation (copy hosted by Lindex Group) · 27 August 2026

    Cited by: VN-19VN-20
  17. ZDHC Gateway (opens in a new tab)

    Zero Discharge of Hazardous Chemicals (ZDHC) Foundation

    Cited by: GFC-31
  18. bluepass Labels & Claims Guide, Version 4.0 (opens in a new tab)

    bluesign technologies ag (An SGS Company) · 1 July 2026

    Cited by: VN-29
  19. bluesign System Substances List (BSSL), version 17.0 (opens in a new tab)

    bluesign technologies ag (an SGS company) · 1 July 2026

    Cited by: VN-28

Studies of practice13 sources

  1. Kledinglabels: nauwkeurig of niet? (English edition: Labels: Accurate or not?) (opens in a new tab)

    Circle Economy, for the Netherlands Ministry of Infrastructure and Water Management (published as parliamentary annex blg-930139) · 15 November 2019

    Cited by: TECH-29TECH-30TECH-31
  2. Practical, market-driven End-of-Waste criteria are key to textile circularity (opens in a new tab)

    EuRIC (European Recycling Industries' Confederation) · 29 April 2025

    Cited by: LIFE-20
  3. EU exports of used textiles in Europe's circular economy (Briefing 01/2023) (opens in a new tab)

    European Environment Agency · 27 February 2023

    Cited by: LIFE-34
  4. Accelerating action: new and existing issues of concern (note by the secretariat) (opens in a new tab)

    Global Framework on Chemicals secretariat (UNEP) · 25 August 2026

    Cited by: GFC-10
  5. Tracking progress: indicative overview of progress under the Global Framework on Chemicals (note by the secretariat) (opens in a new tab)

    Global Framework on Chemicals secretariat (UNEP) · 26 August 2026

    Cited by: GFC-09
  6. Fate and Composition of Textile Waste from Italy, the Czech Republic and Romania (JRC141441) (opens in a new tab)

    Joint Research Centre, European Commission (External Study report; Bakowska, O. et al.; Huygens, D., editor) · 2025

    Cited by: LIFE-11LIFE-15LIFE-16LIFE-17LIFE-18
  7. Produits textiles (TLC) (opens in a new tab)

    Ministère de la Transition écologique · 31 August 2026

    Cited by: LIFE-35
  8. Les indicateurs clés de performance de la Filière Textile d'habillement, Linge de maison et Chaussures, année 2025 (opens in a new tab)

    Refashion · 2026

    Cited by: LIFE-09
  9. Synthèse: Bilan environnemental de la filière de traitement des TLC ménagers usagés - 2025 (opens in a new tab)

    Refashion · July 2026

    Cited by: LIFE-14
  10. Indicators for chemical information transfer in the textile value chain (SAICM/IP.4/INF/36, annex; TemaNord 2022:549) (opens in a new tab)

    SAICM secretariat; study funded by the Nordic Council of Ministers, submitted by Sweden · 30 December 2022

    Cited by: VN-34
  11. Evaluation of the SCIP database: Experiences of use by Swedish waste treatment operators (PM 1/23) (opens in a new tab)

    Swedish Chemicals Agency (Kemikalieinspektionen), study by Ramboll · 2023

    Cited by: LIFE-19LIFE-24
  12. The Chemicals in Products Project: Case Study of the Textiles Sector (opens in a new tab)

    UNEP Division of Technology, Industry and Economics (DTIE), Chemicals Branch · January 2011

    Cited by: GFC-13GFC-14
  13. Sustainability and Circularity in the Textile Value Chain: Global Stocktaking (opens in a new tab)

    United Nations Environment Programme (UNEP) · 2020

    Cited by: GFC-18

Research17 sources

  1. Development of a certified reference material for per- and polyfluoroalkyl substances (PFAS) in textiles (opens in a new tab)

    Analytical and Bioanalytical Chemistry (Springer) · 9 September 2025

    Cited by: TECH-27
  2. The hidden fluorine: a critical review of analytical methods for unmasking PFAS and closing fluorine mass balance in environmental samples (opens in a new tab)

    Analytical and Bioanalytical Chemistry (Springer) · 5 April 2026

    Cited by: TECH-20TECH-21
  3. Beyond the watchlist: How the TOP assay exposes untargeted PFASs for current and future regulations in consumer products (opens in a new tab)

    Chemosphere (Elsevier) · 31 January 2026

    Cited by: TECH-25
  4. Systematic determination of perfluoroalkyl and polyfluoroalkyl substances (PFASs) in outdoor jackets (opens in a new tab)

    Chemosphere (Elsevier) · 1 July 2016

    Cited by: TECH-26
  5. Alternatives to perfluoroalkyl and polyfluoroalkyl substances (PFAS) in textiles (Survey of chemical substances in consumer products No. 137) (opens in a new tab)

    Danish Environmental Protection Agency · 1 May 2015

    Cited by: TECH-05TECH-09TECH-11TECH-12
  6. Properties, performance and associated hazards of state-of-the-art durable water repellent (DWR) chemistry for textile finishing (opens in a new tab)

    Environment International (Elsevier) · 16 March 2016

    Cited by: TECH-10
  7. Closing the Mass Balance on Fluorine on Papers and Textiles (opens in a new tab)

    Environmental Science & Technology (American Chemical Society) · 15 July 2017

    Cited by: TECH-22
  8. Disposition of Fluorine on New Firefighter Turnout Gear (opens in a new tab)

    Environmental Science & Technology (American Chemical Society) · 27 December 2021

    Cited by: TECH-23
  9. Fate of Per- and Polyfluoroalkyl Substances from Durable Water-Repellent Clothing during Use (opens in a new tab)

    Environmental Science & Technology (American Chemical Society) · 11 April 2022

    Cited by: TECH-07TECH-08
  10. How Well Do Product Labels Indicate the Presence of PFAS in Consumer Items Used by Children and Adolescents? (opens in a new tab)

    Environmental Science & Technology (American Chemical Society) · 4 May 2022

    Cited by: TECH-24
  11. PFAS in textiles in Europe's circular economy (opens in a new tab)

    European Environment Agency · 17 September 2024

    Cited by: TECH-34TECH-35LIFE-21
  12. EU trade since 1988 by HS2-4-6 and CN8 (DS-045409) (opens in a new tab)

    Eurostat (Comext) · 16 October 2026

    Cited by: VN-35
  13. Textile Recognition and Sorting for Recycling at an Automated Line Using Near Infrared Spectroscopy (opens in a new tab)

    Recycling (MDPI) · 8 February 2021

    Cited by: TECH-32
  14. State of the art of automated sorting and disassembly technologies for textiles and footwear in Europe (opens in a new tab)

    Refashion · July 2026

    Cited by: LIFE-13
  15. Occurrence and use of highly fluorinated substances and alternatives (Report 7/15) (opens in a new tab)

    Swedish Chemicals Agency (KEMI) · 1 January 2015

    Cited by: TECH-01TECH-04TECH-06
  16. Unlocking Value: Compositional Analysis of Post-Consumer Textile Waste in the Residual Fraction in Catalonia and Its Recycling Potential (opens in a new tab)

    Textiles (MDPI) · 30 December 2025

    Cited by: TECH-33
  17. Liquid repellent finishing in outdoor apparel: chemical management, environmental concerns and performance testing (PhD thesis) (opens in a new tab)

    University of Leeds (White Rose eTheses Online) · 1 April 2019

    Cited by: TECH-03TECH-28

Method

How we built the case, what a claim needs before we publish it, and what we could not see.

The case

One water-resistant jacket on an illustrative pathway, not a traced shipment. A chemical supplier formulates the finishing agent. A mill in Viet Nam finishes and laminates the fabric, and a factory there sews the jacket. A brand sells it in France. The owner wears it, then hands it to a collector and sorter, who sends it on to re-use or recycling.

At each of the six handovers we named the decision the recipient has to make, and followed five things to know: component identity, chemical identity or group, concentration or test result, hazard and handling, and evidence type and date.

Four lenses

Each thing to know at each handover is assessed four times. No lens scores another: a law can require what no recipient can reach, and a record can arrive that answers nothing.

Recipient access

Can the next person get it?

Demonstrated
The recipient receives it by default with the product or material, for example printed on the label.
Conditional or restricted
The recipient can obtain it only on request, by contract, by membership or above a threshold.
Not demonstrated
We found no route by which this recipient receives it. Not demonstrated does not mean it does not exist.

What requires it to pass?

Applicable duty
A law in force at the snapshot requires this information to reach this recipient, under the conditions stated.
Future duty
Adopted law that will require it, from a stated date. Not yet in force at the snapshot.
Proposal
Proposed by a public authority, not adopted at the snapshot.
Voluntary provision
Required by a voluntary standard, industry programme or contract, not by law.
Applicability unresolved
A duty may apply, but its applicability to this case depends on facts or interpretation we could not settle.
No duty identified
We found no legal duty or voluntary provision that requires this information at this handover.
Decision usefulness

Does it answer their question?

Supports the named decision
When received, it supports the recipient's named decision.
Insufficient for that decision
Even when received, it does not answer the recipient's named decision on its own.
Not assessed
This field does not bear on the decision at this handover.
Case evidence

What can this investigation show?

Product-specific record
A record for this specific product. This illustrative pathway has none.
Documented general practice
Documented general practice from a primary source: a programme's own rules, an agency study or a peer-reviewed paper.
Illustrative assumption
A scenario assumption we chose for this illustrative pathway, and say so.
Not established
We could not establish this from public evidence. That is not evidence that it does not happen.

What a claim needs

A claim is published only with its source, a verbatim passage with its pinpoint, and the date we checked it. Passages in French, Vietnamese and Dutch appear in the original, with our English translation. Each record also says where the claim stops, and gives the strongest evidence against it when we found any.

We ranked sources in this order and quoted the highest we could reach. Trade press and law-firm notes helped us find primary texts. None is cited, though the expected date of the EU’s textiles act rests on them, as its claim says.

  1. Final legal texts, official implementation material and agency records.
  2. Records for this specific product. This illustrative pathway has none.
  3. Original scientific studies and documented process information.
  4. Standards and industry programmes, for their own requirements, marked as voluntary.
  5. Reported practice, attributed by role.

Law in force, law that applies later, proposals, voluntary programmes and company commitments stay apart throughout. The minimum package is Foresight’s proposal, and says so.

Where we could not look

Private records
Supplier declarations, test reports, contracts and brand systems are not public. When we found no route to a recipient, the cell says not demonstrated. A route may still exist out of sight.
Official sites
Légifrance and EUR-Lex refused automated reading. We read French law in the consolidations that INERIS, France’s national institute for industrial environment and risks, publishes on AIDA, and EU law at the EU Publications Office. Viet Nam’s Decree 26/2026 came from a secondary host, checked against the official scan for every article quoted.
Other blocked sources
The European Chemicals Agency (ECHA), the OECD, UNECE and some journal publishers also refused. Where another primary text carried the same words, we cited that, such as EU law for the OECD’s definition of PFAS. Otherwise the question stays open.
Copies and abstracts
Seven scientific studies were read in abstract only, because the full text was paywalled or blocked. UN Environment Programme (UNEP) and ILO pages came from Wayback Machine captures when the live sites refused. Five passages from JRC reports came from a mirror with the same report number and DOI, and ZDHC’s restricted substances list from a copy a brand hosts. Each claim’s record says how it was read.
Scope
One jacket on one illustrative pathway, through Viet Nam and France, with the EU and international rules that reach it. We did not test a jacket or trace a shipment.

What could change

Dated changes after our snapshot of 23 October 2026. Any of them could move a cell.

  1. Due October 2026

    ZDHC’s promised PFAS update, including how PFAS information should be communicated. It was due in October 2026 and not published on 23 October. Evidence: VN-27

  2. 16 to 20 November 2026

    The first International Conference of the Global Framework on Chemicals (GFC) meets in Geneva. Watch whether it adopts the three indicators for Target B2, and whether “globally” keeps its square brackets. Evidence: GFC-07GFC-08

  3. 14 December 2026

    The European Parliament’s indicative plenary vote on the Environmental Omnibus, which would end suppliers’ duty to notify SCIP and drop waste operators’ access to it. Until the change is adopted and in force, the duty applies. Evidence: LAW-15LIFE-25

  4. About 16 December 2026

    The Stockholm Convention listing of long-chain perfluorocarboxylic acids (PFCAs) should enter into force, including for Viet Nam on the current record. Viet Nam’s chemical lists do not yet name them. Evidence: VN-12

  5. 31 December 2026

    France’s sell-off window closes for PFAS clothing made before 1 January 2026. From 1 January 2027, none of it may be sold or exported, whatever its date of manufacture. Evidence: LAW-24LIFE-29

  6. Draft

    Viet Nam’s draft decree amending Decree 26/2026, consulted on in August 2026. It keeps the import declaration’s exemption for mixtures outside chapters 28 and 29. Evidence: VN-05

  7. Overdue

    The EU’s revision of the Textile Labelling Regulation, which would add specifications for physical and digital labels. It was planned for the second quarter of 2026. Evidence: LAW-07

  8. Indicative 2027

    The textiles delegated act under the EU’s Ecodesign for Sustainable Products Regulation (ESPR). It would be the first EU duty designed to carry a finish’s chemistry, on or through the product, to sorters. Evidence: LAW-32LIFE-26

How the pictures were made

The photographs were generated with image models from Google and OpenAI, from prompts written for this piece, then cropped and graded. The layered shell is a 3D model rendered in Blender. They illustrate the case and carry no evidence. The score and the assessments draw on the same dataset as the claims.

Changes

  1. First published, with evidence checked on 23 October 2026.

Know where PFAS sitsin what you make.

See how Foresight checks each material against each market’s PFAS rules, finds what your supplier records leave out, and links every verdict to its source.

Claim

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