Version 2 of the baby-wipes standard adds antimony, and it sets the ceiling by binding a government floor rather than inventing one. The limit is total antimony below 30 mg/kg, entered as 30000 µg/kg, in the finished product, measured directly on a wipe and included in pass/fail.
Abstract
Version 2 of the Heavy Metal Tested and Certified standard for baby wipes adds antimony to the panel and holds it below 30 mg/kg, entered as 30000 µg/kg, on the total content of the finished product. The number is not one HMTc originated. It is the antimony floor in the EU Ecolabel for absorbent hygiene products, Commission Decision (EU) 2023/1809, Annex I criterion 7.3.8, which requires antimony to be present in the final product at less than 30 mg/kg [1]. That Ecolabel is voluntary, and the cell says so plainly rather than dressing a voluntary floor as a mandate. Because the criterion is written on total content in the final product, the limit is measured directly on a wipe, and the cell is included in pass/fail. One government figure sits close enough to invite confusion, and it is kept separate on purpose: Korea's MFDS Notice No. 2026-23, revised 24 March 2026 and first enacted as Notice No. 2018-19 on 21 March 2018, sets antimony for children's disposable diapers at 60 mg/kg or less by migration, applied separately to the inner lining and the waterproof layer [2]. Migration and total content are not the same measurement, so the Korea diaper figure is precedent that antimony belongs on a baby-product panel rather than the baby-wipes number itself.
Version 2 adds antimony and changes nothing else about how the standard is published. No products had been certified under version 1.0. The version-1.0 DOI stays live as the previous version, 10.83138/hmtc.std.2.baby-wipes, dated 2026-08-17 [3], and version 2 deposits no new DOI. Every other analyte cell keeps the basis it already carried. An evidence note dated 2 October 2026 brings the literature current with the Heavy Metal Index syntheses on baby wipes and on antimony in baby products, rebuilt after the 26 September 2026 ingest. That note does not change the ceiling. What follows sets out what version 2 changes, where the number comes from, the evidence it answers to, and what the mark does and does not claim.
What version 2 sets, and what it leaves alone
Version 2 adds antimony and does nothing to the version-1.0 DOI. No products had been certified under version 1.0, so nothing certified is disturbed. That DOI is the previous version, not a withdrawn one, and it stays resolvable at https://doi.org/10.83138/hmtc.std.2.baby-wipes [3]. DataCite records it as version 1.0, publication year 2026, registered 19 September 2026, with no separate print date and no volume or pages, and the house version history dates edition 1.0 to 2026-08-17. Version 2 does not replace that DOI with a new one, and it deposits none of its own. The current text of the standard is the baby wipes standard, where the antimony cell reads 30000 µg/kg, is included in pass/fail alongside the other analytes, and carries its source comparator, strictly less than 30 mg/kg, in the cell provenance.
Where the number comes from
The design rule is the one the rest of the program follows: adopt the applicable government figure on the product’s own basis, and invent nothing. For antimony in a wipe, the figure written on total content in the final product of an absorbent hygiene product is the EU Ecolabel one, so the cell is entered at 30000 µg/kg and included in pass/fail. Numerically lower impurity figures exist for cosmetics in general. They are not this cell, for the reasons in the table.
Commission Decision (EU) 2023/1809 is the EU Ecolabel for absorbent hygiene products, and its Annex I criterion 7.3.8 governs impurities in the final product: the listed chemicals shall not be present in the final product at a concentration higher than Table 9, where antimony is set at < 30 mg/kg [1]. The instrument text is unchanged. Table 9 is content in the final product, not migration. The Ecolabel is voluntary, and the cell discloses that rather than implying a mandate. It is the government floor for this analyte. Because the decision’s own assessment accepts analysis of the final product, the limit is measured directly on a wipe. Thirty mg/kg is 30000 µg/kg, the source comparator is strictly less than 30 mg/kg, and because the compiled record carries no comparator field, that inequality is written into the cell provenance so nothing is lost.
The antimony cell sits on a different basis from the analytes already published, and that is deliberate. Those cells are written on the total content of the impregnating cosmetic liquid, in µg/kg of that liquid as sold; the antimony cell is written on total content in the finished product, because that is the basis the EU criterion uses and the one that can be checked directly on a wipe.
The one government figure that has to be held apart is Korea’s. MFDS Notice No. 2026-23 sets antimony for children’s disposable diapers at 60 mg/kg or less by migration, applied separately to the inner lining and the waterproof layer [2]. That is a migration test, where this ceiling is a total-content test, and the two measure different quantities. The Korea figure is real precedent that a government limits antimony in a baby product; it is not, and is not used as, the baby-wipes number.
| Basis | Figure, as printed | Status |
|---|---|---|
| EU Ecolabel absorbent hygiene products, Decision (EU) 2023/1809, Annex I criterion 7.3.8 | less than 30 mg/kg total content in the final product | Selected. Voluntary. Entered as 30000 µg/kg. Strictly less than. |
| Korea MFDS Notice No. 2026-23, children’s disposable diapers | Sb 60 mg/kg or less by migration, inner lining and waterproof layer, each | Government precedent in baby products. Migration, not total. Not the ceiling. |
| Health Canada guidance, heavy-metal impurities in cosmetics, section 4 | antimony above 5 ppm treated as technically avoidable | Not selected. Guidance, not a regulation. The indexed text does not name wipes [13]. |
| Korea cosmetic safety standard, Article 6(2) | antimony at or below 10 µg/g | Not selected. No wet-wipe-specific figure for the metal [14]. |
| BVL 2017 orientation values, cosmetics in general | 0.5 mg/kg antimony | Not selected. Orientation value. The monitoring set was decorative cosmetics, baby powder, and toothpaste, not wipes [15]. |
| EU Ecolabel textiles, Decision 2014/350/EU, criterion 7(a), polyester fibres | shall not exceed 260 ppm | Not selected. Recycled PET bottles are derogated. |
| EU Ecolabel textiles, Decision 2014/350/EU, criterion 13, Appendix 1 (iv), acid sweat | 30,0 mg/kg extractable antimony | Not selected. Extraction EN ISO 105-E04:2013. |
| United States, diapers, wipes, or textiles | no federal limit for antimony | Not a number. |
| 40 CFR 141.62(b)(11), drinking-water MCL | 0.006 mg/L | Orientation only. |
| Directive (EU) 2020/2184, Annex I, Part B | 10 μg/L parametric value | Orientation only. |
The evidence the number answers to
The ceiling is the EU Ecolabel figure, 30000 µg/kg. Everything in this section is the evidence that put antimony on the panel in the first place, and none of it is the ceiling. These measurements establish that antimony occurs in baby-wipe materials; they are not used to set the limit.
Washington State Department of Ecology Publication 14-04-014, revised June 2021, measured total elemental antimony in baby-wipe components and in moist baby-wipes packaging [5]. Components were prioritised by X-ray fluorescence and confirmed by ICP-MS, so the design is an upper-tail screen of products bought for that study rather than a random sample of the category. Across that screen, antimony was detected in 57 percent of 150 children’s-product components. The report’s frame of reference is the Washington Children’s Safe Products Act threshold of 100 ppm, which is a manufacturer reporting trigger, not a health-based maximum and not this ceiling. The analyte is total elemental antimony, and the report does not speciate Sb(III) from Sb(V). The same three wipe rows print lead at 0.4, 0.8, and 1.4 ppm and total chromium at 0.5 to 0.6 ppm. Those prints are not scored against the lead or chromium cells here: the preparation is a screened component, and the report does not say the component was the whole wipe. One breast-wipes package is a separate article, at 38.0 ppm antimony, and it is not a baby-wipe sheet. These are occurrence figures, and occurrence does not set a certification cell.
Choi, Song, and Kim 2016 digested approximately 0.2 g and diluted with 25 mL of water, not made up to 25 mL [6]. Table 5 prints an antimony range for wet-wipe nonwovens but neither sheet figure in mg/kg, and the conversion to a sheet estimate is uncertain because the methods do not state a made-up final volume. Treating the final volume as 25 mL gives µg/L × 0.125, from mg/kg ≈ (µg/L × 0.025 L / 0.0002 kg) / 1,000, or about 23.48 to 2,444.79 mg/kg; the division by 1,000 is required because the quotient of those inputs is micrograms per kilogram. Treating the digest as 8 mL of acid plus 25 mL of water gives µg/L × 0.165, and a higher top of about 3,227.13 mg/kg. The paper prints neither figure, and neither reading is the certification ceiling. The authors’ attribution of the result to an antimony trioxide or antimony glycolate catalyst is their inference, and it does not hold cleanly for wipes: the highest sheet in Table 5 is labelled rayon only, and several polyester-labelled sheets were not detected, so the polyester-catalyst explanation is a hypothesis here rather than a finding.
The China Association for Quality Promotion of Consumer Products Safety page dated 2 April 2026 reports a detection count for total antimony in online baby wipes [7]. The sample-by-sample annex is an image. Preferred reads of total antimony, taken as micrograms per liter, are numeric in 20 of 21 columns. The stable low read is 15.02 µg/L and the stable high preferred read is 450.45 µg/L. A second full-cell pass of the same image also produced 490.40 µg/L where the preferred read is 450.45, and 399.43 µg/L where the preferred read is 355.43. This briefing keeps the preferred range and does not adopt the second pass. The preparation that produced the per-liter figure is not described, so the unit is not a sheet concentration in milligrams per kilogram, and it is not a candidate limit. Brands named on that page are not repeated here.
Göçer’s 2025 master’s thesis is the dataset that separates the three objects in a wipe: the liquid squeezed from the sheet, the digested fiber, and the digested packaging [12]. Solution antimony in one coded product is 695.40 ppb, which the English abstract rounds to 695.4 ppb. Fiber antimony is printed as 565.46 ppb and 537.86 ppb, and a further sentence and section 4.1 print 476.69 ppb. All three fiber figures are in the thesis, and 476.69 is lower than the other two. Packaging antimony is printed at 0.03 and 0.04 ppb, at or below the quantification limit of 0.10 ppb. Those antimony results of several hundred ppb sit above the stated calibration top of 50 ppb. The methods digested an approximate 0.2 g and then added 10 mL of water, and they do not print a made-up final volume, so no sheet concentration is calculated. Product codes are kept. Brand names are not repeated. This split shows that lotion, fiber, and packaging are different measurements. It is not a candidate limit.
The Heavy Metal Index syntheses that carry this record are the baby-wipes synthesis and the antimony-in-baby-products synthesis [16][17]. Both state the same boundary this briefing uses. A concentration in a wipe is not a dose, because a ppm in a sheet is not a microgram on the skin and a microgram on the skin is not a microgram absorbed. Neither synthesis ranks products, and neither sets a certification number. The ceiling on this side remains Table 9.
Biver, Turner, and Filella 2021 measured artificial-sweat release from polyester textiles, not from wipes [8]. The extract row is a simulant result under ISO 105-E04, which is neither absorption nor a wipe-sheet total.
| Source | Figure, as printed or as derived | What the figure is |
|---|---|---|
| WA Ecology 14-04-014, revised June 2021, three baby-wipe components | 40.6, 61.3, and 70.6 ppm | Total elemental antimony. Upper-tail screen, not a random sample. Not a candidate limit. |
| WA Ecology 14-04-014, revised June 2021, moist baby-wipes packaging | 95.8 ppm | Total elemental antimony. Not a candidate limit. |
| WA Ecology 14-04-014, revised June 2021, one breast-wipes package | 38.0 ppm | Package, not a baby-wipe sheet. Not a candidate limit. |
| Choi, Song, and Kim 2016, Table 5, 12 of 24 wet-wipe nonwovens | 187.86 ± 5.24 to 19,558.35 ± 3,537.3 µg/L | Printed concentration. Not a sheet concentration in mg/kg. Not a candidate limit. |
| Choi, Song, and Kim 2016, derived reading, final volume treated as 25 mL | about 23.48 to 2,444.79 mg/kg | Not printed. µg/L × 0.125, from mg/kg ≈ (µg/L × 0.025 L / 0.0002 kg) / 1,000. The methods diluted approximately 0.2 g with 25 mL of water, not made up to 25 mL. Not a candidate limit. |
| Choi, Song, and Kim 2016, derived reading, 8 mL of acid plus 25 mL of water | higher top of about 3,227.13 mg/kg | Not printed. µg/L × 0.165. The paper prints neither sheet figure. Not a candidate limit. |
| China Association for Quality Promotion of Consumer Products Safety, 2 April 2026 | preferred reads numeric in 20 of 21; 15.02 to 450.45 µg/L | Annex image. Preferred range kept. A second pass differed on wrapped cells and is not adopted. Preparation not described. Not a sheet concentration. Not a candidate limit. |
| Göçer 2025, expressed solution | 695.40 ppb | Instrument solution. Abstract rounds to 695.4 ppb. Above the stated calibration top of 50 ppb. Not a sheet concentration. Not a candidate limit. |
| Göçer 2025, fiber | 565.46, 537.86, and 476.69 ppb | All three are printed. 476.69 is lower than the other two. No made-up final volume, so no mg/kg is calculated. Not a candidate limit. |
| Göçer 2025, packaging | 0.03 and 0.04 ppb | At or below the quantification limit of 0.10 ppb. Not a candidate limit. |
| Biver, Turner, and Filella 2021, six polyester textiles, totals | 125 to 471 µg/g | Textiles, not wipes. Not a wipe-sheet total. |
| Biver, Turner, and Filella 2021, artificial-sweat extracts, ISO 105-E04 | 0.402 ± 0.128 to 2.572 ± 0.031 µg/g | Simulant. Not absorption. Not a wipe-sheet total. |
What the standard does not claim
The mark on a baby wipe certifies heavy-metal safety, and antimony is now part of what that means: the finished product was tested and its total antimony fell below the EU Ecolabel floor of 30 mg/kg. It is not a claim that a wipe contains no antimony, and no analytical method can certify the absence of an element. It is not a claim built on the occurrence figures above either; those establish that antimony occurs in these materials, and the ceiling comes from a government limit rather than from the spread of the measurements. A concentration in a component, a digest, an annex, or a separated lotion or fiber is not a dose to an infant [16][17]. The evidence is read here as harm reduction rather than alarm: antimony is measurably present in wipe materials, the sovereign floor is a defensible place to hold it, and a caregiver is entitled to a product whose antimony content was actually checked against that floor. The certification decision is made on this side of the program; the Heavy Metal Index remains the literature base, cited one way, and does not set this ceiling [4]. This briefing names no brand and ranks no product.
Common questions
Is 30000 µg/kg a number HMTc made up?
No. It is the antimony floor in the EU Ecolabel for absorbent hygiene products, Commission Decision (EU) 2023/1809, Annex I criterion 7.3.8, which requires antimony below 30 mg/kg in the final product [1]. Thirty mg/kg is 30000 µg/kg. The standard binds that figure and discloses that the Ecolabel is voluntary; it originates no number of its own.
Why not use the Korea diaper limit of 60 mg/kg?
Because it measures a different thing. Korea’s MFDS Notice No. 2026-23 sets antimony for children’s disposable diapers at 60 mg/kg or less by migration, applied separately to the inner lining and the waterproof layer [2]. Migration is how much metal leaves the article under a test; total content is how much is in it. The baby-wipes cell is a total-content test, so the two figures are not interchangeable, and the Korea value is precedent rather than the ceiling.
Do the measured figures in this briefing set the limit?
No. The Washington, Choi, China Association, Göçer, and Biver figures are occurrence and context, and several are in units that cannot be compared with a finished-product total in mg/kg [5][6][7][8][12]. They are why antimony is on the panel. The ceiling is the EU Ecolabel total-content figure, and nothing in the certification cell is derived from occurrence. A printed concentration is not a skin dose [16].
Why not the 5 ppm, 10 µg/g, or 0.5 mg/kg antimony figures?
Because each one is a different legal object from Table 9. Health Canada’s cosmetic guidance treats antimony above 5 ppm as technically avoidable. It is guidance, and the indexed text does not name wipes [13]. Korea’s cosmetic safety standard sets antimony at or below 10 µg/g and gives no wet-wipe-specific figure for the metal [14]. Germany’s BVL 2017 orientation value is 0.5 mg/kg antimony for cosmetics in general, from a monitoring set of decorative cosmetics, baby powder, and toothpaste, not wipes [15]. None of those instruments rewrites Decision (EU) 2023/1809. The baby-wipes cell stays on Table 9, strictly less than 30 mg/kg total content in the finished product.
Does version 2 change the standard’s DOI?
No. No products had been certified under version 1.0, its DOI stays live as the previous version at https://doi.org/10.83138/hmtc.std.2.baby-wipes [3], and version 2 deposits no new DOI.
References
Works cited in this briefing’s text, in first-appearance order. This is not the full evidence base for the underlying standard; it is only what the prose above draws on. Every range in the briefing is a model built on one of these published anchors. Where a work carries a DOI or a public URL, its title and domain link to it; primary legal documents and published standards are named but not linked to a corpus record.
European Commission. (2023). Commission Decision (EU) 2023/1809 of 14 September 2023 establishing the EU Ecolabel criteria for absorbent hygiene products and for reusable menstrual cups. Official Journal of the European Union, L 234, 142. Criterion text: this sub-criterion applies to impurities in the final product. The following chemicals shall not be present in the final product in a concentration higher than what indicated in Table 9. Antimony < 30 mg/kg. Voluntary government floor, disclosed as such. Selected. Entered as 30000 µg/kg. Strictly less than. eur-lex.europa.eu↗
Ministry of Food and Drug Safety. (2026). Standards and specifications for sanitary products (Notice No. 2026-23, revised 24 March 2026; first enacted as Notice No. 2018-19, 21 March 2018). Section 13, disposable diapers: for children's diapers, harmful-element migration of antimony is 60 mg/kg or less, applied separately to the inner lining and the waterproof layer. No DOI. mfds.go.kr↗
Pendergrass, K. (2026). Baby wipes: HMTc Standard (Version 1.0). Institute of Contaminant Standards. DataCite: version 1.0, publication year 2026, registered 19 September 2026. No volume, no pages, and no separate print date. The house version history dates edition 1.0 to 2026-08-17. This DOI stays live. No products had been certified under it. Version 2 does not deposit a replacement DOI. https://doi.org/10.83138/hmtc.std.2.baby-wipes↗
Institute of Contaminant Standards. (n.d.). Heavy Metal Index. https://heavymetalindex.com. Literature base cited one way from this certification briefing. The Index does not set the baby-wipes antimony ceiling. · heavymetalindex.com↗
Stone, A. (2021). Metals in children’s and consumer products and packaging (Publication No. 14-04-014, rev. June 2021). Washington State Department of Ecology. Total elemental antimony at 40.6, 61.3, and 70.6 ppm in three baby-wipe components, 95.8 ppm in moist baby-wipes packaging, and 38.0 ppm in one breast-wipes package. The package row is not a baby-wipe sheet. The same three wipe rows print lead at 0.4, 0.8, and 1.4 ppm. Upper-tail screen confirmed by ICP-MS after X-ray fluorescence. The 100 ppm Children's Safe Products Act figure is a reporting trigger, not this ceiling. Not a candidate limit. apps.ecology.wa.gov↗
Choi, S.-M., Song, J.-K., & Kim, S.-J. (2016). Determination of heavy metals on the non-woven in wet wipes using ICP-MS. Journal of the Korean Oil Chemists' Society, 33(1), 195-203. Print date 30 March 2016. Crossref records no separate online date. Table 5 prints antimony from 187.86 ± 5.24 to 19,558.35 ± 3,537.3 µg/L in 12 of 24 wet-wipe nonwovens, after digesting approximately 0.2 g and diluting with 25 mL of water, not made up to 25 mL. The paper prints neither sheet figure. × 0.125, treating the final volume as 25 mL, gives about 23.48 to 2,444.79 mg/kg. × 0.165, from 8 mL of acid plus 25 mL of water, gives a higher top of about 3,227.13 mg/kg. The highest sheet in Table 5 is labeled rayon only, and several polyester-labeled sheets were not detected. The polyester-catalyst explanation is a hypothesis for wipes, not a finding. Neither derived figure is a candidate limit. https://doi.org/10.12925/jkocs.2016.33.1.195↗
China Association for Quality Promotion of Consumer Products Safety. (2026, April 2). [Monitoring results for total antimony in 21 baby wet wipes sold online]. Total antimony detected in 20 of 21 online baby wipes and not detected in one. Preferred reads of the annex image, in sample order and without brand names, run from 15.02 to 450.45 µg/L. A second pass of wrapped cells differed and is not adopted. Preparation not described. Not a candidate limit. cpqs.org.cn↗
Biver, M., Turner, A., & Filella, M. (2021). Antimony release from polyester textiles by artificial sweat solutions: A call for a standardized procedure. Regulatory Toxicology and Pharmacology, 119, Article 104824. Print issue February 2021. Crossref records no separate online date. The DOI article number is from 2020; the citation year is the 2021 issue year. Six polyester textiles, not wipes. Totals 125 to 471 µg/g. Extracts under ISO 105-E04, 0.402 ± 0.128 to 2.572 ± 0.031 µg/g. Simulant, not absorption, and not a wipe-sheet total. https://doi.org/10.1016/j.yrtph.2020.104824↗
European Commission. (2014). Commission Decision 2014/350/EU establishing the ecological criteria for the award of the EU Ecolabel for textile products. Criterion 7(a): the level of antimony present in the polyester fibres shall not exceed 260 ppm. Polyester fibres manufactured from recycled PET bottles are derogated. Criterion 13, Appendix 1, point (iv) Extractable metals: antimony 30,0 mg/kg, extraction EN ISO 105-E04:2013 (acid sweat solution), for products intended for babies and children under 3 years old and for all other products. Decision (EU) 2017/1392 replaced that extractable-metals entry and left antimony at 30,0 mg/kg. No DOI. Not selected. eur-lex.europa.eu↗
Maximum contaminant levels for inorganic contaminants, 40 C.F.R. § 141.62(b)(11) (2025). Antimony, 0.006 mg/L. No federal limit for antimony in diapers, wipes, or textiles was identified. The drinking-water figure is orientation only. No DOI. ecfr.gov↗
European Parliament and Council. (2020). Directive (EU) 2020/2184 on the quality of water intended for human consumption (recast), Annex I, Part B, chemical parameters. Antimony, parametric value 10 μg/L. Orientation only. Not a sheet total. No DOI. eur-lex.europa.eu↗
Göçer, İ. A. (2025). Evaluation of the liquid, fiber and packaging content of baby wet wipes for heavy metal contamination (MSc thesis). İstanbul Üniversitesi-Cerrahpaşa. YÖK thesis catalog 988276. Solution antimony 695.40 ppb. Fiber antimony printed as 565.46, 537.86, and 476.69 ppb. Packaging antimony 0.03 and 0.04 ppb, at or below the quantification limit of 0.10 ppb. Results of several hundred ppb sit above the stated calibration top of 50 ppb. Approximate 0.2 g digested, then 10 mL of water added. No made-up final volume, so no sheet concentration is calculated. Brand names are not repeated. Not a candidate limit. tez.yok.gov.tr↗
Health Canada. Guidance on heavy metal impurities in cosmetics, section 4. Antimony above 5 ppm in a finished cosmetic is treated as technically avoidable. Guidance, not a regulation. The indexed text does not name wipes. Not selected. Not the baby-wipes ceiling. canada.ca↗
Ministry of Food and Drug Safety, association reproduction. Cosmetic safety standard, Article 6(2), unintentional traces. Antimony at or below 10 µg/g. The same article names wet wipes for methanol, formaldehyde, and microbial limits, and it gives no wet-wipe-specific figure for antimony. Not selected. Not the baby-wipes ceiling. kcia.or.kr↗
Federal Office of Consumer Protection and Food Safety (BVL). (2017). Technically avoidable heavy metal contents in cosmetic products. Journal of Consumer Protection and Food Safety, 12, 51-53. Online 6 October 2016. Orientation value 0.5 mg/kg antimony for cosmetics in general. The monitoring set was decorative cosmetics, baby powder, and toothpaste, not wipes. Not selected. Not the baby-wipes ceiling. https://doi.org/10.1007/s00003-016-1044-2↗
Pendergrass, K. (2026). Heavy metals in baby wipes. Heavy Metal Index. https://doi.org/10.83376/hmi.heavy-metals-in-baby-wipes. Last updated 2026-09-28. Four datasets, four bases. Antimony is the metal detected in all four, including the expressed lotion and the fiber. A concentration is not a dose. The synthesis ranks no products and proposes no limit. Literature base, cited one way. It does not set the baby-wipes ceiling. heavymetalindex.com↗
Pendergrass, K. (2026). Antimony in baby products. Heavy Metal Index. https://doi.org/10.83376/hmi.antimony-in-baby-products. Last updated 2026-09-30. Table 9 of Decision (EU) 2023/1809 is transcribed as antimony < 30 mg/kg, content in the final product, not migration, criteria valid until 31 December 2029. The synthesis sets no certification number and names no brands. Literature base, cited one way. It does not set the baby-wipes ceiling. heavymetalindex.com↗
Bibliographic record
The fields an indexing service reads. Title, named first author and year are the three that carry the record; a briefing missing any one of them is treated as carrying no metadata at all.
The three peer-track preprints are deposited with DOIs; the briefing series is not. Depositing the briefings would make each independently resolvable after any URL change, worth doing for the documents most likely to be cited.
Cite this briefing
Pendergrass, K. (2026). Why the Baby-Wipes Standard Adds Antimony: Version 2 of the baby-wipes standard sets antimony at 30000 µg/kg. The basis is total content under 30 mg/kg in the finished product, from the voluntary EU Ecolabel in Decision (EU) 2023/1809, Annex I criterion 7.3.8. (HMTc Standards Briefing 13). Institute of Contaminant Standards (ICS).
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