Gautam 2024 - formaldehyde and heavy metals in finger paints
This ESR client report for Health New Zealand develops a generic health-risk assessment for children up to 3 years of age exposed to formaldehyde and heavy metals in finger paints. It is not a New Zealand occurrence survey, but it compiles published finger-paint concentration studies and EU Safety Gate/RAPEX recall examples, then models dermal plus oral exposure for 1-year-old and 2-3-year-old children. The report keeps the finger-paint matrix under toy/graphic-material regulation and uses maximum reported values for the exposure calculations, so the numbers below are secondary and conservative rather than a local market distribution.
Key numbers
- Report identity: ESR client report
FW24026, prepared for Health New Zealand, National Public Health Service, November 2024. - Product description: finger paints are paste-like or jelly-like colored preparations designed for children, applied to suitable surfaces with fingers or hands, and generally containing water, coloring agents, fillers, binders, humectants, preservatives, surfactants, and bittering agents.
- New Zealand incident surveillance: the National Poisons Centre told ESR it does not collect exposure data on finger paints from callers; the most common related calls are children ingesting craft paints, described in the report as of little acute consequence in nearly every case.
Published concentration studies summarized in Table 1
All values below are reproduced as the report prints them in mg/kg. These are secondary literature values summarized by the agency report, not measurements newly generated by ESR.
| Survey country | Samples | Reported mean concentration and range |
|---|---|---|
| Spain | 5 | Formaldehyde 633 (440-793) |
| Spain | 6 | Formaldehyde 610 |
| Not reported | 2 | Formaldehyde >1,000 |
| USA | 1 | Formaldehyde 201 |
| Denmark | 29 | Formaldehyde (20-70) |
| Iran | 10 | tAs 0.38 (0.33-0.45); Cd 6.76 (4.8-9.6); Cr 9 (7.3-11); Pb 50 (42-70) |
| Turkey | 7 | Cu 25.3 (<DL-144); Pb 2.6 (1.7-3.7); Mn 9 (4.5-13) +/- 0.4; Cd 0.83 (<DL-1.3); Co <DL; Ni 3.5 (2.6-5.3) |
| Saudi Arabia | 11 | tAs 3.05 (0.2-8); Pb 1.40 (0.4-5); Mn 42.2 (1.42-372); Cd 0.1 (0.05-0.2); Co 4 (1-14); Ni 5.2 (0.7-18.5) |
| Denmark | 57 | Cd <1; Cr <1->10; Pb <1->10 |
| Portugal | 6 | Pb <DL; Cd 0.02 (<DL-0.03); Co 0.12 (<DL-0.2); Cr 0.25 (0.2-0.42); Ni 0.8 (1.2-0.70); Mn <DL; Cu 86 (<DL-338); Zn <DL |
The Saudi Arabia row is marked in the source as * Type of finger paint not specified. Arsenic is reported only as As, so this page treats it as total arsenic (tAs) and does not promote it to inorganic arsenic.
Regulatory migration limits summarized by the report
| Jurisdiction | Finger-paint regulatory frame | Limits reproduced in the report |
|---|---|---|
| EU | Toy Safety Directive 2009/48/EC; finger paints are Category II liquid or sticky toy material under EN71-3. | Al 1,406 mg/kg; Sb 11.3 mg/kg; As 0.9 mg/kg; Ba 375 mg/kg; B 300 mg/kg; Cd 0.3 mg/kg; Cr(III) 9.4 mg/kg; Cr(VI) 0.005 mg/kg; Co 2.6 mg/kg; Cu 156 mg/kg; Pb 0.5 mg/kg; Mn 300 mg/kg; Hg 1.9 mg/kg; Ni 18.8 mg/kg; Se 9.4 mg/kg; Sr 1,125 mg/kg; Sn 3,750 mg/kg; organic tin 0.2 mg/kg; Zn 938 mg/kg. |
| EU | Toy Safety Directive updates (EU) 2019/1922 and 2019/1929. | Formaldehyde limit for water-based toy material, including finger paints: 10 mg/kg. |
| Australia | Consumer Protection Notice No. 1 of 2009. | Sb 10 mg/kg; As 10 mg/kg; Ba 350 mg/kg; Cd 15 mg/kg; Cr 25 mg/kg; Pb 25 mg/kg; Hg 10 mg/kg; Se 50 mg/kg. |
| New Zealand | Graphic Materials Group Standard 2020. | Sb 60 mg/kg; As 25 mg/kg; Ba 250 mg/kg; Cd 50 mg/kg; Cr 25 mg/kg; Pb 90 mg/kg; Hg 25 mg/kg; Se 500 mg/kg. |
EU Safety Gate/RAPEX recall examples summarized in Table 5
The source names individual recalled products. This source page suppresses product names around contamination values under the brand firewall and reports only category-level recall examples:
- Safety Gate count:
33alerts or recalls for finger-paint products due to formaldehyde, heavy metals, or other chemicals between January 2014 and July 2024. - Formaldehyde recall examples: seven products in 2023, with reported maxima
up to 720 mg/kg,up to 2,500 mg/kg,up to 140 mg/kg,up to 7,255 mg/kg,up to 958 mg/kg,up to 510 mg/kg, and one entry described as containing formaldehyde without a numeric value. - Heavy-metal recall examples: one 2022 product had excessive migration of Al and Cu at
up to 2,612 mg/kgand296 mg/kg, respectively; one 2021 product had Pb in white paint at11,800 mg/kg; one 2016 product had Al at265,000 mg/kgand Co in the red color at2,629 mg/kg; one 2015 product had Pb at4.52 mg/kg.
Exposure inputs and modeled exposure
For its exposure assessment, ESR selected maximum reported values from the published studies and EU product recalls: Pb 11,800 mg/kg; tAs 3.05 mg/kg; Cd 6.76 mg/kg in the dermal/oral input tables, with Table 10 printing Cd concentration as 6.74; Cr 9 mg/kg; Ni 3.5 mg/kg; formaldehyde 7,255 mg/kg.
| Input | Value |
|---|---|
| Dermal product amount | 20 g; the report assumes all paint used each time ends on skin and is accessible for dermal absorption. |
| Dermal absorption | Heavy metals 1%; formaldehyde 5%. |
| Oral product amount | 400 mg swallowed. |
| Oral absorption | tAs 100%; Cd 6%; Cr 7%; Ni 10%; Pb 60%; formaldehyde 100%. |
| Event frequency | 45 minutes per day, 100 times per year, equivalent to 100/365 = 0.274 events/day. |
| Body weight | 1-year-old child 9.65 kg; 2-3-year-old child 15.2 kg. |
| Alternate RIVM ingestion scenario cited but not used | 30 mg/min for 45 min, yielding 1,350 mg per play event. |
Table 10 exposure outputs are in mg/kg bw/day:
| Chemical | Concentration used | 1-year oral | 1-year dermal | 1-year total | 2-3-year oral | 2-3-year dermal | 2-3-year total |
|---|---|---|---|---|---|---|---|
| tAs | 3.05 | 3.41E-05 | 1.70E-05 | 5.12E-05 | 2.10E-05 | 1.10E-05 | 3.10E-05 |
| Cd | 6.74 | 4.52E-06 | 3.76E-05 | 4.22E-05 | 3.0E-06 | 2.42E-05 | 2.72E-05 |
| Cr | 9 | 7.04E-06 | 5.03E-05 | 5.74E-05 | 4.54E-06 | 3.24E-05 | 3.70E-05 |
| Ni | 3.5 | 4.0-06 | 2.0E-05 | 2.35E-05 | 2.52E-06 | 1.26E-05 | 1.51E-05 |
| Pb | 11,800 | 0.08 | 0.06 | 0.14 | 0.05 | 0.04 | 0.09 |
| Formaldehyde | 7,255 | 0.08 | 0.20 | 0.30 | 0.05 | 0.13 | 0.18 |
The 4.0-06 nickel oral-exposure entry is transcribed exactly as printed in Table 10; context indicates scientific notation, but the source page does not silently repair it.
Margin of safety values from Table 11
| Chemical | 1-year total exposure (mg/kg/day) | 2-3-year total exposure (mg/kg/day) | PODsys used | MOS 1-year | MOS 2-3-year |
|---|---|---|---|---|---|
| tAs | 5.12E-05 | 3.10E-05 | NOAEL 0.0008 mg/kg bw/day | 15.64 | 24.25 |
| Cd | 4.22E-05 | 2.72E-05 | NOAEL 0.005 x 0.06 = 0.0003 | 7.11 | 11.02 |
| Cr | 5.74E-05 | 3.70E-05 | NOAEL 2.5 x 0.07 = 0.17 | 3050 | 4731 |
| Ni | 2.35E-05 | 1.51E-05 | NOAEL 5 x 0.1 = 0.5 | 21000 | 33000 |
| Pb | 0.14 | 0.09 | BMDL01 0.0006 x 0.6 = 0.00036 | 0.002 | 0.003 |
| Formaldehyde | 0.30 | 0.18 | NOAEL 15 | 52.82 | 82 |
The report states that MOS values were more than 100 for Cr and Ni, but less than 100 for As, Cd, Pb, and formaldehyde. The report also cautions that these modeled risks use maximum reported values, so the calculated risks are likely overestimates of chronic risk levels and the concentration data were not obtained from products available in New Zealand.
Methods (brief)
This is a Health New Zealand/ESR desk-based risk assessment, not a laboratory occurrence study. It reviews finger-paint regulations, prior assessments, toxicity summaries, published concentration studies, and European Safety Gate/RAPEX recalls, then models oral and dermal exposure for children up to 3 years old. No analytical instrument, digestion method, LOD, LOQ, or New Zealand sample frame is reported because ESR did not generate new concentration measurements. Metal speciation is not provided for the occurrence inputs: As is treated here as total arsenic (tAs), Cr is total chromium unless the regulatory table explicitly says Cr(III) or Cr(VI), and there are no inorganic-arsenic or methylmercury data.
Implications
Certification (HMTc): This source supports regulatory and exposure-model context for finger paints as children’s art/craft toy materials. Its concentration values are useful for identifying analytes and upper-bound scenario inputs for art-craft-materials and toys-crafts-other, but they should not be pooled as a New Zealand market occurrence distribution because the report uses secondary literature and EU recall examples.
Courses: The report is a useful case study for regulatory affairs and product-safety teams because it contrasts EU, Australian, and New Zealand migration limits for the same liquid/sticky toy-material use case and shows how maximum concentration inputs flow into a margin-of-safety screen.
App: If a children’s art-material exposure card is built, this source can supply route and parameter context for finger-paint dermal/oral exposure scenarios. It should not surface named recalled products next to contamination values.
Wiki pages this source may touch
- art-craft-materials
- toys-crafts-other
- arsenic-total
- cadmium
- chromium
- lead
- nickel
- aluminum
- copper
- cobalt
- manganese
- zinc
Verification notes
- PDF text was extracted with
pdftotext -layoutto/tmp/ingest.txt; Tables 1-6, 8-11, the executive summary, and the conclusions were checked against this page. - Identity checks before creation: exact title, report number
FW24026, raw handleMFK_cat21-04-formaldehyde-heavy-metals-finger-paints, raw SHA-256b99c26343a2bf6d5b49ec27ce6e63835ebee108006157c09ca5ab2570737e4d8, and candidate cite keygautam2024-finger-paints-metals-formaldehydewere searched inwiki/sources/anddata/evidence/audit-queue.csv; no existing source page was found. DOI is not assigned on the report landing page, sono_doi_assigned: trueis set with the PHF Science/ESR access URL. - Units are copied as printed (
mg/kg,mg/kg bw/day,g,mg,%, and MOS unitless values). No unit conversion was performed. - Speciation: the report writes arsenic as
As, not inorganic arsenic, so this source page records occurrence/exposure inputs as total arsenic (tAs). The report discusses Cr(III) and Cr(VI) regulatory limits and skin effects, but no finger-paint occurrence input is speciated; measuredCris kept as total chromium. - Brand firewall: Table 5 names recalled finger-paint products. This source page does not reproduce those names next to contamination values; it reports recall examples at the product-category level only.
- Evidence tier:
Abecause this is an ESR/Health New Zealand agency risk-assessment report with transparent exposure equations and regulatory tables. Its occurrence contribution is secondary/contextual, not primary market sampling. - Routing audit:
npm run evidence:source-routesexited0; this source generated2product routing rows (art-craft-materialsandtoys-crafts-other), was absent fromdata/evidence/routing_unresolved.csv, and had only the expected nonblockingingredients;matricesadvisory indata/evidence/routing_malformed.csvbecause this is a non-food hard-goods/craft-material source with no ingredient matrix.
Page history
The five most recent substantive edits to this page. The full version history lives in git; when DOI minting comes online (see schema docs), each entry below will also link to a version-pinned DataCite DOI.
| Commit | Date | Description |
|---|---|---|
| 4039d20 | 2026-06-10 | scope: broaden ingest to the full upstream+downstream literature (marine, atmospheric, attribution, exposure, toxicology) — inclusion is the default |