Gautam 2022 - lead, cadmium, and nickel in jewelry risk assessment
This ESR client report for the New Zealand Ministry of Health develops a generic risk assessment for incidental oral and dermal exposure to Pb, Cd, and Ni in jewelry. It is not a New Zealand occurrence survey; the report explicitly says no New Zealand jewelry recall data and no New Zealand occurrence/prevalence data were available. The quantitative sections summarize overseas metal-content, bioaccessibility, and risk-assessment studies, then interpret those studies for children and adults who mouth, swallow, or wear jewelry.
Key numbers
- Report identity: ESR client report
FW22035, prepared for the Ministry of Health in November 2022 and peer reviewed by Dr Jeff Fowles. - Scope: the report restricts the current assessment to Pb, Cd, and Ni, even though other metals have occasionally been examined in jewelry.
- Product definition: jewelry includes decorative items such as brooches, rings, necklaces, earrings, pendants, bracelets, and cufflinks, attached to the body or clothes. Low-cost jewelry may be made from metals or plastic and may use recycled batteries or other recycled materials.
- New Zealand data gap: the report states that there have been no New Zealand jewelry recalls due to heavy-metal contamination and that occurrence or prevalence data for metals in New Zealand jewelry are not available.
Metal-content and bioaccessibility studies summarized in Table 1
All units below are copied from the report. These are secondary study summaries, not new ESR measurements.
| Study/source summarized | Sample frame | Total content | Bioaccessible or release results |
|---|---|---|---|
| Cui et al. 2015 | Metallic jewelry; Cd, Pb, and Ni by acid digestion ICP-MS; saliva and 0.07 M HCl extraction. | Total Cd 0.017 - 139 mg/kg; total Pb 1 mg/kg - 860 g/kg; total Ni 1.47 - 2894 mg/kg. | Saliva extraction ug/kg: Cd ND - 927, Pb ND - 638, Ni 16 - 261000. HCl extraction ug/kg: Cd 1 - 410, Pb ND - 770, Ni ND - 1039000. |
| Guney and Zagury 2014 | Metallic jewelry; total content not tested; saliva and 0.07 M HCl extraction. | Not tested. | Saliva extraction mg/kg: Cd <0.02 - 22.8, Pb <0.17 - 0.53, Ni <0.06 - 2.93. HCl extraction mg/kg: Cd <0.11 - 80, Pb <0.90 - 647, Ni <0.34 - 46. |
| Pouzar et al. 2017 | Metallic jewelry, Cd by ED-XRF; acidic and alkaline sweat 1 mL per 1 cm2. | Cd surface-layer content 13.4 - 44.64% (w/w). | Total released amount (ug/cm2/Week): acidic 4.0 - 253; alkaline 3.3 - 62. |
| Terry et al. 2020 | Metallic jewelry; Cd, Pb, and Ni by FAAS; no bioaccessibility test. | Total Cd <DL; total Pb 4.6 - 34.4 mg/kg; total Ni 5.8 - 17 mg/kg. | Not tested. |
| Danish EPA 2008 | Metallic jewelry; Cd, Pb, and Ni by XRF plus saliva migration. | Total metal content: Cd 0.03 - 4%; Pb 0.03 - 70%; Ni 0.06 - 70%. | Migration (ug/g): Cd 0.31 - 16; Pb 2 - 540; Ni 0.5 - 210. |
Regulations summarized by the report
- New Zealand: the Product Safety Standards (Children’s Toys) Regulations 2005 set safety standards for children’s toys and jewelry, but the report says those regulations do not address chemical compositional issues. AS/NZS ISO 8124.3:2021 specifies migration limits from toy materials; for toy materials except modelling clay and finger paint, the report lists Cd
75 mg/kgand Pb90 mg/kg. - Canada: children’s jewelry under the Canada Consumer Product Safety Act and Children’s Jewellery Regulations must not contain more than
90 mg/kgtotal Pb and130 mg/kgCd, applying to all materials and coatings. - United States, children’s jewelry (ASTM F2923-14/F2923-20): Pb in accessible components other than paint and surface coatings
<=100 ppm or mg/kg; Cd in accessible plastic/polymeric small parts<=300 ppmcontent and<=75 ppmextractable; Cd in accessible metal small parts<=300 ppmcontent and<=200 ppmextractable; Cd in accessible metal or plastic/polymeric components that are not small parts but may be mouthed<=300 ppmcontent and<=18 ppmextractable; Ni release<=0.2 ug/cm2 per weekfor post assemblies inserted into pierced ears or other pierced body parts; Ni release<=0.5 ug/cm2 per weekfor direct and prolonged skin contact. - United States, adult jewelry (ASTM F2999-19): Pb in electroplated metal
<6.0%, non-plated metal<1.5%, plastic/rubber/stone/PVC<200 mg/kg, paint coatings<600 mg/kg, and other materials<600 mg/kg; Cd in metal or plastic/polymeric materials<1.5%; extractable Cd and Ni release as for children’s jewelry. - EU/EEA REACH: Cd in metal beads and other metal jewelry components
<0.01%; Ni release from piercing post assemblies<0.2 ug/cm2 per week; Ni release from direct/prolonged skin-contact articles<=0.5 ug/cm2 per week; Pb in any individual jewelry part<0.05%. - Brazil: Ordinance No. 43 of 22 January 2016 restricts jewelry and jewelry formulations intended for skin contact to Cd below
0.01%by weight and Pb below0.03%by weight.
Recall and case-report numbers summarized by the report
The report names recalled products in Table 2. This page keeps recalled-product identities out of value-linked rows and reports category-level recall facts only:
- United States: more than
18 millionitems withdrawn from the market because of Pb contamination between 2007 and 2018 via174product recalls. - United States 2010: over
12 millionchildren’s products and jewelry items recalled viasevenrecalls due to elevated total Cd concentrations. - Lead fatality case: a 4-year-old child died after ingesting a heart-shaped metallic charm containing
99.1%lead; CPSC announced a voluntary recall of300,000heart-shaped charm bracelets in 2006. - Lead poisoning case: a 4-year-old child developed abdominal cramping, vomiting, and diarrhea after ingesting a medallion pendant containing
38.8%Pb,3.6%Sb, and0.5%Sn. - Oregon case report: a necklace medallion swallowed by a child contained
39.11%lead, and a similar medallion from the same lot contained44%lead; a related state recall involved approximately1.4 millionmetal toy necklaces. - Another case report: metal beads in an amulet had total Pb
450,000 mg/kg (45%). - Australia 2020-2021: the report identifies two recalls of children’s jewelry because of high Cd levels and says it is unclear whether those products were also sold in New Zealand.
Exposure scenarios and risk-characterization summaries
- Exposure routes considered: adults - dermal exposure from whole jewelry; children - dermal and oral exposure from jewelry or parts. Inhalation is not considered relevant.
- Child mouthing context: the report states mouthing behavior frequency peaks at
6-12 monthswith mouthing duration in the range39-66 min/day. - Danish EPA bioaccessible-concentration and exposure estimates from Table 8:
| Metal | Bioaccessible concentration (ug/kg) | Adult dermal (ug/kg bw/day) | Child dermal (ug/kg bw/day) | Adult oral (ug/kg bw/day) | Child oral (ug/kg bw/day) |
|---|---|---|---|---|---|
| Cd | 1.2 - 3.0 | 0.014 - 0.036 | 0.043 - 0.072 | 0.2 - 0.5 | 0.6 - 1.5 |
| Pb | 39 - 210 | 0.046 - 0.25 | 0.14 - 0.75 | 5.6 - 30 | 0.06 - 105 |
| Ni | 13 - 90 | 0.5 - 3.6 | 1.56 - 10.8 | 2 - 15 | 6.5 - 4.5 |
The Ni child-oral range is copied as printed (6.5 - 4.5) and appears internally reversed or truncated in the source.
- Cui et al. 2015 child CDI/HIs from Table 12: Cd saliva CDI
0.003 - 1.0 ug/kg bw per daywith HIsaliva0.016 - 3.0; Cd gastrointestinal CDI0.001 - 0.44with HIgastro0.021 - 0.89. Pb saliva CDI0.3 - 5.0with HIsaliva0.08 - 0.5; Pb gastrointestinal CDI0.1 - 0.7with HIgastro(3.0E-05) - 0.19. Ni saliva CDI0.05 - 800with HIsaliva0.005 - 80; Ni gastrointestinal CDI0.0002 - 1183with HIgastro(2.17E-05) - 118. - Guney and Zagury 2014: ingestion of jewelry parts or pieces gave unacceptable HIs in the range
1.1 - 75for Cd, Pb, or Ni; saliva mobilization produced HI>1for three jewelry items, two for Cd and one for Ni, with HI range1.1 - 6.1; ingestion of scraped-off material had HI< 1for all samples, metals, and age categories. - Pouzar et al. 2017: Cd release into alkaline sweat
3.2 - 62 ug/cm2 per weekwith MADD3.56 x 10-4 to 4.54 x 10-3 ug/kg bw/day; acidic sweat3.5 - 253 ug/cm2 per weekwith MADD2.00 x 10-4 to 1.86 x 10-2 ug/kg bw/day. Adult RCR values were7.4 x 10-3 to 1.1 x 10-1%for alkaline sweat and5.0 x 10-3 to 4.64 x 10-1%for acidic sweat. - The report’s overall conclusion: contamination of jewelry with Pb, Cd, and Ni at levels reported in overseas studies may present a health risk to children and adults after oral exposure, while dermal Cd risk was inconsistent across studies.
Methods (brief)
This is a desk-based ESR/Ministry of Health risk assessment rather than a laboratory survey. It reviews jewelry definitions, overseas regulations, recalls, case reports, prior metal-content and bioaccessibility studies, and existing risk assessments for Pb, Cd, and Ni in jewelry. The summarized studies used XRF, ED-XRF, FAAS, ICP-MS, ICP-OES, artificial saliva, 0.07 M HCl, acidic sweat, and alkaline sweat depending on study. Speciation is not reported for Pb, Cd, or Ni; the report treats them as elemental total content or extractable/released elemental metal. It explicitly notes that the JECFA Pb PTWI used in older studies has been withdrawn and that Pb exposure should be as low as possible.
Implications
Certification (HMTc): This source supports regulatory and exposure-context routing for children’s jewelry and piercing post assemblies, especially for Pb, Cd, and Ni. It should not be pooled as New Zealand market occurrence data because it contains no original New Zealand testing and relies on secondary overseas studies and recalls.
Courses: The report is a useful regulatory-affairs and product-safety case study for distinguishing total metal content, saliva/gastric bioaccessibility, sweat release, and dermal versus oral exposure assumptions in jewelry.
App: If a jewelry or pierced-contact-product exposure surface is built, this source can provide child mouthing-duration context, oral/dermal route distinctions, and a warning that older Pb risk characterizations used a withdrawn PTWI.
Wiki pages this source may touch
Verification notes
- PDF text was extracted with
pdftotext -layoutto/tmp/ingest.txt; the executive summary, Tables 1-13, regulatory sections, recall/case-report sections, and conclusions were checked against this page. - Identity checks before creation: exact title, report number
FW22035, raw handleMFK_cat21-05-heavy-metal-in-jewellery, raw SHA-256010d1eee9289bf51735b280dc8e1eb6890f154d6ce37902fe86d263a76134daa, access URL, and candidate cite keygautam2022-jewellery-heavy-metalswere searched inwiki/sources/anddata/evidence/audit-queue.csv; no existing source page was found. - DOI is not assigned in the extracted PDF or publisher PDF URL, so
no_doi_assigned: trueis set with the PHF Science/ESR PDF access URL. - Units are copied as printed (
mg/kg,ug/kg,ug/g,ug/cm2 per week,%,ug/kg bw/day, and RCR%). No unit conversion was performed. - Speciation: Pb, Cd, and Ni are not speciated; the page does not infer chemical forms. Sb and Sn appear in one case report but are not part of the report’s risk-assessment scope or frontmatter analyte routing.
- Brand firewall: the report names recalled jewelry products. This page suppresses those names around contamination values and reports recall examples by category/event only.
- Product slug note: no adult-jewelry product slug is available in the current routing vocabulary, so the page routes to the existing children’s jewelry and piercing-post product pages and records the broader adult-jewelry context in text only.
- Evidence tier:
Abecause this is an ESR/Ministry of Health agency risk-assessment report with transparent source tables, regulatory review, and risk-characterization logic. Its occurrence contribution is secondary/contextual, not primary market sampling. - Routing audit:
npm run evidence:source-routesexited0; this source generated1product routing row (childrens-jewelry), 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/jewelry 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 |