Li 2019 - plastic food packaging metal migration
Li, Lee, and Zhan report a Shimadzu application-note experiment measuring 14 elements leached from plastic food-packaging materials into aqueous simulants by ICP-MS. The evidence is C-tier because it is a vendor application note rather than a peer-reviewed paper, but it contains routeable food-contact-material leachate values for PS and PP containers and PE film. The results are migration into simulants, not metal concentrations in food as consumed.
Key numbers
- Source identity: Shimadzu Application News No.
AD-0207; PDF metadata creation date13 November 2019;5PDF pages. - Materials: polystyrene (
PS) container, polypropylene (PP) container, and polyethylene (PE) film obtained from local food markets. - Leaching setup:
0.5 gramsof each packaging material immersed in40 mLof aqueous solution at room temperature. Simulants were DI water (simulant A),3% acetic acid(simulant B), and2% nitric acid. - Analysis setup: after immersion,
1 mLof soaking solution was mixed with1 mLof3% acetic acidand diluted to10 mL; calibration standards were prepared up to50 ppbfor Al, As, Cd, Co, Mn, Ni, and Sb or200 ppbfor Ba, Cr, Cu, Fe, Li, Pb, and Zn. - Table 2 method performance: calibration coefficients were
r >0.9999for all targeted elements. LODs were sub-ppb for all analytes, including As0.005 µg/L, Cd0.001 µg/L, and Pb0.123 µg/L. - Table 3 spike recovery:
10 ppbspikes in simulant B from PS and PP samples gave recovery rates from87%to116%across 14 elements, with most triplicate RSDs below3%. - Contact-time result: Figure 2 is graphical only in the extracted text; the authors state qualitatively that migration into simulant B increased from
1hto72hfor both PS container and PE film.
Table 4 migration into food simulant B after 72 hours
Values are copied with the source table’s unit label, µg/kg; N.D. is the source notation. The results prose describes the same concentrations as µg/L, so the table/prose unit conflict is flagged in Verification notes.
| Element | PS container | PP container | PE film | MDL |
|---|---|---|---|---|
| Al | 49.3 | 71.4 | 135.5 | 2.01 |
| As | 0.11 | 0.06 | 0.48 | 0.05 |
| Ba | 14.0 | 7.14 | 22.9 | 0.05 |
| Cd | N.D. | N.D. | 0.26 | 0.012 |
| Co | N.D. | N.D. | N.D. | 0.006 |
| Cr | 6.50 | 0.15 | 0.84 | 0.13 |
| Cu | 30.4 | 19.6 | 13.3 | 1.23 |
| Fe | 17.0 | 2.39 | 142.5 | 1.04 |
| Li | N.D. | N.D. | N.D. | 0.64 |
| Mn | 2.51 | N.D. | 52.8 | 0.08 |
| Ni | 8.81 | 1.86 | 2.14 | 0.67 |
| Pb | 2.22 | 0.19 | 3.27 | 0.06 |
| Sb | 0.08 | 0.04 | 0.40 | 0.006 |
| Zn | 34.60 | 23.50 | 685.5 | 0.73 |
The text highlights PE film as having Zn 685.5, Fe 142.5, and Al 135.5 among the highest leachate values; for PS and PP containers, the most leached element was Al followed by Zn and Cu. Arsenic and lead were detected across 0.06 - 0.48 and 0.19 - 3.27, respectively, using the source’s prose units; cadmium was detected only from PE film at 0.26.
Table 5 PE film migration into different aqueous solutions
Values are copied as µg/kg.
| Element | Food Simulant A DI water | 2% HNO3 | Food Simulant B 3% acetic acid |
|---|---|---|---|
| Al | 21.0 | 29.9 | 135.5 |
| As | 0.01 | 0.15 | 0.48 |
| Ba | 13.4 | 15.8 | 22.9 |
| Cd | N.D. | 0.05 | 0.26 |
| Co | N.D. | N.D. | N.D. |
| Cr | 0.03 | 0.69 | 0.84 |
| Cu | 1.94 | 3.86 | 13.3 |
| Fe | 3.72 | 73.0 | 142.5 |
| Li | N.D. | N.D. | N.D. |
| Mn | 1.09 | 15.9 | 52.8 |
| Ni | 0.91 | 1.37 | 2.14 |
| Pb | 0.02 | 2.54 | 3.27 |
| Sb | 0.04 | 0.08 | 0.40 |
| Zn | 31.4 | 127.5 | 685.5 |
Methods (brief)
The application note used a Shimadzu ICPMS-2030 with helium collision-cell mode for all elements except Li and Sb. Samples were prepared from plastic packaging pieces leached at room temperature into DI water, 3% acetic acid, or 2% nitric acid; tabled PS/PP/PE comparisons use food simulant B after 72 hours. Calibration used multi-element standards, online internal standards (Sc, Y, Rh, Bi), blank-derived LOD/LOQ estimates, and 10 ppb spike-recovery checks in PS and PP simulant B extracts.
Implications
Certification (HMTc): This source is small, C-tier food-contact-material leachate evidence for plastic packaging rows. It should not be pooled with food-as-consumed values and should carry the application-note quality caveat.
Courses: The note is a compact example of how simulant choice and contact time can change apparent metal migration from packaging materials.
App: If surfaced, the source can support a food-packaging-material context card that distinguishes PS/PP containers from PE film and keeps 3% acetic acid leachate values separate from DI-water or nitric-acid simulants.
Wiki pages this source may touch
- food-packaging-plastic-tubs
- food-packaging-flexible-pouches-films
- aluminum
- arsenic-total
- barium
- cadmium
- chromium
- cobalt
- copper
- iron
- lithium
- manganese
- nickel
- lead
- antimony
- zinc
Verification notes
- PDF text was extracted with
pdftotext -layoutto/tmp/ingest.txt; the overview, sample preparation, analytical conditions, Tables 2-5, contact-time paragraph, conclusion, and references were checked against this page. - Identity checks before creation: title phrase, Application News number
AD-0207, raw SHA-256b9e53b47d199040dcf9bae2b8ffa620d1cb53f1ddaace538152b835281c22567, raw handleMFK_evaluation-of-heavy-metal-migration-from-plastic, and cite keyli2019-plastic-packaging-metal-migrationwere searched inwiki/sources/and evidence files; only intake/tracker CSV rows were found. - DOI status: no DOI is printed in the PDF metadata or extracted text. The page uses
doi: nullandno_doi_assigned: true. - Unit fidelity: Tables 4 and 5 label migration values as
µg/kg; the surrounding prose describes Table 4 values asµg/L. I retained the table units for tabular values and explicitly flagged the source-internal conflict rather than converting. - Speciation: arsenic and chromium are not speciated. The source reports elemental ICP-MS leachate results, so frontmatter uses
tAsfor arsenic andCrfor total chromium; no Cr(VI) or inorganic arsenic values are inferred. - Brand firewall: the Shimadzu instrument/vendor name is retained only as method/source identity. No consumer brand names from sampled packaging are reported or attached to values.
- Closed-vocabulary check: product routing uses broad existing plastic packaging rows. Exact PS-container, PP-container, and PE-film forms are retained in the source text and not invented as product slugs.
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 |