Overview
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 aluminum (Al), arsenic (As), cadmium (Cd), Co, Mn, nickel (Ni), and Sb or200 ppbfor Ba, chromium (Cr), Cu, Fe, Li, lead (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 |
|---|---|---|---|---|
| aluminum (Al) | 49.3 | 71.4 | 135.5 | 2.01 |
| arsenic (As) | 0.11 | 0.06 | 0.48 | 0.05 |
| Ba | 14.0 | 7.14 | 22.9 | 0.05 |
| cadmium (Cd) | N.D. | N.D. | 0.26 | 0.012 |
| Co | N.D. | N.D. | N.D. | 0.006 |
| chromium (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 |
| nickel (Ni) | 8.81 | 1.86 | 2.14 | 0.67 |
| lead (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 |
|---|---|---|---|
| aluminum (Al) | 21.0 | 29.9 | 135.5 |
| arsenic (As) | 0.01 | 0.15 | 0.48 |
| Ba | 13.4 | 15.8 | 22.9 |
| cadmium (Cd) | N.D. | 0.05 | 0.26 |
| Co | N.D. | N.D. | N.D. |
| chromium (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 |
| nickel (Ni) | 0.91 | 1.37 | 2.14 |
| lead (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.
Related evidence
- Plastic tubs
- Flexible pouches/films
- Aluminum
- Arsenic, Total
- Barium
- Cadmium
- Chromium
- Cobalt
- Copper
- Iron
- Lithium
- Manganese
- Nickel
- Lead
- Antimony
- Zinc
Update history
The five most recent substantive edits to this page, classified major (evidence or structure moved), correction (a published value or statement was wrong and has been fixed), or minor (narrative rewritten without changing the underlying evidence). Each description is derived from what the edit did to this page; the linked commit is the authoritative record, routine regeneration passes are excluded, and the full version history lives in git.
| Commit | Date | Change | Description |
|---|---|---|---|
| b01ec52c31 | 2026-08-04 | major | 1 section added |
| 3171d069e3 | 2026-08-02 | major | 1 section added |
| 90a2f9a38e | 2026-07-30 | major | 1 section added and 1 removed; narrative text revised |
| eaa8eeeedf | 2026-07-27 | major | 1 section added |
| 50de6ab217 | 2026-07-27 | minor | Narrative text revised |
