Overview
Mandrile and colleagues evaluated surface-enhanced Raman scattering (SERS) for detecting dibutyltin maleate (DTM) and tributyltin chloride (TBT) migrating from intentionally spiked PVC cling film into 3% acetic-acid food simulant. The study is useful food-contact leachate context, but it is not a market-occurrence survey because the PVC films were experimentally additivated. Organotin values are reported as compound-specific DTM/TBT or as tin equivalents and should not be collapsed into total tin or inorganic tin.
Key numbers
- Source identity: Talanta
220(2020) article121408; DOI10.1016/j.talanta.2020.121408; local readable PDF has20pages. - Food-contact matrix: an industrial food-grade PVC cling film described as
10 mm thicknessin the extracted text was dissolved and re-cast after spiking with TBT, DTM, or both compounds. - Regulatory context stated by the authors: for organotin compounds, the specific migration limit was
0.05 mg of tin per kg of food; the paper gives corresponding legal limits of0.15 mg/lfor DTM and0.14 mg/lfor TBT. - Migration test setup:
5 cm2film portions,8.33 mlof3%acetic-acid food simulant, proportional relationship1 dm3simulant per6 dm2packaging,10 daysat40 ºC. - SERS calibration: DTM dynamic range
0-1 mg/lwith reducedχ2 = 0.8; TBT dynamic range0.5-5 mg/lwith reducedχ2 =0.2. - SERS detection limits as described in different parts of the paper: abstract says DTM and TBT were detected down to
0.01 mg/land0.08 mg/l; the Results section reports TBT LOD0.10 mg/land LOQ1.53 mg/l; the conclusion says TBT down to0.1 mg/l. - ICP-MS calibration in
3%acetic acid: DTMR2 0.99, LOD0.005 mg/l, LOQ0.007 mg/l; TBTR2 = 0.99, LOD0.027 mg/l, LOQ0.092 mg/l. - UV-Vis DTM calibration: linear dynamic range
0.1to2.0 mg/l, reducedχ2 = 1.4, LOD0.08 mg/l, and LOQ0.13 mg/l. - Authors’ overall comparison: the organotin migration limit was exceeded for all tested spiked-PVC cases except PVC spiked with low-concentration DTM.
Spiked PVC-film loadings
Table 1 reports the following added organotin and corresponding tin loadings; the paper states uncertainty for all values is 0.1 mg/g.
| PVC sample | mg OTCs/g (PVC) | mg Sn/g (PVC) |
|---|---|---|
| PVC + TBT l.c. | 0.7 | 0.3 |
| PVC + TBT h.c. | 74.1 | 27.0 |
| PVC + DTM l.c. | 0.6 | 0.2 |
| PVC + DTM h.c. | 70.4 | 23.9 |
| PVC + OTCs l.c. (DTM and TBT 50:50) | 0.7 | 0.3 |
| PVC + OTCs h.c. (DTM and TBT 50:50) | 75.0 | 26.1 |
Migration results as compound concentrations
The Results prose reports SERS and UV-Vis compound concentrations in mg/l food simulant:
| Sample and method | DTM | TBT |
|---|---|---|
| PVC + DTM h.c., SERS | 0.41 ± 0.04 mg/l | not applicable |
| PVC + TBT h.c., SERS | not applicable | 10.72 ± 1.11 mg/l |
| PVC + OTCs h.c., SERS | 0.12 ± 0.01 mg/l | 4.16 ± 0.11 mg/l |
| PVC + DTM h.c., UV-Vis | 0.40 ± 0.27 mg/l | not applicable |
| PVC + OTCs h.c., UV-Vis | 0.61 ± 0.41 mg/l | not applicable |
Table 2 migration results as tin equivalents
Table 2 reports mg(Sn)/kg (simulant) by method:
| PVC sample | ICP-MS (mg/kg) | SERS (mg/kg) | UV-Vis (mg/kg) |
|---|---|---|---|
| PVC + DTM l.c. | 0.004 ± 0.001 | > LOD; < LOQ | > LOD; < LOQ |
| PVC + TBT l.c. | 0.049 ± 0.021 | > LOD; < LOQ | - |
| PVC + OTCs l.c. | - | not reported in table cell | > LOD; < LOQ |
| PVC + DTM h.c. | 0.273 ± 0.054 | 0.14 ± 0.02 | 0.14 ± 0.09 |
| PVC + TBT h.c. | 5.70 ± 2.52 | 3,91 ± 0.78 | - |
| PVC + OTCs h.c. | - | DTM 0.04 ± 0.01; TBT 1.52 ± 0.04 | DTM 0.21 ± 0.14; TBT - |
Methods (brief)
The authors prepared spiked PVC films from dissolved PVC cling film and TBT/DTM stock solutions, then performed migration tests into 3% acetic acid under EU food-contact-material simulant conditions. Simulants were analyzed by direct-in-liquid SERS using 30 nm silver nanoparticles, by ICP-MS for tin, and by UV-Vis for DTM. ICP-MS used five tin isotopes (116Sn, 117Sn, 118Sn, 119Sn, 120Sn) with gallium isotopes as internal standards; high-concentration migration samples were diluted at 1:40.
Implications
Certification (HMTc): This paper should be used as food-contact organotin leachate context only. The measurements come from intentionally spiked PVC films and should not be pooled as representative market packaging occurrence, and the TBT/DTM values should remain organotin-specific rather than being converted into total or inorganic tin evidence.
Courses: The source is useful for showing how migration-test design, speciation, and method selectivity interact: SERS can distinguish TBT from DTM, while ICP-MS quantifies tin but cannot by itself distinguish which organotin species produced the signal.
App: If flexible food-packaging organotin context is surfaced, this source can support a method-context warning that PVC food-contact films can release organotin stabilizers under acidic simulant conditions, with the caveat that the tested films were deliberately spiked.
Wiki pages this source may touch
Verification notes
- The readable sibling PDF was extracted with
pdftotext -layoutto/tmp/ingest_alt.txt; abstract, introduction, Materials and method, Table 1, Results, Table 2, Discussion, and Conclusions were checked against this page. - Identity checks before creation: DOI
10.1016/j.talanta.2020.121408, exact title phrase, author surnameMandrile, raw SHA-256cbe37097d9dfadf1d101bec9c7f1368a5889a8f65b7da78774eeb54ec019c1b8, raw handleMFK_migration-study-of-organotin-compounds-from-food-p, and cite keymandrile2020-organotin-food-packaging-serswere searched inwiki/sources/and evidence files; only intake/tracker CSV rows were found. - A corrupt sibling file,
raw/Manual Fetch Kimi /June 8/Kimi_Agent_Download Corruption Issue/_extracted_may31_cat23_food_contact/cat23_food_contact/Migration Study of Organotin Compounds from Food Packaging.pdf, has SHA-256932618e8a420c4204fc21ac9e6c058bc255f1b382c361995b6c1a0a3c9f2fd0a;pdftotextandpdfinfofail with invalid xref/page-tree errors. The readable_2PDF is used as the canonical raw file for this source. - Units are preserved as printed:
mg/l,mg/kg,mg(Sn)/kg (simulant),mg/g,cm2,ml,dm3,dm2, andºC. No conversion to ppb or µg/kg was performed. - Speciation check: the source measures organotin species DTM and TBT and tin-equivalent Sn by ICP-MS. This page does not treat organotins as total tin or inorganic tin.
- The
3,91 ± 0.78SERS value for PVC + TBT h.c. is copied with the source table’s comma decimal mark. - The page records the source’s regulatory migration-limit comparison as context only and does not propose any HMTc threshold.
- Closed-vocabulary check: product routing uses the broad flexible food-packaging films row. No PVC-cling-film product or organotin ingredient slug was invented.
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. When DOI minting comes online (see schema docs), each entry below will also link to a version-pinned DataCite DOI.