Blunden & Wallace 2003 — Tin in canned food: occurrence and effect review
Blunden and Wallace (ITRI Ltd, UK) review the literature on tin dissolution from tinplate food and beverage cans, surveyed occurrence values in retail canned foods, published acute clinical and human-incident reports of gastrointestinal effects following ingestion of tin-rich canned products, and the chronic-effect and absorption literature for divalent inorganic tin. The review’s central conclusion is that adverse gastrointestinal effects have been clinically documented at tin concentrations of approximately 700 mg/kg and above in canned foods or beverages, but that two human studies at higher concentrations reported no adverse effects, and that no published reports of acute adverse effects attributable to tin contamination in the 100-200 mg/kg range have appeared in the 25 years preceding the review. The authors estimate that approximately 4% of UK plain (unlacquered) tinplate food cans contain over 150 mg/kg tin and infer that the contents of roughly 25 million such cans containing at least 150 mg/kg tin are consumed annually in the UK alone without published acute-effect reports. The review supports the position that tin contamination at concentrations up to about 200 mg/kg in canned products is not associated with reported acute gastrointestinal effects, while noting that controlled clinical studies at these concentrations are absent. ITRI Ltd is the tin-industry research institute and the sponsorship context of the review is relevant when interpreting its overall framing.
Key numbers
Tin can production and use (pp. 1651-1652)
| Quantity | Reported value | Source cited in review |
|---|---|---|
| European food cans produced and filled per annum | ~25,000 million | Review’s own industry data |
| Worldwide food cans per annum | ~80,000 million | Review’s own industry data |
| Proportion of European food cans with plain (unlacquered) internal tin surface | ~20% | Review |
| European beverage cans per annum | >15,000 million tinplate (all internally lacquered) | Review |
| UK plain (unlacquered) tinplate food cans containing ≥150 mg/kg tin | ”almost 4%“ | MPMA, 2000 |
| UK plain (unlacquered) tinplate food cans per annum | ~2,500 million | MPMA, 2000 |
| Implied UK cans containing ≥150 mg/kg tin consumed per annum | ~25 million can contents | Review’s arithmetic |
Regulatory limits cited (p. 1653, Section 2)
| Limit body | Analyte | Matrix | Value | Cite in review |
|---|---|---|---|---|
| JECFA | Total tin | All sources | PTWI 14 mg/kg body weight | JECFA, 1988a, 1988b |
| Codex | Total tin | Solid foods | 250 mg/kg recommended maximum (200 mg/kg UK) | Codex, 1998; MAFF, 1992 |
| Codex | Total tin | Beverages | 150 mg/kg recommended maximum | Codex, 1998 |
| UK statutory | Total tin | Canned fruit and vegetables | 200 mg/kg | MAFF, 1999a, 1999b; FSA, 2002 |
Occurrence in canned foods (Section 4)
Table 1 of the review (p. 1654, citing Ratana-Ohpas et al. 1996) reports concentrations of total tin in conserves of acidic fruit:
| Fruit | Tin concentration (mg/l) |
|---|---|
| Guava | 49.8-59.4 |
| Lychee | 43.9-45.7 |
| Tomato | 59.7-69.7 |
| Mango | 64.3-77.4 |
| Pineapple | 57.8-69.1 |
Additional occurrence values cited in the review body:
| Population / matrix | Reported tin value | Source cited in review |
|---|---|---|
| French daily dietary tin intake | 2.7 mg/day, or 0.04 mg/kg bw/day | Biégo et al., 1999 |
| Fresh food | 0.03 mg/kg | Biégo et al., 1999 |
| Food in lacquered cans | 3.2 ± 2.3 mg/kg | Biégo et al., 1999 |
| Food in unlacquered cans | 76.6 ± 36.5 mg/kg | Biégo et al., 1999 |
| USA unlacquered (or partially lacquered) cans of grapefruit juice, orange juice, tomato sauce, and pineapple at can-opening | 51-150 mg/kg; mean across unlacquered cans 88 mg/kg | Greger and Baier, 1981 |
| UK canned pineapple survey, Jan-Mar 1999 | 50 mg/kg to 210 mg/kg | MAFF, 1999a |
| UK 2002 FSA repeat survey of canned fruit and vegetables | All but two samples (gooseberries) below 200 mg/kg statutory limit; mean 59 mg/kg across 234 unlacquered-can samples | FSA, 2002 |
| UK 1994 Total Diet Study | Canned vegetables contributed 66%, canned fruit 31% of 2.4 mg/day estimated total tin intake | MAFF, 1997 |
Storage-temperature effect on tin dissolution (Section 3, citing Calloway and McMullen, 1966)
| Matrix | Storage temperature comparison | Reported tin concentration after 20 months |
|---|---|---|
| US military rations, five fruit types, unlacquered cans | 37 °C versus 1 °C | 420 mg/kg vs 34 mg/kg (~12-fold increase) |
| US military rations, seven mixed-dish types, unlacquered cans | 37 °C versus 1 °C | 190 mg/kg vs 32 mg/kg (~6-fold increase) |
Acute clinical studies (Section 6.1.1, Primary reports)
| Study population | Tin concentration | Outcome | Source cited in review |
|---|---|---|---|
| 5 adults, 240 ml orange juice, pH 3.9 (no-nitrate arm) | 0, 498, 540 mg/kg | No overt adverse effects (review describes lower concentrations as “apparently without effect”) | Benoy et al., 1971 |
| 5 adults, 240 ml orange juice, pH 3.9 (nitrate-supplemented arm) | 730 mg/kg tin + 50 mg/kg nitrate | No overt adverse effects | Benoy et al., 1971 |
| 5 adults, 240 ml orange juice, pH 3.9 (no-nitrate arm) | 1,370 mg/kg | Nausea and/or diarrhoea in all 5; on re-administration one month later, nausea in 1 of 5 | Benoy et al., 1971 |
| 9 US Army personnel, 24 days, canned combat rations stored at extreme temperatures | Daily menus 99 (72-125) to 310 (273-356) mg/kg dry solids; average daily intake 162.8 mg (115.8-206.7) | No gastrointestinal effects specifically mentioned in the study report | Calloway and McMullen, 1966 |
| 8 men, 20 or 40 days, dietary tin 49.67 mg/day | ~50 mg/day total intake | No overt gastrointestinal effects | Johnson and Greger, 1982; Johnson et al., 1982 |
Acute clinical studies (Section 6.1.2, Secondary reports)
| Study population | Tin concentration | Outcome | Source cited in review |
|---|---|---|---|
| 4 participants, 6 days canned pumpkin and asparagus | Pumpkin 383-476 mg/kg, asparagus 361 mg/kg | No overt adverse effects | Dack, 1955 |
| 8 subjects, tomato-vegetable juice mixture (unpublished) | 700 mg/kg | Nausea in 2, nausea/diarrhoea in 2 | Cheftel, 1967 |
| Same 8 subjects, pH 4.5 citrate buffer with stannous chloride before meal | 700 mg/kg | Nausea/vomiting in 2, diarrhoea in 1 | Cheftel, 1967 |
| Unspecified number of volunteers | Fruit juice 342 mg | Gastrointestinal irritation symptoms | MAFF, 1983 |
| Same volunteers | Similar juice 125-182 mg | No effect | MAFF, 1983 |
Acute episode reports (Section 6.2)
Reported general dose range associated with episode reports: 250-2,000 mg/kg, predominantly in acidic fruits and fruit juices. Symptom frequency (combined across reports): nausea 97%, abdominal cramps 87%, vomiting 70%, headaches 57%, diarrhoea 33%, fever 13%. Incubation 15-30 minutes, duration 30 minutes to 3 weeks (Piscator, 1979; Schafer and Femfert, 1984; Dewitte et al., 2001; Barker and Runte, 1972).
| Episode | Tin concentration | Affected | Source cited in review |
|---|---|---|---|
| Swedish meeting, canned peaches | Fruit 413-597 mg/kg, juice 398 mg/kg, pH 3.9-4.1 | 76 of 85 respondents (89%) had GI symptoms; 95% of those eating ≥220 g | Svensson, 1975 |
| Washington/Oregon canned tomato juice, 1969 | 327-392 mg/kg (4 banquets, unopened can analyses) and 154-289 mg/kg (family outbreaks); 4 opened cans from family outbreaks 131-405 mg/kg | 113 cases over 3 months: two banquets with 43 and 22 cases respectively (~65% of those consuming juice at banquets affected); 30 family outbreaks (48 of 49 = 98% affected) | Barker and Runte, 1972 |
| Subsequent samples implicated lots | 227-294 mg/kg (partially detinned) to 381-477 mg/kg (completely detinned) | Detinning attributed to elevated nitrate (or sodium chlorate) | Barker and Runte, 1972 |
| Peaches | Fruit 350-600 mg/kg, liquor 220-440 mg/kg | Nausea/vomiting in 91 of unknown total | Nehring, 1972 |
| Canned peaches | ≥100 mg tin total dose | 74 of 78 GI disturbances | Piscator, 1979 |
| Canned peaches | 50 mg tin total dose | 2 of 7 GI disturbances | Piscator, 1979 |
| Repeated ingestion 3 × 24 days, 9 volunteers | 13, 33, 204 mg tin per ingestion from canned foods | No signs of toxicity | Piscator, 1979 |
| Volunteers, fruit juice | 500 mg/l | No signs | Piscator, 1979 |
| Volunteers, fruit juice | 1,370 mg/l | Digestive disturbances | Piscator, 1979 |
| Orange/grapefruit juice | 330-400 mg/kg | GI effects in unspecified consumer number | Anon., FDA Consumer, 1986 |
| Grapefruit juice, visibly corroded cans | 450 mg/kg | GI effects | Anon., The Guardian, 1972 |
| Orange juice | 100-494 mg/kg | At least 15 students with GI symptoms | Horio et al., 1967; JECFA, 1971, 1982 |
| Orange drink, Japan (Omori 1966) | 425-452 mg/kg (figures differ between reports) | 1,838 affected | Omori, 1966 |
| Orange and apple juice, Kuwait | 250-385 mg/kg | ”Large but unspecified” number | Metal Box Co., 1967 |
| Tomato juice (Kojima 1969) | 156-247 mg/kg (cited concentration); samples from same maker 75-500 mg/kg | 8 affected | Kojima, 1969 |
| Tomato juice (Horio 1967) | 156-221 mg/kg | 8 of 10 affected | Horio et al., 1967 |
| Vodka punch with pineapple/grapefruit juice, pH 3, retinned container | 2,000 mg/kg | 32 with severe GI | Warburton et al., 1962 |
| Canned salmon | 650 mg/kg | Family of 3 affected (vomiting, weakness, diarrhoea or abdominal pain) | Kwantes, 1966 |
| Canned rhubarb in school canteen | 350 mg/kg | 64 of 127 students affected | Kwantes, 1966 |
Non-human oral studies (Section 6.2.3, Table 2)
Acute oral LD50 of divalent inorganic tin compounds:
| Compound | Species | LD50 (mg/kg bw) | Source |
|---|---|---|---|
| Stannous chloride | Mouse | 1,200 | Pelikan et al., 1968 |
| Tin-citric acid complex (30% tin) | Mouse | 2,700 | Omori et al., 1973 |
| Sodium pentafluorostannate (67% tin) | Mouse | 590 | Conine et al., 1975 |
| Stannous chloride | Rat | 700 | Calvery, 1942 |
| Stannous chloride | Rat (fasted) | 2,300 | Conine et al., 1975 |
| Stannous chloride | Rat (fed) | 3,200 | Conine et al., 1975 |
| Sodium pentafluorostannate (67% tin) | Rat (fasted, F) | 220 | Conine et al., 1975 |
| Sodium pentafluorostannate (67% tin) | Rat (fasted, M) | 220 | Conine et al., 1975 |
| Sodium pentafluorostannate (67% tin) | Rat (fed, M) | 570 | Conine et al., 1975 |
| Stannous chloride | Rabbit | 10,000 | HSDB, 1999; JECFA, 1982; RTECS, 1999; WHO, 1980 |
Cats given orange juice containing 540 or 1,370 mg/kg tin by stomach tube at 5 or 10 ml/kg bw showed vomiting; apple juice at 605 mg/kg and pear nectar at 750 mg/kg were not emetic (Benoy et al., 1971). A Japanese study reported vomiting in 5 of 6 cats given 10 ml/kg bw orange juice at 452 mg/kg tin but not at 337 mg/kg (Omori et al., 1973).
Chronic effects and absorption (Section 7)
| Finding | Reported value | Source cited in review |
|---|---|---|
| Diet causing zinc-metabolism effects | ~50 mg tin/day for 40 days | Johnson et al., 1982 |
| Oral absorption of Sn²⁺ in humans (high-tin diet, 49.7 mg/day, 20 days) | ~3% (range -7% to +9%) | Johnson and Greger, 1982 |
| Oral absorption at low daily diet, 0.1 mg/day | ~27% (range -4% to +71%) | Johnson and Greger, 1982 |
| Inorganic tin in faeces of humans/animals | >90% of administered dose | ATSDR, 1992; Codex, 1998; COT, 1998; JECFA, 1982; Fritsch et al., 1977; Haguenoer and Furon, 1982; Hiles, 1974; Kutzner, 1971; Piscator, 1979; WHO, 1996; Winship, 1988; Tipton, 1969 |
| Rat single 20 mg Sn²⁺/kg bw oral dose absorption | ~3%, half excreted within 48 h | Hiles, 1974 |
| Rat 1.02% Sn²⁺ vs 4% Sn⁴⁺ retention in bones (oral) | Bones 1.02% / 4%; liver 0.08% / 0.02%; kidney 0.09% / 0.02% | Haguenoer and Furon, 1982; Piscator, 1979 |
| Rat IV inorganic tin retention 2 days post-injection | 35% Sn²⁺, 46% Sn⁴⁺ | Haguenoer and Furon, 1982; Piscator, 1979 |
| Bone half-life in rat | 34 days (Sn²⁺), 40 days (Sn⁴⁺) | Piscator, 1979 |
| ¹¹³Sn kidney/liver clearance in rat | 10-20 days | Piscator, 1979 |
| Human clearance phases (three-phase) | First 20% with half-life 4 days; second 20% with half-life 25 days; final 60% with half-life ~400 days | Winship, 1988 |
| Rat biological half-life | Bone 30-40 days; spleen 50 days; liver 85 days | Codex, 1998; JECFA, 1982; WHO, 1996 |
| Inorganic tin absorption (overall) | 2.8% for Sn²⁺ compounds, 0.64% for Sn⁴⁺ compounds | Review’s overview statement |
Overview-section worst-case dose calculation (Section 8)
If all canned foods and beverages contained 200 mg/kg tin and a 1 kg daily diet consisted of 4-8% canned foods (MAFF 1998), average daily intake would be 8-16 mg/day or 0.13-0.3 mg/kg bw/day for a 60 kg adult, which is approximately 7-fold below the JECFA reference of 2 mg/kg bw/day (the daily equivalent of the JECFA Provisional Tolerable Weekly Intake of 14 mg/kg body weight per week; JECFA 1988a, 1988b). The UK is described as the highest per capita European consumer of canned food and the largest consumer of plain unlacquered cans (~2,500 million annually, MPMA 2000); approximately 4% probably contain at least 150 mg/kg tin, implying contents of ~25 million such cans containing this concentration are consumed annually in the UK without published acute-effect reports in the prior 25 years.
Evidence Fitness
This is a narrative literature review without explicit search-and-selection protocol or PRISMA-style inclusion criteria, sponsored by ITRI Ltd (the International Tin Research Institute). It contributes no primary heavy-metal measurements and no occurrence distributions of its own; all quantitative figures it presents are second-hand summaries of the underlying primary studies that should be obtained as primary evidence. Public evidence label “Context only” is appropriate.
The source supports literature-context claims about (i) the magnitude and variability of tin dissolution from unlacquered tinplate into canned acidic foods and beverages, (ii) the approximate concentration threshold (700 mg/kg and above) at which controlled clinical studies have detected acute gastrointestinal effects from divalent inorganic tin, (iii) the absorption-limited and local-irritation mechanism of inorganic tin GI effects, and (iv) the historical regulatory framework (JECFA PTWI 14 mg/kg bw, Codex 250 mg/kg solid / 150 mg/kg beverage, UK 200 mg/kg statutory). It should not be used as the basis for HMTc threshold work for tin in canned product categories, which should reference the primary occurrence studies (Biégo 1999, Greger and Baier 1981, Ratana-Ohpas 1996, MAFF/FSA UK surveys) and the primary clinical studies (Benoy 1971, Calloway and McMullen 1966, Johnson 1982) directly, and should account for the review’s industry-sponsored framing when interpreting its overall position.
Methods (brief)
Narrative literature review with no stated search strategy, inclusion/exclusion criteria, quality appraisal, or quantitative pooling. The authors restrict the review (with stated exceptions for particular relevance) to reports published after 1970, citing changes in can-making technology (elimination of soldered side-seams, improvements in filling procedures) as the rationale for the cutoff. The review organises evidence into seven thematic sections: introduction and packaging context, background tin chemistry, factors affecting tin dissolution, surveyed levels in foods, toxicology overview, acute effects (clinical studies and consumption episodes), and chronic effects (including absorption, distribution and excretion). No new measurements are reported. Quantitative figures in tables and prose are reproduced verbatim from cited primary sources.
Implications
Certification: Process and toxicology context only. The review supports the general claim that tin in canned acidic foods and beverages is associated with acute gastrointestinal irritation at concentrations of approximately 700 mg/kg and above in controlled studies, with episode reports at 250-2,000 mg/kg, and that the JECFA PTWI of 14 mg/kg bw/week is approximately 7-fold above the worst-case daily intake estimable from a diet at the 200 mg/kg statutory limit. HMTc threshold-setting for tin in canned product categories should reference the primary occurrence and clinical studies directly rather than this review, and should treat the review’s “little evidence of acute effects at up to 200 mg/kg” framing with the caution appropriate to industry sponsorship.
Courses: A useful entry point to the tin-canned-food acute-effect literature for course modules covering the local-irritation versus systemic-absorption distinction (tin is one of the few heavy metals where the principal acute effect is gastrointestinal irritation and absorption is below ~3% for divalent forms), the relationship between can construction (unlacquered tinplate, nitrate-driven detinning, storage temperature) and tin migration, and the regulatory landscape for tin in canned foods. The review provides convenient pointers to the primary studies and should be presented to learners alongside source-sponsorship context.
App: No ingredient contamination_profile impact directly from this review. Per-product caution flags for canned acidic juices and fruits in unlacquered tinplate, particularly after extended storage at warm temperatures, are supported by the underlying primary literature this review compiles.
Wiki pages this source may touch
- tin
- tin-inorganic
- tomato
- canned-tomatoes
- orange-juice
- grapefruit-juice
- pineapple
- peach
- asparagus
- guava
- mango
- canned-foods-general
- canned-fruit
- canned-tomatoes
- canned-vegetables
- fruit-juices-non-apple
- fruit-juices-apple-containing
- codex-cxs-193-1995-tin-canned-foods
Verification notes
- 2026-06-04 fresh ingest (Claude Opus 4.7, manual-fetch ingest from
raw/Manual Fetch Kimi /June 3 Folder/): DOI 10.1016/S0278-6915(03)00217-5 verified against the article’s first page; received 24 April 2003, revised 1 July 2003, accepted 5 July 2003; published in Food and Chemical Toxicology 41 (2003) 1651-1662. The article is an Elsevier copyrighted review (no Creative Commons licence statement on the PDF); recorded as subscription-access. SHA256 of the source PDF recorded in frontmatter. - Author affiliation: ITRI Ltd, Unit 3, Curo Park, Frogmore, St Albans, Hertfordshire AL2 2DD, UK. ITRI Ltd is the International Tin Research Institute, the trade-funded research body of the tin industry. The review acknowledges assistance from APEAL (European Steel Association), Ledepp-Arcelor Group, BIBRA International, Crown Cork & Seal, Shell International, and others. The sponsorship context is preserved in the page text (Evidence Fitness and Implications sections) so downstream readers can weight the review’s framing accordingly. This is a structural source-context disclosure, not a brand attribution to a contamination value; it does not violate Part 12.
- Evidence tier B reflects the narrative-review character of the source (no primary measurements, no PRISMA protocol, no quality appraisal of cited primary studies, industry sponsorship).
evidence_fitness: EF-4andpublic_evidence_label: Context onlyreflect that the review contributes no occurrence values usable for HMTc threshold work. - No brand names are reported in the review’s body content for canned foods being measured (the implicated products are described by category: canned peaches, canned tomato juice, canned salmon, canned rhubarb, orange juice, grapefruit juice, etc.). The review does name two industrial container vendors in the Acknowledgements (Crown Cork & Seal, Shell International) and the Metal Packaging Manufacturers Association data source (MPMA 2000); these are not brand-attributions of contamination values and are retained only as bibliographic context.
- The Kuwait outbreak (Metal Box Co., 1967) and the Washington/Oregon canned tomato juice incident (1969, Barker and Runte 1972) are public-record regulatory events documented in the review. Brand names are not provided in the review for these episodes; the review uses geographic and product-form descriptors throughout.
- Speciation convention: the review treats inorganic tin (divalent Sn²⁺ as primary, with Sn⁴⁺ noted for absorption studies) throughout; organotins are explicitly excluded as outside the scope of canned-food tin migration (Section 5, p. 1655). Frontmatter records
Snonly withspecies: [Sn2+, Sn4+]. jurisdictions: [UK, EU, US, international]reflects the geographic scope of cited primary studies: UK MAFF/FSA surveys, EU/European production figures, US FDA/Greger/Calloway data, JECFA international guidance.matrices: [canned-food, canned-beverage, canned-fruit-juice]follows the convention established byeu-scf-2002-acute-tin-canned-foods.mdandjecfa-64th-cadmium-tin-2006.md.- Ingredient slug selection: only slugs that exist in the current taxonomy are referenced. The review names canned products of pumpkin, salmon, rhubarb, and gooseberries that do not have current ingredient pages; these are not invented as new slugs here and will be picked up by the routing layer if and when those pages are created (see auto-stub policy in CLAUDE.md Part 10).
- Product slug selection:
canned-foods-generalfor the umbrella scope, plus the specific product slugs that the review’s evidence supports (canned-fruit, canned-tomatoes, canned-vegetables, fruit-juices-non-apple, fruit-juices-apple-containing).canned-fishandcanned-seafoodare not added despite the canned-salmon episode (Kwantes 1966) because tin migration from modern fish cans is generally low and the review does not develop the fish-can occurrence picture beyond the one salmon outbreak; over-broad product fan-out would weaken row-fit downstream. - The review’s Section 8 “200 mg/kg up to 200 mg/kg” framing — that there is “little evidence” for an association between canned-food tin at concentrations up to 200 mg/kg and acute GI effects — is preserved in the page as the review’s own claim, with the industry-sponsorship caveat. This is the literature-native view; HMTc threshold-setting work should evaluate this position alongside the primary clinical and outbreak evidence (some of which is below 250 mg/kg, e.g., the 156-247 mg/kg Kojima 1969 tomato juice episode and 154-289 mg/kg family outbreaks in Barker and Runte 1972) directly rather than relying on the review’s interpretation.
- 2026-06-04 fresh-context audit (general-purpose subagent) — verdict REVISE. Applied findings:
- Benoy et al. 1971 dose-structure correction (Check 1 ❌): Audit subagent flagged that the Key Numbers Acute Clinical row had merged the no-nitrate arm (0, 498, 540, 1370 ppm tin) with the nitrate-supplemented arm (730 ppm tin + 50 mg/kg nitrate). Verified against PDF p. 1655 (“0, 498, 540 or 1370 ppm tin, or 730 ppm tin and 50 ppm nitrate … Nausea and/or diarrhoea were reported by all participants, following ingestion of the highest tin concentration. Lower concentrations were apparently without effect.”). Corrected: split into three rows showing no-nitrate-no-effect (0/498/540), nitrate-supplemented-no-effect (730 + 50 nitrate), and high-dose-effect (1370).
- Barker and Runte 1972 banquet-count framing (Check 1 ❌): Audit flagged that “(43, 22 affected)” was misleading — PDF p. 1656 reports these as total cases at the two banquets, not affected counts; the ~65% affected applies separately. Corrected the row to read “43 and 22 cases respectively (~65% of those consuming juice at banquets affected)“.
- Johnson and Greger 1982 absorption-range sign error (Check 1 ❌): Audit flagged that the wiki had written the absorption ranges with multiple negative signs (“range -7 to -9 to +9%” and “range -4 to -71%”). Verified against PDF p. 1658 (“the range was −7-9%” and ”(−4-71% of dose)”); the en-dash is a range separator and the second number is positive. Corrected to “(range -7% to +9%)” and “(range -4% to +71%)“.
- Winship 1988 human clearance phases (Check 1 ❌): Audit flagged that the wiki wrote “First 20% in 4 days; second 20% in 25 days” but the PDF p. 1658 reports half-lives (“The first 20% is cleared with a half-life of 4 days and the second 20% with a half-life of 25 days. The final 60% has a much longer half-life of 400 days”). Corrected to “First 20% with half-life 4 days; second 20% with half-life 25 days; final 60% with half-life ~400 days” — the half-life-versus-clearance-time distinction matters because the half-life expresses an exponential-decay parameter, not a complete-elimination time.
- JECFA “PTWI of 2 mg/kg bw/day” unit basis (Check 1 ⚠️): Audit flagged that calling 2 mg/kg bw/day a “PTWI” confuses units. The PTWI is the weekly value (14 mg/kg bw/week, per JECFA 1988a, 1988b); the 2 mg/kg bw/day is its daily equivalent (14 ÷ 7). PDF Section 8 (p. 1659) actually says “current JECFA figure of 2 mg/kg body weight/day” rather than “PTWI.” Corrected the Overview-section paragraph to refer to “the JECFA reference of 2 mg/kg bw/day (the daily equivalent of the Provisional Tolerable Weekly Intake of 14 mg/kg body weight per week)“.
- Greger and Baier 1981 matrix labelling (Check 1 ⚠️): Audit flagged that the wiki listed matrices as “grapefruit, orange, tomato sauce, pineapple” while PDF p. 1654 has “grapefruit juice, orange juice, tomato sauce and pineapple in unlaquered or partially lacquered cans”. Corrected to “grapefruit juice, orange juice, tomato sauce, and pineapple” and added the “partially lacquered” qualifier.
- 2026-06-04 audit findings rejected as false positives:
- Check 2 invented slugs (audit ❌; false positive): Audit claimed
ingredients/pineappleandproducts/canned-foods-generalare not in the current taxonomy and were invented. Verified against the live filesystem:wiki/ingredients/pineapple.mdandwiki/products/canned-foods-general.mdboth exist as real wiki pages. The audit subagent appears to have read a stale or partial copy ofdocs/gpt-collaboration/taxonomy-snapshot.mdthat does not reflect the current ingredient and product directories. Slugs retained without change. - Check 1 European beverage cans figure (audit ⚠️; clarification rather than correction): Audit noted that the abstract says “15,000 million tinplate beverage cans” while the body (p. 1652) says “approximately 40,000 million [beverage] cans per annum, of which almost half are made of tinplate and all are internally lacquered.” The wiki’s row “European beverage cans per annum: >15,000 million tinplate” matches the abstract and is consistent with “almost half of ~40,000 million total” in the body. The two figures are not in conflict; they refer to total beverage cans (40,000 million) and tinplate beverage cans specifically (>15,000 million). No correction applied.
- Check 1 cat-dose orange juice “498 ppm not emetic” omission (audit ⚠️; clarification only): Audit noted that the page omits the PDF detail that 498 ppm orange juice did not produce emesis in cats and that dogs (groups of four) did not vomit at 540 or 1370 ppm. Omission rather than error; the page’s purpose is to summarise tin-occurrence and acute-effect ranges, not reproduce every animal-dosing data point. Not applied; flagged here for future readers.
- Check 2 invented slugs (audit ❌; false positive): Audit claimed
- Audit-application summary: 6 ❌/⚠️ findings applied (Benoy dose structure; Barker-Runte case framing; Johnson-Greger absorption sign; Winship half-life framing; JECFA PTWI unit basis; Greger-Baier juice labelling); 2 findings rejected as false positives (invented-slug claim contradicted by filesystem; European-beverage-can figure consistent with abstract). Subagent’s other ✅ confirmations on Checks 3 (speciation/methods), 4 (Part 12 brand firewall — sponsorship-context disclosure correctly handled), and 5 (Part 2 wiki/HMTc firewall — source-attribution framing correctly preserved) recorded.
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 |
|---|---|---|
| 9c0b0a7 | 2026-06-05 | codex fire 2026-06-05: no unclaimed auto-fetched pdfs |