De Roma et al. 2017 — Cd, Pb, Hg, and As in prepared meals in Italy
De Roma and colleagues measured cadmium, lead, mercury, and arsenic in prepared meal composites collected in Italy as practical surrogates for dietary-intake assessment. The 17 composites included baby food for toddlers, school canteen meals for children, adult canteen/fast-food/duplicate-portion meals, a vegetarian meal, and restaurant/hotel-school meals. The occurrence table is whole-composite prepared-meal evidence; it does not identify the contaminant concentration of individual menu ingredients. Arsenic and mercury are reported as total elements only, not inorganic arsenic or methylmercury.
Key numbers
Table 1 reports upper-bound contamination of Hg, Pb, Cd, and As in meal composites, expressed as ng g−1:
| Meal composite | tHg | Pb | Cd | tAs |
|---|---|---|---|---|
| BF | 1.69 | < 7.0 | 4.37 | 15 |
| Ferrara | 2.37 | < 7.0 | 8.86 | 155 |
| Perugia | < 1.5 | < 7.0 | 7.82 | 26.9 |
| Portici | 1.72 | < 7.0 | 8.26 | 117 |
| Genoa-1 | 2.07 | < 7.0 | 8.05 | 20.1 |
| Genoa-2 | < 1.5 | < 7.0 | 9.11 | 42.3 |
| Brescia | < 1.5 | <7 | 4.95 | 44.8 |
| FF | < 1.5 | < 7.0 | 9.63 | 16.1 |
| DP | 3.27 | 17.5 | 5.92 | 39.3 |
| V | < 1.5 | < 7.0 | 6.1 | < 15.0 |
| RM-A | < 1.5 | 7.87 | 6.21 | 17.8 |
| RM-B | 14.9 | 21.7 | 27.0 | 326 |
| RM-C | 2.02 | 10.5 | 7.77 | 26.9 |
| RM-D | < 1.5 | 23.1 | 7.64 | < 15.0 |
| RM-E | < 1.5 | 7.66 | 8.86 | < 15.0 |
| RM-F | < 1.5 | 27.0 | 12.9 | 24.3 |
| RM-G | < 1.5 | < 7.0 | 10.8 | < 15.0 |
Table 2 reports upper-bound daily dietary intake from the different composites, expressed as μg kg−1 b.w. day−1:
| Meal composite | tHg | Pb | Cd | tAs |
|---|---|---|---|---|
| BF | 0.40 | 1.50 | 0.96 | 3.64 |
| Ferrara | 0.12 | 0.58 | 0.40 | 6.91 |
| Perugia | 0.08 | 0.58 | 0.36 | 1.26 |
| Portici | 0.08 | 0.34 | 0.39 | 5.19 |
| Genoa-1 | 0.10 | 0.34 | 0.37 | 0.91 |
| Genoa-2 | 0.08 | 0.34 | 0.41 | 1.89 |
| Brescia | 0.03 | 0.27 | 0.09 | 0.83 |
| FF | 0.03 | 0.27 | 0.18 | 0.33 |
| DP | 0.06 | 0.45 | 0.11 | 0.74 |
| V | 0.06 | 0.27 | 0.11 | 0.31 |
| RM-A | 0.03 | 0.15 | 0.12 | 0.33 |
| RM-B | 0.27 | 0.40 | 0.49 | 5.78 |
| RM-C | 0.04 | 0.20 | 0.15 | 0.49 |
| RM-D | 0.03 | 0.42 | 0.15 | 0.28 |
| RM-E | 0.03 | 0.15 | 0.17 | 0.28 |
| RM-F | 0.03 | 0.49 | 0.24 | 0.44 |
| RM-G | 0.03 | 0.14 | 0.21 | 0.28 |
Additional source-reported observations:
- The abstract summarizes estimated intake ranges across surrogate diets as As 0.28-6.91, Cd 0.09-0.96, Pb 0.14-1.50, and Hg 0.03-0.40
μg kg−1 b.w. day−1. - The authors state that cadmium intake from almost all surrogate diets was close to the EFSA TDI of 0.36
μg kg−1 b.w. day−1. - The discussion attributes higher As values in BF, Ferrara, Portici, and RM-B to seafood-containing menus, including homogenised fish, halibut/fried fish, and “risotto alla pescatora”; these are menu-level explanations, not ingredient-specific concentration data.
- The paper states that arsenic speciation was not available and that this limits arsenic risk assessment.
Methods (brief)
Meals were collected in multiple Italian towns across northern, central, and southern Italy. The meals represented baby food for 9-12 month toddlers, school canteen lunches for 4-9 year children, adult canteen meals, fast-food meals, duplicate portions, a vegetarian meal, and restaurant meals from a secondary hotel-school. Samples were weighed, pooled, and homogenized into 17 composites. One gram of each pool was digested with nitric acid and hydrogen peroxide in a microwave system and analyzed by ICP-MS-DRC. Concentrations were expressed on a wet-weight basis as mg kg−1 in the methods and as ng g−1 in Table 1. Upper-bound handling assigned the numerical value of the left-censoring limit to non-quantified results.
Implications
This source contributes Italy-market prepared-meal occurrence evidence for Cd, Pb, total Hg, and total As, especially for infant food composites and mixed meals as consumed outside the home. Because the samples are pooled whole meals, they are useful for prepared-meal and infant-food context but should not be used as direct concentration evidence for individual foods such as fish, rice, or cereal. Total Hg must not be substituted for methylmercury, and total As must not be substituted for inorganic arsenic.
Wiki pages this source may touch
- baby-food
- mixed-meals
- baby-food
- infant-food-general
- mixed-meals-non-rice
- mixed-meals-rice-containing
- cadmium
- lead
- mercury-total
- arsenic-total
Verification notes
- PDF text extracted with
pdftotext -layout; the extracted text contained the title/DOI page, methods, Tables 1-3, discussion, conclusion, and references. - DOI verified from the first page as
10.1016/j.jfca.2017.07.027; DOI, raw-handle, and cite-key checks found no existing source page before creation. - Table 1 and Table 2 values were checked against the extracted text. Units were preserved as printed; no conversion between
ng g−1,mg kg−1, andμg kg−1 b.w. day−1was made. - Speciation: arsenic is total As and mercury is total Hg. The source explicitly notes the lack of arsenic speciation and does not report methylmercury.
- Composite labels are retained as the source prints them: BF, FF, DP, V, RM-A through RM-G, and city-labelled canteen composites. No brand or vendor names are attached to contamination values.
- Frontmatter product and ingredient slugs were checked against
docs/gpt-collaboration/taxonomy-snapshot.md; no new slug was invented.
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 |
|---|---|---|
| 418e6ee | 2026-06-08 | ingest: solidum2013-metro-manila-junk-food-metals fresh from MFK/June 8 New Folder With Items 3 2 |