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Toledo et al. 2024 - Essential and toxic elements in infant cereal, Brazil

Toledo et al. (2024) used published concentration data from Pedron et al. to assess cancer and non-cancer risk from essential and toxic elements in Brazilian infant cereals. The occurrence dataset covers 18 infant-cereal samples bought in 2014-2015 across several Brazilian jurisdictions, with three source groupings: rice cereal, multi-grain cereal containing rice, and non-rice-based cereal. The paper’s added contribution is the deterministic exposure and risk assessment for infants and toddlers aged 4 to <24 months.

Key numbers

Source dataset and analytes:

Source groupingnDescription
Rice cereal9Rice-only infant cereals
Multi-grain cereal containing rice5Rice-and-oat, rice-and-fruit, and rice-and-cornstarch cereals
Non-rice-based cereal4Corn, oatmeal, and non-rice multi-grain cereals

The paper reports total concentrations for Ag, Al, As, B, Ba, Co, Cr, Cu, Mn, Se, Sr, Zn, Ni, Cd, and Pb in Table 3. It also discusses arsenic as total arsenic (tAs) for the full 18-sample set and as inorganic arsenic (iAs) only through source-side speciation assumptions.

Source-reported total arsenic means by cereal grouping:

GrouptAs mean +/- SD
Rice cereal111.37 +/- 43.23 ng/g
Multi-grain cereal containing rice48.13 +/- 46.76 ng/g
Non-rice-based cereal7.86 +/- 4.12 ng/g

Regulatory-comparator outcomes reported by the source:

Scenario or comparatorSource-reported result
iAs assumed to equal 100% of tAs1 of 18 samples (5.5%) above the Brazilian iAs maximum contaminant level; 8 of 18 samples (44.4%) above the US FDA and European Commission iAs comparator of 100 ng/g
iAs assumed to equal 90% of tAs7 of 18 samples (38.9%) above the US FDA and European Commission comparator
iAs assumed to equal 80%, 70%, 60%, and 50% of tAs4 samples (22.2%), 2 samples (11.1%), 1 sample (5.5%), and no samples, respectively, above the US FDA and European Commission comparator
CdUnder the cited maximum contaminant levels in all samples
PbTwo samples above the Brazilian and European Union Pb maximum contaminant levels: one cereal containing rice and oats and one rice-only cereal

Selected cancer-risk outputs:

OutputSource-reported value
Combined iAs + Pb ILCR range across infant cereals1.14 x 10^-6 to 3.99 x 10^-5
Mean ILCR for rice cereal2.6 x 10^-5 +/- 9.7 x 10^-6
Mean ILCR for multi-grain cereal containing rice1.3 x 10^-5 +/- 1.0 x 10^-5
Mean ILCR for non-rice-based cereal2.2 x 10^-6 +/- 8.7 x 10^-7
iAs contribution to total ILCR98.5% to 99.9%
iAs-risk range if iAs is assumed to be 52% of tAs5.9 x 10^-7 to 2.1 x 10^-5
Mean rice-cereal ILCR if iAs is assumed to be 52% of tAs1.4 x 10^-5
Pb ILCR range across infant cereals1.15 x 10^-8 to 8.08 x 10^-8

Selected non-cancer-risk outputs:

OutputSource-reported value
Samples with at least one HQ > 118 of 18
Elements responsible for HQ > 1As, Cd, Cu, Mn, Se, and Zn
Elements most often responsible for HQ > 1Cd, Cu, Mn, and Zn, each in 15 or 16 samples
Element least often responsible for HQ > 1Se, in 3 samples
Proportion of evaluated element-sample combinations with HQ > 181.5% for rice cereal, 52.8% for multi-grain cereal containing rice, and 50.0% for non-rice-based cereal
If iAs is assumed to be 52% of tAsthe number of samples with iAs HQ > 1 remains the same in the source’s iAs sensitivity scenario; the authors state that 10 samples might present human-health risk under that assumption
Elements with HQ < 1 in all evaluated samplesAg, B, Ba, Co, Cr, Ni, Sr, Al, and Pb

The sample-level Table 3 extraction for five structured-extraction analytes (tAs, Al, Ni, Cd, Pb) is retained at data/evidence/category1_toledo2024_infant_cereal_brazil_samples.csv; the source page does not use that extraction as an independent study count.

Methods

Toledo et al. used a deterministic risk-assessment framework with hazard identification, dose-response assessment, exposure assessment, and risk characterization. Exposure was modeled for two age groups: 4 to <12 months and 12 to <24 months.

Risk inputs in Table 1:

Parameter4 to <12 months12 to <24 months
Body weight7.8 kg11.2 kg
Exposure frequency365 days/year365 days/year
Exposure duration0.67 years1 year
Ingestion rate31.2 g/day94.08 g/day

The concentration data came from 18 infant-cereal samples reported by Pedron et al. The source states that total concentrations of 22 elements were determined by ICP-MS and that arsenic speciation used HPLC coupled to the mass spectrometer. For the risk assessment, the authors selected elements with available slope factors or reference doses from IARC, US EPA, OEHHA, ATSDR, FAO, and related agencies. Cancer risk was calculated for iAs and Pb only because those were the two agents with available slope factors in the authors’ framework.

Speciation and methods caveats

  • The full sample set reports total arsenic, not measured sample-by-sample iAs. One Brazilian rice-cereal sample had iAs speciation; the authors cite that iAs was approximately 40% of tAs in that sample.
  • The authors present a conservative scenario where iAs is 100% of tAs, and a lower scenario where iAs is 52% of tAs based on cited infant-cereal literature.
  • Chromium is total Cr only; the paper does not report Cr-VI.
  • Al, Cd, and Ni were not included in the cancer-risk calculation because the authors did not have cancer slope factors for those elements.
  • The Pb reference dose was calculated from a provisional tolerable weekly intake that the source notes had been withdrawn; the authors therefore caution that no Pb exposure level is currently considered safe.
  • The concentration data were originally generated by Pedron et al.; Toledo et al. is the risk-assessment integration paper and should not be double-counted as an independent concentration survey if Pedron et al. is separately ingested.

Implications

Standards work: This source provides Brazilian-market infant-cereal occurrence context and risk-model outputs for rice-based and non-rice dry baby-cereal pages. Its strongest source-specific signal is the contrast between rice-containing cereals and non-rice cereals for total arsenic and modeled iAs risk, with Cd and Pb retained as secondary toxic-element comparators.

Courses: The paper is useful for teaching how speciation assumptions move arsenic risk estimates. The same tAs table can support materially different iAs risk scenarios depending on whether the model assumes 100%, 52%, or another fraction of total arsenic is inorganic.

App: The Table 3 sample extraction can support jurisdiction-labeled Brazilian occurrence context for baby-cereal displays, but it should be labeled as Brazilian-market data acquired in 2014-2015 and as a small sample set.

Wiki pages updated on ingest

Verification notes

  • Merge-enhanced 2026-05-18 from the full manual-fetch PDF path and SHA-256 recorded in frontmatter, while retaining the earlier JATS and sample-extraction paths.
  • Fresh-context audit (Codex, 2026-05-18) caught an ambiguous 52% iAs non-cancer-risk row; clarified that the unchanged HQ count refers to the source’s iAs sensitivity scenario and the authors’ 10-sample risk statement, not the overall 18-of-18 all-element count.
  • Removed the unsupported Sn frontmatter metal from the older page; tin appears in the Brazilian infant-food regulation background but was not one of the paper’s reported infant-cereal concentration analytes.
  • Replaced older cross-study HMTc comparison prose with source-only risk-assessment results to preserve the wiki/HMTc firewall.
  • Strict brand-firewall check: the source says the 18 samples came from eight brands, but this page does not name or rank any sampled brand.

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.

CommitDateDescription
b0f3d382026-06-12batch | corpus rescreen b04 old terminal skips