Baby Cereals / Grain Products, Dry (Non-Rice)
This page is a structural scaffold for HMTc Category 1 row 5. FDA compliance samples now provide a direct non-rice dry-cereal lower-bound distribution, while broader cereal and infant-food sources remain useful context.
Who this page is for
Heavy Metal Index pages are written for several audiences at once. Each entry point below names where to start if you are reading this page with a specific question in mind.
- Brand legal and regulatory affairs
- Cherry-pick attack vectors on non-rice cereal typically center on lead and cadmium in grain bases (oats, wheat, barley) where soil-uptake and harvest-year variance is wide. The Methodology section's basis preservation rule (dry cereal vs prepared) is the defensive core. Compare with Baby Cereals Dry Rice Based for the within-pair sibling. The cited sources at the bottom of this page are the citations list, written to be quoted into a Daubert brief without further editing.
- Retailer quality and compliance
- The Federal / Regulatory Limits vs Field Findings section compares the applicable regulatory cap to cited field evidence on a like-for-like basis, with basis conversion shown when conversion is well-defined and a methodology anchor when speciation differs. The Literature Evidence Summary gives source count and confidence rating per analyte.
- Brand QA and product development
- Use the Lab Result Comparator to position a single lab value inside the cited literature. The comparator positions a single lab value inside the cited literature for non-rice cereal grains, against the FDA 2025 dry-cereal cap.
- Regulators, journalists, and adversarial readers
- Every numeric claim on this page traces to a source page. The Evidence Governance note explains what this page is and is not (literature evidence, not HMT&C certification thresholds).
- HMT&C staff (internal)
- The threshold-selection arithmetic (percentile statistics, clean / dirty subcategory designation, CC eligibility) lives on the staff workbench snapshot at baby-cereals-dry-non-rice, not on this public page.
This is the fast comparison view for standards developers, regulators, retailers, brands, and legal teams. It shows the applicable federal or regulatory limit next to the current field-evidence state. It is not an HMTc pass/fail table; technical distributions remain in the evidence sections below.
| Metal | Federal / regulatory limit | Actual field finding | Decision read | Evidence |
|---|---|---|---|---|
| lead (Pb) | fda2025-lead-processed-baby-foods: Federal FDA final action level: 20 ug/kg Pb. Scope: dry infant cereals for children under 2. Basis: dry infant cereal. | Promoted field evidence exists, but comparable product-row values have not been extracted yet. | Regulatory value loaded; field-finding comparison blocked until structured occurrence rows are extracted. | fda2025-lead-processed-baby-foods; fera2014-fsa-metals-infant-foods-formula |
| lead (Pb) | eu2023-contaminants-maximum-levels: EU European Commission maximum level: 20 ug/kg Pb. Scope: baby food and processed cereal-based food for infants and young children, except covered infant drinks and formula/medical foods. Basis: product as placed on market. | Promoted field evidence exists, but comparable product-row values have not been extracted yet. | EU maximum level loaded; field-finding comparison blocked until structured occurrence rows are extracted and EU product scope is confirmed. | eu2023-contaminants-maximum-levels; fera2014-fsa-metals-infant-foods-formula |
| cadmium (Cd) | eu-2023-915-cadmium: EU European Commission maximum level: 40 ug/kg Cd. Scope: baby food and processed cereal-based food for infants and young children. Basis: product as placed on market. | Promoted field evidence exists, but comparable product-row values have not been extracted yet. | EU maximum level loaded; field-finding comparison blocked until structured occurrence rows are extracted and EU product scope is confirmed. | eu-2023-915-cadmium; fera2014-fsa-metals-infant-foods-formula |
Evidence Governance
Public evidence label: Modeled or limited evidence.
This page is part of the Category 1 Evidence Fitness pilot. It summarizes source-backed occurrence evidence, partial distributions, and data gaps for this product row. Existing cited tables remain public page-level synthesis; value-level tracking is maintained in the staff Standards Workbench.
This page does not publish or justify HMT&C certification limits. Public Index pages show what the cited sources say, what is still uncertain, and where readers can verify the evidence trail.
Literature Evidence Summary
The table below summarizes what the peer-reviewed and government literature cited on this page reports for heavy-metal concentrations in non-rice grain-based, dry baby cereal. Values are pulled directly from cited sources without re-aggregation; pooling, percentile selection, and threshold math sit in the staff Standards Workbench rather than this public page.
Methodology rules for speciation, basis preservation, non-detect handling, and source pooling are stated in the Methodology section above and apply to every row below.
| Analyte | Subcategory | Reported concentration range | Detection rate | Applicable regulatory cap | Sources | Confidence | Basis |
|---|---|---|---|---|---|---|---|
| iAs | non-rice grain-based, dry (summary-only / supporting context) | highest reported 6 ppb | Sample-level detection rate not reported | No applicable cap loaded | 1 cited | low (1-2 sources) | as-sold-or-source-reported |
| Cd | non-rice grain-based, dry (direct row-fit) | mean/median 3 to 15 ppb (3 sources); highest reported 62.9 ppb | 96% detected (24/25, Fda 2024, as-sold) | eu-2023-915-cadmium: 40 ppb (product as placed on market) | 3 cited | medium (3 sources) | as-sold; as-sold-or-source-reported; mixed-or-source-reported |
| Pb | non-rice grain-based, dry (direct row-fit) | median 4 to 7 ppb (2 sources); highest reported 9.9 ppb | 84% detected (21/25, Fda 2024, as-sold) | fda2025-lead-processed-baby-foods: 20 ppb (dry infant cereal) | 3 cited | medium (3 sources) | as-sold; as-sold-or-source-reported; mixed-or-source-reported |
Lead Benchmark Context
HMI normalizes this row’s lead benchmarks to ppb so regulatory ceilings, exposure screens, and occurrence values can be compared on one concentration scale. The values below do not all mean the same thing: FDA and EU entries are regulatory context, Prop 65 is a serving-based exposure screen, and source tables on this page remain occurrence evidence.
| Reference point | Lead ppb view | Basis | How to use it |
|---|---|---|---|
| Current FDA | 20 ppb (FDA final guidance action level) | dry infant cereal, as sold | Dry infant cereals for children under 2; FDA does not split the lead action level by rice versus non-rice |
| EU 2023/915 | 20 ppb | processed cereal-based food as placed on market | EU maximum level. |
| Prop 65 MADL screen | 33.3 ppb | 21 CFR 101.12 dry instant infant cereal RACC of 15 g | Derived from the 0.5 ug/day lead MADL using 500 ÷ grams/day; not a product-specific food limit. |
| HMTc standards use | ppb-normalized context | FDA and EU both map to 20 ppb for lead; the Prop 65 value is a one-serving exposure conversion and would fall with higher daily intake. | Use 20 ppb as an external regulatory cap/context; occurrence percentiles decide whether HMTc can justify a lower standard. |
A 20 ppb cereal can be legally aligned while still not representing best-in-class occurrence if the category median is lower.
Full crosswalk: lead-benchmark-context.
Scaffold Status
- Page state: evidence-backed scaffold with first distribution caveats; row-specific synthesis remains incomplete.
- Source coverage: measured-values table populated from promoted sources; row-fit caveats remain in the table.
- Next ingest target: infant cereal datasets for non-rice dry grain products, especially iAs, Cd, and Pb.
- Ingredient targets are unresolved app-taxonomy placeholders, not source-backed typical-ingredient findings.
Distribution Context
The current source set does not yet support a non-rice dry cereal HMTc clean-platform P90. Parker 2022 provides a small grain baby-food distribution, but the authors report that two of three grain-product types were rice-based, so the table is more appropriate as a grain-category warning than a non-rice benchmark. parker2022-baby-food-arsenic-cadmium-lead-mercury-risk
| Evidence type | Analyte | Product or row fit | N | Statistic available | Values | Distribution use | Caveat |
|---|---|---|---|---|---|---|---|
| FDA compliance sample-level distribution | Total arsenic, Cadmium, Lead, Total mercury | FDA Dry Infant Cereals with no rice named | tAs 25; Cd 25; Pb 25; tHg 9 | lower-bound p50, p90, p95, max | tAs p50 12.9 ppb, p90 37.8 ppb, max 54.8 ppb; Cd p90 27.4 ppb, max 62.9 ppb; Pb p90 8 ppb, max 9.9 ppb; tHg all lower-bound 0 | Supports source-scope lower-bound distribution after review for tAs, Cd, and Pb; Hg subset is small | Machine-extracted; <LOD and NDb treated as 0; “no rice named” is not ingredient-list confirmation. fda2024-toxic-elements-baby-food-compliance-2009-2024 |
| Grain baby-food distribution | Total arsenic | Grain baby foods, mostly rice-containing | 9 | min, mean, median, max, detection rate | min 10 ppb; mean 90.4 ppb; median 126 ppb; max 132 ppb; detected 9/9 | Not for non-rice threshold setting | Total arsenic, not iAs; row fit is weak because the grain group is mostly rice-containing. parker2022-baby-food-arsenic-cadmium-lead-mercury-risk |
| Grain baby-food distribution | Cadmium | Grain baby foods, mostly rice-containing | 9 | min, mean, median, max, detection rate | min 12 ppb; mean 25.8 ppb; median 20 ppb; max 61 ppb; detected 9/9 | Not for non-rice threshold setting | Row fit is weak because the grain group is mostly rice-containing; no p10/p90. parker2022-baby-food-arsenic-cadmium-lead-mercury-risk |
| Grain baby-food distribution | Lead | Grain baby foods, mostly rice-containing | 9 | min, mean, median, max, detection rate | min 5 ppb; mean 9.7 ppb; median 5 ppb; max 20 ppb; detected 9/9 | Not for non-rice threshold setting | Row fit is weak because the grain group is mostly rice-containing; no p10/p90. parker2022-baby-food-arsenic-cadmium-lead-mercury-risk |
| All-sample baby-food/formula distribution | Cadmium | Broad U.S. baby foods and formulas | 564 | p50, p75, p90, p95, p99, max | p50 2.76 ppb; p75 9.54 ppb; p90 20.75 ppb; p95 29.44 ppb; p99 42.50 ppb; max 103.90 ppb | Broad source-scope context only | Main paper Table 1 combines all categories; it does not publish cereal-specific or non-rice cereal concentration percentiles. Sample-level or supplemental data would be needed before this source can support the non-rice cereal clean-platform aggregate. gardener2019-lead-cadmium-infant-formula-baby-food |
| All-sample baby-food/formula distribution | Lead | Broad U.S. baby foods and formulas | 564 | p50, p75, p90, p95, p99, max | p50 0 ppb; p75 5.60 ppb; p90 10.80 ppb; p95 18.50 ppb; p99 62.75 ppb; max 183.60 ppb | Broad source-scope context only | Main paper Table 1 combines all categories; it does not publish cereal-specific or non-rice cereal concentration percentiles. Sample-level or supplemental data would be needed before this source can support the non-rice cereal clean-platform aggregate. gardener2019-lead-cadmium-infant-formula-baby-food |
Measured Values And Concentration Evidence
Non-rice cereal evidence remains mixed because many infant cereal sources combine rice and non-rice cereals. Values below are included only with scope caveats.
| Analyte | Evidence scope | Reported value | Approximate ppb equivalent | Source | Row-fit caveat |
|---|---|---|---|---|---|
| Total arsenic | FDA FY2009-FY2024 dry infant cereal samples with no rice named | p50 12.9 ppb; p90 37.8 ppb; p95 40.4 ppb; max 54.8 ppb | p50 12.9 ppb; p90 37.8 ppb; p95 40.4 ppb; max 54.8 ppb | fda2024-toxic-elements-baby-food-compliance-2009-2024 | Lower-bound machine extraction; source reports As, not iAs. |
| Cadmium and Lead | FDA FY2009-FY2024 dry infant cereal samples with no rice named | Cd p90 27.4 ppb, max 62.9 ppb; Pb p90 8 ppb, max 9.9 ppb | Cd p90 27.4 ppb, max 62.9 ppb; Pb p90 8 ppb, max 9.9 ppb | fda2024-toxic-elements-baby-food-compliance-2009-2024 | Lower-bound machine extraction; product name does not prove absence of rice ingredients. |
| Cadmium | Processed baby-food cereal category in global scoping review | median 0.013 mg/kg | 13 ppb | collado-lopez2025-heavy-metals-baby-food-formula | Broad cereal category; may include rice and non-rice products. |
| Cadmium | Parker 2022 grain baby foods | mean 25.8 ppb; median 20 ppb; max 61 ppb | mean 25.8 ppb; median 20 ppb; max 61 ppb | parker2022-baby-food-arsenic-cadmium-lead-mercury-risk | Grain group, mostly rice-containing; weak row fit for non-rice. |
| Lead | Parker 2022 grain baby foods | mean 9.7 ppb; median 5 ppb; max 20 ppb | mean 9.7 ppb; median 5 ppb; max 20 ppb | parker2022-baby-food-arsenic-cadmium-lead-mercury-risk | Grain group, mostly rice-containing; weak row fit for non-rice. |
| Total arsenic | UK cereal-based infant foods/dishes | 10 ug/kg | 10 ppb | fsa2016-infant-food-formula-metals-survey | Cereal-based infant foods/dishes; rice status not isolated. |
| Inorganic arsenic | UK cereal-based infant foods/dishes | 5 to 6 ug/kg | 5 to 6 ppb | fsa2016-infant-food-formula-metals-survey | Cereal-based infant foods/dishes; rice status not isolated. |
| Cadmium | UK cereal-based infant foods/dishes | 3 ug/kg | 3 ppb | fsa2016-infant-food-formula-metals-survey | Cereal-based infant foods/dishes; rice status not isolated. |
| Lead | UK cereal-based infant foods/dishes | 0 to 1 ug/kg | 0 to 1 ppb | fsa2016-infant-food-formula-metals-survey | Lower-bound/upper-bound non-detect treatment. |
| Nickel | UK cereal-based infant foods/dishes | 124 to 127 ug/kg | 124 to 127 ppb | fsa2016-infant-food-formula-metals-survey | Cereal-based infant foods/dishes; rice status not isolated. |
Gardener 2019 Cereal Exceedance Context
Gardener 2019 includes 30 baby cereal products in the solid-food exceedance tables. These rows support cereal-level risk context, but they still do not split rice from non-rice cereals and do not provide cereal-specific concentration percentiles.
| Analyte | Broad cereal row | Scenario | Result | Standards use |
|---|---|---|---|---|
| Lead | Baby cereals | FDA daily lead limit at 300 calories | 1/30, 3.33% exceeded | Exceedance context only; not a concentration percentile. |
| Lead | Baby cereals | California Prop 65 lead daily limit at 300 calories | 13/30, 43.33% exceeded | Exceedance context only; not a concentration percentile. |
| Cadmium | Baby cereals | WHO cadmium daily limit for a 9 kg baby at 300 calories | 0/30 exceeded | Exceedance context only; not a concentration percentile. |
| Cadmium | Baby cereals | California Prop 65 cadmium daily limit at 300 calories | 0/30 exceeded | Exceedance context only; not a concentration percentile. |
French TDS Category Rows
Chekri 2019 reports a French cereal-based infant-food category with N=17, including baby cereals and infant biscuit/cereal products. The source does not split rice-based from non-rice cereal products, so these rows are context until the individual food list is mapped. Chekri 2019
| French TDS row | N | Basis | Al mean / max | tAs mean / max | Cd mean / max | Cr-total mean / max | Ni mean / max | Sn mean / max |
|---|---|---|---|---|---|---|---|---|
| Cereal-based infant foods | 17 | as consumed | 630 / 3810 ppb | 3.13 / 8 ppb | 2.79 / 17 ppb | 23 / 125 ppb | 43 / 234 ppb | 49.2 / 83 ppb |
Row Relationship
This row is the clean-benchmark counterpart to baby-cereals-dry-rice-based for the row architecture relationship covering iAs, Cd, and Pb.
Why This Category Is High-Risk
A 2025 scoping review reported that cereals had the highest median Cd concentration among baby-food groups in the review at 0.013 mg/kg, and 17% of detected cereal items exceeded the Cd maximum level used by the authors. collado-lopez2025-heavy-metals-baby-food-formula
Gardener 2019 reported that cadmium values were higher in foods containing rice, quinoa, wheat, and oats, which makes non-rice cereal subtyping necessary before treating this row as a clean benchmark. gardener2019-lead-cadmium-infant-formula-baby-food
Non-rice-specific risk remains unresolved because the promoted review’s cereal grouping is broader than this row and may include products not cleanly separable by grain type.
What Drives Variance Across Brands
The promoted sources support cereal-level monitoring but do not yet distinguish oat, wheat, corn, quinoa, multigrain, fortification premix, or non-rice-only products. collado-lopez2025-heavy-metals-baby-food-formula bair2022-heavy-metals-infant-toddler-foods
Potential variance drivers for non-rice dry baby cereals should be documented only after sources distinguish grain type, fortification, sourcing geography, processing, and analytical method.
How The App Would Estimate Risk From An Ingredient List
The app model placeholder for this row should treat baby-cereals-dry and non-rice-grains as unresolved ingredient targets until source-backed contamination profiles exist.
Historical Recalls/Enforcement
FDA’s 2023 proposed lead action levels, as summarized by Price et al. 2023, included 20 ppb for dry infant cereals. price2023-baby-food-lead-biokinetic-models
No row-specific regulatory event has been added for this scaffold.
Broad Product Context: Author-Scope Index
The sources below are catalogued as product-context candidates for this row. The “Author-scope row-fit” column states what the authors actually resolved on each axis: matrix (cow milk-based, soy-based, rice-based, non-rice, or unresolved) and format (powder, ready-to-feed liquid, concentrated liquid, dry, or unresolved). A source counts toward this row’s evidence pool only once; rows marked “Cross-reference” already appear as direct evidence elsewhere on this page and are not counted again here.
| Source | Title | Source scope | Metals | Author-scope row-fit | Canonical appearance |
|---|---|---|---|---|---|
| chekri2019-french-infant-toddler-tds-trace-elements | Trace element contents in foods from the first French Total D… | infant-formula; baby-cereals; fruit-purees; fruit-juice-not-canned | Al; Sb; tAs; Cd; Cr; Co; Ni; Sn; V | Matrix axis: unresolved (declares infant formula broadly). Format axis: unresolved (powder vs RTF not split). Source is broader than this row; authors do not narrow to this exact matrix/format pair. | Cross-reference - section: French TDS Category Rows |
| gardener2019-lead-cadmium-infant-formula-baby-food | Lead and cadmium contamination in a large sample of United St… | infant-formula; baby-cereals; toddler-formula; fruit-juice | Pb; Cd | Matrix axis: unresolved (declares infant formula broadly). Format axis: unresolved (powder vs RTF not split). Source is broader than this row; authors do not narrow to this exact matrix/format pair. | Cross-reference - section: Distribution Context |
| meli2024-chemical-characterization-baby-food-italy | Chemical characterization of baby food consumed in Italy | infant-formula-powder; fruit-purees; meat-and-poultry-purees; fish-containing-baby-foods | Al; tAs; Cd; tHg; Ni; Pb; Sn | Matrix axis: unresolved (declares powder generally; soy/non-soy not split). Format axis: exact (powder). Source is broader than this row; authors do not narrow to this exact matrix/format pair. | (context only) |
| parker2022-baby-food-arsenic-cadmium-lead-mercury-risk | Human health risk assessment of arsenic, cadmium, lead, and m… | fruit-purees; root-vegetable-purees; non-root-vegetable-purees; baby-cereals | tAs; Cd; tHg; Pb | Matrix axis: unresolved. Format axis: unresolved. Source is broader than this row; authors do not narrow to this exact matrix/format pair. | Cross-reference - section: Distribution Context |
| signes-pastor2018-infants-dietary-arsenic-solid-food | Infants’ dietary arsenic exposure during transition to solid … | infant-formula-powder; rice-cereal; fruit-purees; vegetable-purees | iAs; tAs | Matrix axis: unresolved (declares powder generally; soy/non-soy not split). Format axis: exact (powder). Source is broader than this row; authors do not narrow to this exact matrix/format pair. | Cross-reference - section: Sources |
Sources
Auto-generated from source-page frontmatter. The “Used on this page for” column is populated by the orchestrator’s POPULATE-SOURCE-LEGEND action; pending entries appear as *[awaiting synthesis]*.
| # | Citation | Year | Type | Used on this page for |
|---|---|---|---|---|
| 1 | Chronchol et al. 2026. Trace Element Intake from Dairy-Free Infant Porridges, Nutrients 2026, 18, 333 | 2026 | Peer-reviewed | Pb, Cd, and Hg in 105 samples of Polish commercial dairy-free infant porridges by ICP-AES and Hg-AAS; all concentrations low (Pb 2–4 ppb wet weight, Cd <1–3 ppb) and within EU limits; contributes directly to the non-rice clean-benchmark clean-platform evidence |
| 2 | Collado-Lopez et al. 2025. Concentrations of Heavy Metals in Processed Baby Foods and Infant Formulas Worldwide: A Scoping Review, Nutrition Reviews | 2025 | Peer-reviewed | Global scoping review (75 studies, 580 baby foods); cereals highest Cd median among baby-food groups (0.013 mg/kg) with 17% exceedance rate; rice/non-rice not consistently separated within cereal grouping |
| 3 | FDA 2025. Action Levels for Lead in Processed Food Intended for Babies and Young Children: Guidance for Industry, U.S. Department of Health and Human Services, Food and Drug Administration, Human Foods Program | 2025 | Government guidance | FDA final Closer to Zero guidance setting the 20 ppb Pb action level for dry infant cereals (rice and non-rice); applicable regulatory ceiling for this row |
| 4 | FDA 2024. Analytical Results for Lead in Processed Food Intended for Babies and Young Children (FY2023), FDA analytical results table | 2024 | Government dataset | FDA FY2023 386-sample Pb dataset across all processed baby-food categories; guidance-basis empirical foundation for the 20 ppb dry-cereal action level applicable to both rice and non-rice rows |
| 5 | FDA 2024. Analytical Results for Arsenic, Lead, Cadmium, and Mercury in Food Intended for Babies and Young Children - TEP (FY2009-FY2024), FDA analytical results table | 2024 | Government dataset | Primary compliance distribution source for this row: As, Pb, Cd, and Hg in FY2009–FY2024 FDA dry infant cereals with no rice named (n=25); tAs p90 37.8 ppb, Pb p90 8 ppb, Cd p90 27.4 ppb |
| 6 | Meli et al. 2024. Chemical characterization of baby food consumed in Italy, PLOS ONE | 2024 | Peer-reviewed | Multi-metal (Al, tAs, Cd, tHg, Ni, Pb, Sn) in 25 European baby foods; Cd and Pb below LOD in all samples; broader baby-food context; cereal compositions not split by rice vs non-rice in this study |
| 7 | Toledo et al. 2024. Essential and Toxic Elements in Infant Cereal in Brazil: Exposure Risk Assessment, International Journal of Environmental Research and Public Health 21(4):381 | 2024 | Peer-reviewed | iAs-speciated multi-metal survey in 18 Brazilian infant cereals by ICP-MS/HPLC-ICP-MS; non-rice cereal subcategory (n=4: corn, oatmeal, multi-grain) with exact author-scope matrix and format classification |
| 8 | Alharbi et al. 2023. Occurrence and Dietary Exposure Assessment of Heavy Metals in Baby Foods in the Kingdom of Saudi Arabia, Food Science & Nutrition | 2023 | Peer-reviewed | As, Cd, and Pb by ICP-MS in 111 Saudi baby food products (2020 NFMP); cereal-based meals (n=33) mean Pb 35.2 ppb and Cd 5.18 ppb dry weight; includes wheat-based and non-rice cereal products |
| 9 | Price et al. 2023. Biokinetic Modeling of Lead Exposures in Baby Food Consuming U.S. Infants (0–7 Years), Foods 12(9):1782 | 2023 | Peer-reviewed | IEUBK biokinetic model estimating blood Pb distributions in US infants 0–7 years from multi-pathway exposure; supports FDA CTZ lead action-level context for dry infant cereals; not a primary food concentration dataset |
| 10 | Bair 2022. A Narrative Review of Toxic Heavy Metal Content of Infant and Toddler Foods and Evaluation of United States Policy, Frontiers in Nutrition 9:919913 | 2022 | Peer-reviewed | US-focused narrative review synthesizing Pb, Cd, As, and Hg occurrence across IandC food categories; notes Cd elevated in wheat- and oat-containing foods; supports evidence-gap framing for non-rice cereal subtyping |
| 11 | Parker et al. 2022. Human health risk assessment of arsenic, cadmium, lead, and mercury ingestion from baby foods, Toxicology Reports | 2022 | Peer-reviewed | tAs, Cd, Pb, and tHg in 36 US baby foods; grain group (n=9) is mostly rice-containing so row fit for this page is weak; provides comparison context but not a clean non-rice benchmark |
| 12 | Zmudzinska et al. 2022. Health Safety Assessment of Ready-to-Eat Products Consumed by Children Aged 0.5–3 Years on the Polish Market, Nutrients 14(11):2325 | 2022 | Peer-reviewed | As, Cd, Hg, and Pb by ICP-MS and AAS in 397 Polish ready-to-eat baby products; porridge category included; broad scope (wet weight); rice vs non-rice not split; broad market context for the non-rice cereal row |
| 13 | FDA 2021. Analytical Results for Lead in Food Intended for Babies and Young Children (FY2020-FY2021), FDA analytical results table | 2021 | Government dataset | FDA FY2021 416-sample Pb dataset across all processed baby-food categories including dry infant cereals; precursor to the FY2009–FY2024 multi-year TEP compliance dataset |
| 14 | de et al. 2020. Aluminum content and effect of in vitro digestion on bioaccessible fraction in cereal-based baby foods, Food Research International 131:108965 | 2020 | Peer-reviewed | Total Al and in vitro bioaccessibility in 35 Brazilian infant cereals; corn-flour-only composition (non-rice) routes to this row; corn-flour cereal Al mean 920 ppb, the lowest of all compositions tested |
| 15 | Elsheikh et al. 2020. Evaluation of Some Toxic and Essential Trace Elements in Children Foods and Infant Formulae by Using ICP-OES, Asian Journal of Chemistry 32(6):1273-1278 | 2020 | Peer-reviewed | Multi-element (Al, Pb, Cd, As) in 57 Saudi children’s-food and formula samples; Cerelac infant cereal included as partial-fit non-rice context; rice/non-rice composition within Cerelac not confirmed |
| 16 | Igweze et al. 2020. Public Health and Paediatric Risk Assessment of Aluminium, Arsenic and Mercury in Infant Formulas Marketed in Nigeria, Sultan Qaboos University Medical Journal 20(1):e63-e70 | 2020 | Peer-reviewed | Al, tAs, and tHg in 26 Nigerian infant formula samples including cereal-based (n=7) and corn-meal (n=10) categories; non-rice cereal-based context; cereal-based mean tAs 680 ppb notably elevated vs milk-based |
| 17 | Chekri et al. 2019. Trace element contents in foods from the first French Total Diet Study on infants and toddlers, Journal of Food Composition and Analysis | 2019 | Peer-reviewed | French TDS category-level Al, Sb, tAs, Cd, Cr, Ni, Sn means and maxima for cereal-based infant foods (n=17, as consumed); includes rice and non-rice products without splitting; context until individual food list is mapped |
| 18 | Gardener et al. 2019. Lead and cadmium contamination in a large sample of United States infant formulas and baby foods, Science of the Total Environment | 2019 | Peer-reviewed | Pb and Cd in 564 US infant formula and baby-food products; 30 baby cereals included in exceedance tables but not split by rice vs non-rice; notes Cd elevated in quinoa, wheat, and oat-containing foods relevant to this row |
| 19 | Hernandez et al. 2019. Cr(VI) and Cr(III) in milk, dairy and cereal products and dietary exposure assessment, Food Additives & Contaminants Part B: Surveillance | 2019 | Peer-reviewed | Cr(VI) not detected in any of 68 French milk, dairy, and cereal products by LC-ICP-MS; confirms food-matrix chromium is essentially Cr(III); total Cr breakfast-cereal mean 269 ppb; extends by mechanism to non-rice infant cereal matrices |
| 20 | Signes-Pastor et al. 2018. Infants’ dietary arsenic exposure during transition to solid food, Scientific Reports | 2018 | Peer-reviewed | Infant biomarker cohort linking rice cereal to urinary As increase at weaning; cites iAs up to 20 ppb in mixed-cereal weaning foods and up to 49 ppb in mixed cereals as the non-rice cereal iAs reference range |
| 21 | FDA 2016. Analytical Results from Inorganic Arsenic in Rice Cereals for Infants, Non-Rice Infant Cereal and Other Foods Commonly Eaten by Infants and Toddlers, U.S. Food and Drug Administration | 2016 | Government dataset | Sample-level iAs with speciation in US non-rice infant cereals (n=30, oats/corn/wheat/multigrain with no rice); highest iAs 6 ppb; structured data extracted to data/evidence/category1_fda2016_infant_cereal_ias_samples.csv |
| 22 | FSA 2016. Survey of metals in commercial infant foods, infant formula and non-infant specific foods, UK Food Standards Agency report FS102048 | 2016 | Government report | UK multi-metal category-level survey; cereal-based infant foods tAs 10 ppb, iAs 5–6 ppb, Cd 3 ppb, Pb 0–1 ppb, Ni 124–127 ppb; rice status not isolated within this category |
| 23 | Sipahi et al. 2014. Safety assessment of essential and toxic metals in infant formulas, The Turkish Journal of Pediatrics 56(4):385-391 | 2014 | Peer-reviewed | Pb, Cd, Al, Mn, Cr, Co in 63 Turkish infant foods (n=23 cereal-based wheat/rice/corn/oat); cereal-based group Cd significantly higher than milk-based (8.88 vs 0.96 ppb); rice/non-rice composition not enumerated per sample |
| 24 | Jackson et al. 2012. Arsenic concentration and speciation in infant formulas and first foods, Pure and Applied Chemistry, Vol. 84, No. 2, pp. 215-223 | 2012 | Peer-reviewed | Dartmouth group iAs speciation in US infant formulas and first foods by HPLC-ICP-MS; non-rice first foods included alongside rice cereal; provides speciation context for distinguishing rice-based from non-rice arsenic profiles |
| 25 | Kirkpatrick et al. 1980. The Trace Element Content of Canadian Baby Foods and Estimation of Trace Element Intake by Infants, Canadian Institute of Food Science and Technology Journal 13(4):154-161 | 1980 | Peer-reviewed | Historical baseline: Cd, Cr, Pb, Ni, Co in 330 Canadian baby-food samples (1975 market) including cereal category by AAS; LOD 10 ppb precludes modern percentile math; context for 50-year trajectory documentation |