Oat
Completeness scorecard
Deterministic gap audit — no score is composite, no cell is LLM-judged. Each chip is re-derivable by re-running tools/evidence/build-ingredient-scorecard.mjs. review: residuals and missing data are worked autonomously via data/evidence/ingredient-scorecard-review-flags.csv and wiki/completeness-gaps.md.
| Dimension | Status | What’s there (auditable counts) | What’s missing |
|---|---|---|---|
| D1 Analyte coverage (tier: occasional) | GAP | 4/10 HMTc analytes, total n=20 | only 4/10 analytes have evidence |
| D2 Regional coverage | OK | 16 jurisdictions, top EU 32% | — |
| D3 Anthropogenic evidence | GAP | no upstream/attribution sources | link a supply-chain/ hub page |
| D4 Background mechanism | GAP | section present, 0 drivers, 0 upstream source(s) | drivers[] empty; no upstream source to substantiate |
| D5 Pooling depth | THIN | Pb POOLABLE, Cd POOLABLE, Ni POOLABLE, Cr THIN, tAs THIN, U THIN | Cr: needs 1 more study(ies); tAs: needs 1 more study(ies); U: needs 1 more study(ies) |
| D6 Speciation | OK | iAs, tHg, tAs declared | — |
| D7 Basis declaration | GAP | 0/10 populated cells declare a basis token | 10 populated cell(s) lack a basis token: Pb, Cd, iAs, tHg, Ni, Al, Cr, Sn, tAs, U |
| D8 Provenance integrity | GAP | 0 claims checked, 0 supported; 1 citations, 0 orphan, 1 foreign | 1 foreign citation(s) not naming oat: codex-cxs-193-1995 |
| D9 Mitigation | GAP | 0 cited lever(s), 6 mitigation/ link(s) | section present but no source-cited lever |
| D10 Regulatory coverage | OK | 2 rule link(s), 0 metal(s) covered | unmapped analytes: Pb, Cd, Ni, Cr, tAs, U |
| D11 Standards-readiness | NOT-READY | priority: Pb, Cd, Ni, Cr, tAs, U; pairing 0 paired, 6 single, 0 unpaired | Cr: THIN, needs 1 more study(ies); tAs: THIN, needs 1 more study(ies); U: THIN, needs 1 more study(ies); basis: 10 populated cell(s) lack a basis token: Pb, Cd, iAs, tHg, Ni, Al, Cr, Sn, tAs, U; depth below occasional bar |
| Principle balance | OK | consumer-protection 0.50, contamination-reduction 0.00, brand-value 0.00, legal-defensibility 0.50, scale 0.25 | — |
This is a structural ingredient node created so product pages can link to a real wiki target. Occurrence values remain pending until a source is promoted for this ingredient.
Heavy metal contamination profile
Per-analyte snapshot derived from the machine-readable contamination_profile in the frontmatter above. data gap indicates the literature has been reviewed for this commodity-analyte combination and no usable occurrence data was found (a finding, not a placeholder). The Key sources column shows the top 2-3 contributing sources by year and sample size, with numbered wikilink aliases.
| Analyte | Coverage | Typical (ppb) | p95 (ppb) | Confidence | Key sources |
|---|---|---|---|---|---|
| Pb | n=5 | 10–100 | 400 | medium | 1, 2, 3 |
| Cd | n=4 | 10–100 | 310 | medium | 1, 2, 3 |
| iAs | data gap | — | — | — | — |
| tAs | n=2 | 10–100 | 600 | low | 1, 2 |
| tHg | data gap | — | — | — | — |
| Ni | n=5 | 300–1000 | 1970 | medium | 1, 2, 3 |
| Al | data gap | — | — | — | — |
| Cr | n=2 | 10–100 | 5400 | low | 1, 2 |
| Sn | data gap | — | — | — | — |
| U | n=2 | 0–1 | — | low | 1, 2 |
Routing
This node is linked from plant-milks-non-soy-non-rice, teething-and-snacks-non-rice.
Contamination Profile State
The machine-readable contamination profile is pending. Ingredient-level values belong here once parsed; finished-product values belong on the relevant product-category page.
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 | Begday et al. 2026. Integral assessment of the environmental safety of plant-based milk alternatives based on heavy metal analysis, Izvestiya KGTU (KSTU News) | 2026 | Peer-reviewed | RU Pb, Cd, Zn, Cu occurrence in Eight plant-based milk samples assessed on the Russian market: four commercial ready-to-drink beverages (one each of almond, rice,… (n=8) |
| 2 | Good et al. 2026. Comparative exposure and risk assessment of heavy metals, nutrients, and organochlorine pesticides in cow and plant-based milks, Scientific Reports | 2026 | Peer-reviewed | US Cr, tAs, Cd, Pb occurrence in Twenty-two commercially available milk products purchased from major grocery retailers in Houston, Texas, USA. Eight milk-type categories: cow… (n=22) |
| 3 | Du et al. 2025. Heavy metal exposures in aerodigestive clinic cohort of infants with reflux or dysphagia, Scientific Reports | 2025 | Peer-reviewed | US tAs, iAs, Pb, tHg, Cd, Sn, Cr, Ni, U occurrence in Infants under 1 year of age with reflux or oropharyngeal dysphagia seen at Boston Children’s Hospital aerodigestive clinic,… (n=56) |
| 4 | Zvěřina et al. 2025. Essential and toxic elements in plant-based dairy alternatives: implications for vegan diets, European Food Research and Technology | 2025 | Peer-reviewed | CZ/EU Pb, Cd occurrence in Fifty-four plant-based dairy alternative (PBDA) samples sourced from the Czech market in Brno, Czech Republic. Composition: 35 milk… (n=54) |
| 5 | EU 2024. Commission Recommendation (EU) 2024/907 of 22 March 2024 on the monitoring of nickel in food, Official Journal of the European Union, L series, 2024/907 (26.3.2024) | 2024 | Regulation | EU Ni concentrations |
| 6 | 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 | BR Ag, Al, tAs, iAs, B, Ba, Cd, Co, Cr, Cu, Mn, Ni, Pb, Se, Sr, Zn occurrence in Eighteen Brazilian infant-cereal samples acquired in 2014-2015: 9 rice cereals, 5 multi-grain cereals containing rice, and 4 non-rice-based… (n=18) |
| 7 | Oduro et al. 2023. Health risks of potentially toxic metals in cereal-based breakfast meals in the Kumasi Metropolis, Ghana, Discover Food 3:25 | 2023 | Peer-reviewed | GH tAs, Cd, Cr, Ni, Pb, Mn occurrence in Locally produced cereal-based breakfast meals (31 breakfast cereals, 20 biscuits, 3 bread types) from markets in Kumasi, Ghana;… (n=54) |
| 8 | Redan et al. 2023. Analysis of Eight Types of Plant-based Milk Alternatives from the United States Market for Target Minerals and Trace Elements, Journal of Food Composition and Analysis | 2023 | Peer-reviewed | US tAs, Cd, Pb occurrence in Eighty-five plant-based milk alternative product units from 19 brands purchased from 10 retail markets and an online retailer… (n=85) |
| 9 | Rubio et al. 2023. Dietary Exposure to Toxic Metals (Cd, Pb and Hg) from Cereals Marketed in Madeira and the Azores, Biological Trace Element Research | 2023 | Peer-reviewed | PT Cd, Pb, tHg occurrence in Cereals and cereal derivatives marketed in Madeira and the Azores (Portuguese Atlantic archipelagos); multiple cereal types including rice,… |
| 10 | BfR 2022. Nickel: estimate of long-term intake via food based on the BfR MEAL Study, BfR Communication No. 033/2022 | 2022 | Government report | DE/EU Ni occurrence in 840 food pools from 356 foods representing 90%+ of German food consumption; adults and adolescents N=13,926 (NVS II,… (n=840) |
| 11 | Marques et al. 2021. Essential and Non-essential Trace Elements in Milks and Plant-Based Drinks, Biological Trace Element Research | 2021 | Peer-reviewed | Measured Pb, tHg, Ni, and U in retail oat-based plant drinks from Spain; Pb detected in one non-organic oat drink sample |
| 12 | Saraiva et al. 2021. Speciation analysis of Cr(III) and Cr(VI) in bread and breakfast cereals using species-specific isotope dilution and HPLC-ICP-MS, Journal of Food Composition and Analysis | 2021 | Peer-reviewed | FR/DK/EU Cr, Cr-VI occurrence in 22 retail samples — 11 breads (Danish rye/rugbrød, malt flour, wheat ‘burger’ buns, spelt, wheat ‘pita’, wheat baguette,… (n=22) |
| 13 | U.S. House of Representatives, 2021. Baby Foods Are Tainted with Dangerous Levels of Arsenic, Lead, Cadmium, and Mercury, Staff Report | 2021 | Gray literature | US iAs, tAs, Pb, Cd, tHg occurrence in Internal company testing records (ingredient pre-shipment tests and finished-product tests) subpoenaed from seven major US baby-food manufacturers covering… |
| 14 | CFIA 2020. Toxic Metals in Selected Foods – April 1, 2018 to March 31, 2019: Food chemistry – Targeted surveys – Final report, Canadian Food Inspection Agency | 2020 | Government report | CA tAs, Cd, Pb, tHg occurrence in Retail food samples (bran products, infant formula, meal replacement beverages, protein powders, rice products) collected from 6 Canadian… (n=985) |
| 15 | Paiva et al. 2020. Aluminium in infant foods: Total content, effect of in vitro digestion on bioaccessible fraction and preliminary exposure assessment, Journal of Food Composition and Analysis 90:103493 | 2020 | Peer-reviewed | Brazilian infant food Al survey (n=95); oat is a constituent of salty purees in scope; documents high Al content and variable bioaccessibility in oat-containing infant foods |
| 16 | Mania et al. 2020. Assessment of exposure to nickel intake with selected cereal grains and cereal-based products, Roczniki Panstwowego Zakladu Higieny (Annals of the National Institute of Hygiene) | 2020 | Peer-reviewed | PL/EU Ni occurrence in Polish market samples 2019–2020: 5 cereal grains (millet, rye, wheat, barley), 11 pasta, 13 flours, 12 groats, 10… (n=56) |
| 17 | TatahMentan et al. 2020. Toxic and Essential Elements in Rice and Other Grains from the United States and Other Countries, International Journal of Environmental Research and Public Health | 2020 | Peer-reviewed | US/CA/TH tAs, Pb, Cd, Cu, Fe, Mn, Zn occurrence in Rice and other grains purchased from local stores in Louisiana, USA: 28 white rice samples, 11 brown rice… |
| 18 | Slepecka et al. 2017. Evaluation of cadmium, lead, zinc and copper levels in selected ecological cereal food products and their non-ecological counterparts, Current Issues in Pharmacy and Medical Sciences 30(3):147-150 | 2017 | Peer-reviewed | PL Cd, Pb, Zn, Cu occurrence in 10 ecological and 10 non-ecological cereal products (flour, flakes, bran) from different producers and regions of Poland; product… (n=20) |
| 19 | Flyvholm et al. 1984. Nickel Content of Food and Estimation of Dietary Intake, Zeitschrift für Lebensmittel-Untersuchung und -Forschung 179(6):427-431 | 1984 | Peer-reviewed | Foundational Ni occurrence dataset; oat identified as a high-Ni grain with a disproportionate load factor relative to dietary weight |
Why this commodity accumulates heavy metals
Oats (Avena sativa) are a non-rice cereal grain grown in temperate climates worldwide (Canada, Russia, EU member states, Australia, US). Oats accumulate cadmium from soil at moderate rates — generally lower than wheat from the same growing region, and an order of magnitude lower than rice for iAs specifically (oats are not an iAs accumulator). Oat bran concentrates Cd relative to the endosperm; whole-oat products carry approximately 2× the Cd of rolled or steel-cut oats from the same source grain.
Oat positioning in baby cereal and breakfast cereal markets has shifted in the post-2018 brown-rice-syrup-iAs-debate era: parents and infant nutrition manufacturers have moved toward oat-based products to avoid rice-iAs exposure. This makes oat an increasingly important Cat 3 and Cat 1 ingredient.
The HMTc panel concerns for oat are Cd (moderate, with bran fraction concentration) and Pb (generally low). iAs in oat is at trace levels, not a meaningful contributor to dietary iAs.
Ranges by source, region, and variety
Geographic variance: Canadian oats are a major North American and global commodity oat source; Canadian Prairie soils generally carry lower Cd than European production regions. Australian oats from Western Australia carry moderate Cd. European production (Finland, Sweden, Germany, Poland) shows variance by region. Oats from areas with documented elevated soil-Cd from phosphate-fertilizer history carry higher Cd than oats from cleaner soils.
Cultivar variance: oat varieties with documented low Cd accumulation have been identified in breeding programs; commercial varieties span a 2-3× range of Cd accumulation within a single growing region.
Processing effects
Oat processing (cleaning, hulling, kilning, rolling or steel-cutting, packaging) does not change source-grain Cd meaningfully. Hulling removes the inedible hull but retains the bran. Rolled and steel-cut oats carry the source-grain Cd unchanged. Instant oats (pre-cooked, flash-dried) carry the source-grain Cd plus minor concentration effects from drying.
Oat bran (separated from the endosperm-rich fraction during milling) concentrates Cd; oat-bran cereal carries 2-3× the Cd of equivalent rolled-oat cereal.
Cooking oats with water and consuming the cooking water (as is standard for oatmeal) conserves the source-grain Cd in the finished bowl. Boiling-and-discard is uncommon for oats and would only modestly reduce per-serving Cd.
Ingredient-derivative risk
Oat derivatives: oat flour, oat milk (typically 7-15 percent oat by mass; see plant-milk), oat-fiber supplements, oat-protein isolates (concentrated Cd), beta-glucan supplements (oat-derived fiber). Oat-milk products inherit the source-grain Cd with water-dilution effects.
Oat baby cereal is a major Cat 1 product category that has gained share over rice baby cereal in iAs-conscious consumer segments. See baby-cereals-dry and baby-cereals-dry-non-rice.
Mitigation options
Sourcing levers (supply-chain-screening) include single-origin sourcing from documented low-Cd growing regions (parts of Canadian Prairies, certain Australian production zones), supplier-side Cd testing of incoming grain.
Agronomic levers (agronomic) include soil pH management, low-Cd-accumulator cultivar selection, avoidance of high-Cd phosphate fertilizers.
Processing levers (processing) include whole-oat vs steel-cut-oat vs rolled-oat formulation (impacts bran-fraction Cd contribution).
Formulation levers (formulation) include substitution of oat for rice in iAs-target-low products (oat substantially reduces iAs while moderately increasing Cd), and oat-percentage adjustment in compounded products.
Testing and QC levers (testing-and-qc) include lot-level Cd testing on incoming oat grain, particularly for infant-targeted and baby-cereal manufacturing. See icp-ms.
Packaging and storage levers (packaging-and-storage) are not generally consequential for oat metal load.
Regulatory limits that apply
- eu-2023-915 — EU Reg. 2023/915 sets maximum levels for Cd in cereal grains. Oat falls under the general cereal Cd ML.
- Codex CXS 193-1995 — Codex Cd ML for cereal grains.
- FDA does not maintain a binding action level for Cd in oats specifically.
- California Prop 65 (california-prop65) Cd MADL applies to oat-containing products sold in California.
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 |
|---|---|---|
| b0f3d38 | 2026-06-12 | batch | corpus rescreen b04 old terminal skips |