Skip to content
Heavy Metal Index

Plant Milks, Rice-Based — RETIRED

A category profile assembled from its inputs. It reports what the routed literature says about the ingredients that drive it, not brand-by-brand product tests.

Overview

Category framing

This is a category risk profile assembled from the ingredients that drive it. It does not test products, name brands, or publish brand-by-brand tables. The metals that govern it, in the routed corpus, are Inorganic arsenic, Cadmium and Lead.

Ingredient drivers

The inputs below are ordered by their share of the routed occurrence evidence for the metal each drives; the bar shows relative position within this category, not a comparison against any limit.

RiceCadmium

Leading cadmium driver among this category's routed inputs — p95 160 ppb, 8 sources, medium confidence.

Plant milk baseInorganic arsenic

Leading inorganic arsenic driver among this category's routed inputs — p95 24 ppb, 1 source, low confidence.

Limits applicable to this category

The category inherits the maximum levels and action levels that apply to it. These are regulatory limits, not certification thresholds.

InstrumentMetalValueStatus
EU inorganic arsenic maximum level for non-alcoholic rice-based drinksInorganic arsenic30 µg/kgBinding

Testing and verification posture

Occurrence values in this category are measured by ICP-MS in the source literature, the same method the FDA Toxic Elements Program uses for the survey data behind its action levels.

Where third-party testing programs are cited as sources, the category-level signal is summarized and the reader is pointed at the original document for anything brand-specific. The Index does not reproduce brand-by-brand tables.

This subcategory has been re-routed to Category 3, currently in build. The standards page will be available when Category 3 is finalized.

HMTc Category 5 row 7 was retired under Category 5 Step 0 Amendment 1 (April 28, 2026), authority Step Zero Protocol v1.4 §0G operation 2. Rice-based plant milks (rice milk) are certified under Category 3 (Grains, Cereals, and Rice Products), row 10 (Rice beverages), so that the rice higher-contamination row is handled coherently within one category. This URL is preserved permanently and will resolve to the Category 3 row 10 standards page once Category 3 is locked.

The literature evidence below is retained for historical reference and will be re-routed to the Category 3 row 10 page when that page is built. No HMTc standards values are published from this page.

Historical literature evidence (Category 5 row 7, retired)

The content below was the original Category 5 row 7 literature synthesis. It is preserved verbatim for traceability under the locked-file-immutability principle. Standards inheritance moves to Category 3 row 10.

Methodology

This page reports what the peer-reviewed and regulatory literature states about heavy-metal concentrations in rice-based plant milks. HMT&C certification thresholds for products in this row are developed under the certification program at heavymetalcertified.com, not on this page.

Speciation is non-substitutable. Inorganic arsenic (iAs) and total arsenic (tAs) are separate analytes. Total mercury (tHg) and methylmercury (MeHg) are separate analytes. Total chromium (Cr) and hexavalent chromium (Cr-VI) are separate analytes. Values are never interchanged across speciation boundaries.

Basis is preserved and labeled. Concentration values are reported as the source states them (as consumed, as placed on market, dry weight). Conversion between bases is shown explicitly when performed; silent conversion is never done.

Row-fit follows author scope. A source’s matrix and format classification is determined by what the authors state, not by re-derivation. Vague author scope receives a partial row-fit designation; sources silent on matrix receive an unknown designation.

Non-detect handling preserves source convention. Sources that report non-detects as zero, as LOD/2, or as <LOD are recorded as stated. The convention is noted in the Source Evidence Inventory.

Source pooling is avoided across different LOQ thresholds, collection periods, geographies, and analytical-basis differences without explicit documentation of the pooling rationale.

Decision Snapshot

FieldStatus
Row stateSpecies-specific occurrence and regulatory comparison available for iAs
Best current sourceInorganic Arsenic in Rice-Based Beverages: Occurrence in Products Available on the Italian Market and Dietary Exposure Assessment
Applicable regulationEU inorganic arsenic maximum level for non-alcoholic rice-based drinks
Computation readinessData-grounded for EU iAs comparison; Cd and Pb remain evidence gaps
Ingredient routingPlant milk base, Rice
HMTc useStrong evidence for iAs prioritization; not an HMTc threshold

Federal / Regulatory Limits vs Field Findings

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.

MetalFederal / regulatory limitActual field findingDecision readEvidence
Arsenic, Inorganic (iAs)EU inorganic arsenic maximum level for non-alcoholic rice-based drinks: EU European Commission maximum level: 30 ug/kg iAs. Scope: non-alcoholic rice-based drinks. Basis: wet weight.D’Amato 2026 reports 25 Italian rice-based beverages with iAs from 7 to 24 ug/kg; no sample exceeded 30 ug/kg.Direct comparison available; matrix, analyte species, and unit basis match. Not an HMTc certification limit.EU inorganic arsenic maximum level for non-alcoholic rice-based drinks; Inorganic Arsenic in Rice-Based Beverages: Occurrence in Products Available on the Italian Market and Dietary Exposure Assessment
Arsenic, Total (tAs)No federal product-specific limit loaded in this crosswalk.D’Amato 2026 reports total arsenic from 9 to 58 ug/kg in rice-based beverages; total arsenic is context only and is not interchangeable with inorganic arsenic.Occurrence evidence only. Do not infer a federal exceedance or HMTc pass/fail result from this row.Inorganic Arsenic in Rice-Based Beverages: Occurrence in Products Available on the Italian Market and Dietary Exposure Assessment

Broad Product Context: Author-Scope Index

Broad-context source index will be auto-generated here when the routing audit identifies sources whose author-stated scope is broader than this product row.

Source Evidence Inventory

Sources contributing measured rice-based plant milk concentrations are listed below. Intake and exposure estimates are kept separate from measured product concentrations.

Occurrence Evidence

Inorganic Arsenic in Rice-Based Beverages: Occurrence in Products Available on the Italian Market and Dietary Exposure Assessment analyzed 25 Italian-market rice-based beverages collected from April 2022 to March 2023. The study used HPLC-ICP-MS speciation and reported no left-censored iAs values, which makes it unusually useful for comparison-layer work.

The same source reports consumer-only dietary exposure estimates that are important for risk prioritization: toddlers consuming rice drinks averaged 0.27 ug/kg bw/day with MOE 0.2, while other children averaged 0.13 ug/kg bw/day with MOE 0.5. These are exposure-risk context, not product-level compliance values.

Ingredient Handling

The iAs measurements are finished rice-based beverages. They should not be copied into Rice as ingredient-only values. The rice ingredient node can link to this source as related finished-product evidence.

Literature Evidence Summary

The table below summarizes what the peer-reviewed and government literature cited on this page reports for heavy-metal concentrations in rice-based product. Values are pulled directly from cited sources without re-aggregation. This page publishes literature evidence only, not certification thresholds.

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.

AnalyteSubcategoryReported concentration rangeDetection rateApplicable regulatory capSourcesConfidenceBasis
iAsrice-based (no contributing evidence loaded)No concentration data loaded for this analyteSample-level detection rate not reportedEU inorganic arsenic maximum level for non-alcoholic rice-based drinks: 30 ppb (wet weight)0data gapBasis not reported
Cdrice-based (no contributing evidence loaded)No concentration data loaded for this analyteSample-level detection rate not reportedNo applicable cap loaded0data gapBasis not reported
Pbrice-based (no contributing evidence loaded)No concentration data loaded for this analyteSample-level detection rate not reportedNo applicable cap loaded0data gapBasis not reported

References

Works cited in this page’s text, in first-appearance order. See Sources for this page’s source inventory. Each title links to its source record, which carries the ingest receipt, the extracted values, and the file hash of the document it was built from.

  1. Inorganic Arsenic in Rice-Based Beverages: Occurrence in Products Available on the Italian Market and Dietary Exposure AssessmentD’Amato M, Turco AC, D’Amore T, Vitale F, Marini F, Stacchini P, et al. · Foods · 2026 · doi.org/10.3390/foods15020383Peer-reviewed

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]*.

#CitationYearTypeUsed on this page for
1Begday et al. 2026. Integral assessment of the environmental safety of plant-based milk alternatives based on heavy metal analysis, Izvestiya KGTU (KSTU News)2026Peer-reviewedRU 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)
2D’Amato et al. 2026. Inorganic Arsenic in Rice-Based Beverages: Occurrence in Products Available on the Italian Market and Dietary Exposure Assessment, Foods2026Peer-reviewedHPLC-ICP-MS speciation of iAs in 25 Italian-market rice-based beverages (mean iAs 15 µg/kg); primary direct iAs occurrence source for the rice-based plant-milk row with EU regulatory comparison
3Good et al. 2026. Comparative exposure and risk assessment of heavy metals, nutrients, and organochlorine pesticides in cow and plant-based milks, Scientific Reports2026Peer-reviewedUS 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)
4Zvěřina et al. 2025. Essential and toxic elements in plant-based dairy alternatives: implications for vegan diets, European Food Research and Technology2025Peer-reviewedCZ/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)
5Redan 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 Analysis2023Peer-reviewedUS 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)
6Marques et al. 2021. Essential and Non-essential Trace Elements in Milks and Plant-Based Drinks, Biological Trace Element Research2021Peer-reviewedICP-MS survey of Pb, tHg, Ni, and U in retail plant-based drinks from Spain including rice drink; tHg not detected; provides multi-metal occurrence context for the rice-based plant-milk row
7Gu et al. 2020. Arsenic Concentrations and Dietary Exposure in Rice-Based Infant Food in Australia, International Journal of Environmental Research and Public Health 17(2):4152020Peer-reviewedICP-MS tAs and iAs measurement in 3 Australian rice milk powder samples (mean tAs 428 ppb; mean iAs 160 ppb); triangulation source confirming elevated iAs in rice-based beverages in a non-EU market
8C-C et al. 2016. Methylmercury varies more than one order of magnitude in commercial European rice, Food Chemistry2016Peer-reviewedSPE-HPLC-CV-AFS MeHg speciation in 87 commercial European rice products (MeHg range 0.11–6.45 µg/kg; mean 1.91 µg/kg); provides MeHg ingredient cascade for the rice-based plant-milk row via rice-commodity linkage
9Meharg et al. 2008. Levels of arsenic in rice - literature review, Food Standards Agency contract C1010452008Government reportUK tAs, iAs occurrence in Food Standards Agency-commissioned literature review and secondary tabulation of published, FSA, and University of Aberdeen rice arsenic data,…

CC candidate evidence map

AnalyteDistribution sources (sample-level)Summary sourcesTotal source count
Pb—Marques 2021 (n=42 plant-drinks; rice-drink subset count pending)1 summary
Cd——0
tAs—Da Mato 2026 (n=25 summary), Gu 2020 (n=3 triangulation)2 summary
iAs—Da Mato 2026 (n=25 summary), Gu 2020 (n=3 triangulation)2 summary + EU cap
MeHg—Brombach 2017 ingredient cascade1 cascade
tHg—Marques 2021 (not-detected)1 summary
Ni—Marques 20211 summary
Al, Cr-VI, Sn——0

Levers to reduce contamination

The levers below are ordered by estimated impact magnitude for finished rice-based plant milks as a product category. Inorganic arsenic (iAs) is the primary metal of concern, with an applicable EU regulatory cap of 30 µg/kg (EU 2023/915). Magnitude claims are cited; uncited lever rows carry a placeholder noting that quantified evidence has not yet been ingested.

Lever categorySpecific actionEstimated magnitudeSource
SourcingSource rice from low-iAs regions: D’Amato 2026 found iAs ranging from 7 to 24 µg/kg across 25 Italian retail rice beverages; origin geography of the rice base is the primary driverD’Amato 2026: iAs range 7–24 µg/kg in Italian-market samples; no sample exceeded EU 30 µg/kg cap1
SourcingRice raw-material specification: require supplier CoA with iAs values by lot; US long-grain and brown rice carry higher iAs burden than basmati varietiesQuantified magnitude data for material-selection reduction in finished rice beverage iAs not yet ingested; cross-reference Rice when synthesis is available.—
AgronomicWater management at paddy level (aerobic vs flooded conditions); affects iAs uptake in rice grain; operational for brands purchasing direct from growers or cooperativesQuantified magnitude data not yet ingested for finished-beverage impact—
ProcessingRice washing and cooking prior to extraction; higher water-to-rice ratios in beverage production can dilute residual iAs; effect magnitude depends on extraction process designQuantified magnitude data not yet ingested—
FormulationBlending rice with lower-iAs plant bases (oat, almond) reduces per-serving iAs burden but changes the product category; pure rice beverages cannot dilute without product reformulationQuantified magnitude data not yet ingested—
Testing/QCLot-level finished-product HPLC-ICP-MS iAs speciation (not total arsenic); the iAs-to-tAs ratio varies by rice origin; total arsenic alone does not support regulatory compliance against the EU 30 ppb iAs capQuantified magnitude data not yet ingested for lot-level testing impact on exceedance rate—
Packaging/storageNon-canned format typical for rice beverages; tin migration is not a primary lever; glass and paperboard cartons appropriateNot a primary lever for this product class—

How standards math uses this page

This page reports what the peer-reviewed and government literature says about heavy-metal concentrations in this product category; it publishes no certification thresholds of its own. Certification criteria are set separately under the Heavy Metal Tested & Certified program at heavymetalcertified.com, which reads this page as its literature baseline. The two are kept apart by design, so this page remains an independent record of the evidence rather than a justification for any threshold.

Historical recalls and enforcement

No public recalls or enforcement actions specifically targeting heavy metals in rice-based plant milks are documented in the wiki’s source corpus as of the last review. The EU Commission maximum level for iAs in non-alcoholic rice-based drinks (30 µg/kg, established under Regulation EU 2023/915) represents the operative regulatory framework for this product class in the EU market. This section will be populated when specific enforcement events or market-surveillance actions are ingested.

Frame: if FDA, EU, or national-agency enforcement actions involving heavy metals in this product category are identified in future ingest, they will appear here as regulatory events. This section does not rank brands.

Update history

No substantive edit history is available in this build. The full commit record is available in git.