Key Numbers

Inorganic Arsenic Concentrations in Rice Cereal (FDA survey)

  • Range: 0.023–0.283 mg/kg iAs
  • Mean: ~0.100 mg/kg iAs
  • Rice cereal accounted for approximately 55% of total iAs exposure in infants 4–24 months

Exposure Assessment (Monte Carlo, n=1,000,000 iterations)

Infants 4–6 months:

  • Mean daily intake: 0.46 μg/kg/day iAs
  • 95th percentile: 1.32 μg/kg/day iAs

Infants 7–12 months:

  • Mean daily intake: 0.32 μg/kg/day iAs
  • 95th percentile: 0.85 μg/kg/day iAs

Toddlers 13–24 months:

  • Mean daily intake: 0.28 μg/kg/day iAs
  • 95th percentile: 0.75 μg/kg/day iAs

Hazard Quotient for Chronic Non-Carcinogenic Risk

  • ATSDR chronic MRL: 3.0 × 10⁻⁴ mg/kg/day
  • HQ exceeded 1.0 at 50th percentile for 4–6 month-olds
  • HQ exceeded 1.0 at 75th percentile for 7–12 month-olds
  • HQ remained below 1.0 for 13–24 month-olds at all percentiles

Incremental Lifetime Cancer Risk (ILCR)

  • EPA cancer slope factor: 1.5 (mg/kg/day)⁻¹
  • 4–6 month-olds: ILCR 10⁻⁶ to 10⁻⁵
  • 7–12 month-olds: ILCR 10⁻⁶ to 10⁻⁵
  • 13–24 month-olds: ILCR below 10⁻⁶ at mean, 10⁻⁶ to 10⁻⁵ at 95th percentile

Regulatory Reference Values and Proposed MCL

  • ATSDR acute MRL: 5.0 × 10⁻³ mg/kg/day
  • ATSDR chronic MRL: 3.0 × 10⁻⁴ mg/kg/day
  • EPA oral RfD: 3.0 × 10⁻⁴ mg/kg/day
  • FAO/WHO proposed maximum level for polished rice: 0.2 mg/kg
  • Derived MCL (chronic exposure at ATSDR MRL, 4–6 month infants): 0.0 mg/kg (practical limit)
  • Derived MCL (acute exposure at ATSDR MRL): 0.4 mg/kg

Methods

Exposure Assessment Framework

  • Hazard identification: iAs classified as Group 1 carcinogen; dose-response derived from epidemiological and animal studies
  • Exposure pathways: rice cereal (primary), other solid foods, drinking water, infant formula
  • Body weight and dietary intake: age-stratified (4–6, 7–12, 13–24 months); assumed exclusive rice-cereal consumption for 4–6 month cohort in sensitivity analysis
  • Probabilistic modeling: Monte Carlo simulation (1 million iterations) to characterize exposure distribution and percentiles

Risk Characterization

  • Non-carcinogenic risk: Hazard Quotient (HQ) = exposure ÷ ATSDR MRL; HQ > 1.0 indicates potential for adverse effects
  • Carcinogenic risk: ILCR calculated as mean daily intake × cancer slope factor; risk interpreted relative to EPA benchmark of 10⁻⁶

Data Sources

  • FDA 2012–2013 retail rice cereal survey: 116 samples analyzed for total and inorganic arsenic
  • NHANES dietary intake data: age-specific consumption patterns and body weight distributions
  • Drinking water: USDA data for iAs in municipal and private well supplies

Wiki Pages Updated on Ingest

  • metals/arsenic.md — inorganic arsenic toxicology, dose-response, regulatory values
  • ingredients/rice.md — iAs contamination in rice and rice cereal; exposure in infant populations
  • ingredients/rice-cereal.md — if separate page exists, update iAs contamination_profile
  • products/infant-rice-cereal.md — iAs exposure contribution; regulatory context
  • products/infant-formula-cow-milk.md — iAs as background exposure source in mixed-feeding scenarios
  • products/infant-formula-soy.md — iAs as background exposure source
  • products/infant-solid-foods.md — category-level iAs profile; rice cereal dominance
  • regulations/us-fda-closer-to-zero.md — iAs baseline for infant foods; gap between current survey mean and precautionary levels

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
ce3e07c2026-05-28activation | Vercel DATACITE env slots set, curators.md filled with founder entry + six scoped reviewer invitations, peer-review onboarding playbook drafted
51400b92026-05-28audit-queue: gasparik2017-wild-boar-slovakia-metals audited-revised