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Heavy Metal Index

Toxic Elements in Commercial Infant Food, Estimated Dietary Intake, and Risk Assessment in Poland

Source

This monitoring study reports Pb, Cd, total As, and total Hg in approximately 1,000 infant-food samples collected across Poland from 2009 to 2013, with all products analyzed as sold.

Page snapshot
Cited by34 pages
Metals measured4
Evidence tierA
Year2015

Overview

This monitoring study reports Pb, Cd, total As, and total Hg in approximately 1,000 infant-food samples collected across Poland from 2009 to 2013, with all products analyzed as sold. The dataset covers infant formulae, rice and non-rice cereal foods, biscuits, ready-to-eat meals, fish-based foods, fruit desserts, juices, and infant teas. The highest arsenic signals were in rice gruel and fish-based infant foods, the highest mercury signal was in fish-based infant foods, cadmium was most prominent in vegetable meals and some cereal products, and lead exposure estimates approached or exceeded EFSA reference-dose comparators in the authors’ infant diet scenarios.

Key numbers

Concentrations are mg/kg as sold. Tables 1-4 report lower-bound, middle-bound, and upper-bound statistics for left-censored data; this page uses middle-bound means as the compact category comparison. Sample counts differ by analyte because not every product was analyzed for every element.

Product categoryn by analyte (Pb/Cd/tAs/tHg)Pb MB meanCd MB meantAs MB meantHg MB mean
Infant and follow-on formula112 / 119 / 118 / 1130.00510.00120.00670.0007
Milk- and rice-based products58 / 62 / 62 / 610.00460.00160.01210.0006
Soya-based infant formula22 / 22 / 22 / 220.00600.00340.01100.0009
Rice gruel for infants185 / 198 / 197 / 1800.00830.00410.05950.0009
Wheat gruel for infants74 / 86 / 86 / 760.00560.00470.00660.0006
Mixed cereals for infants65 / 74 / 73 / 660.00640.00350.01020.0008
Biscuits for infants49 / 49 / 49 / 480.01260.00660.00870.0007
Vegetable meals, ready-to-eat49 / 49 / 49 / 490.00720.00960.00610.0006
Vegetable-meat meals, ready-to-eat64 / 64 / 62 / 620.00770.00700.00580.0009
Fish-based infant foods, ready-to-eat47 / 47 / 47 / 470.00730.00670.06660.0063
Fruit desserts for infants43 / 43 / 43 / 410.00750.00180.00550.0005
Juices for infants69 / 69 / 69 / 680.00610.00100.00580.0004
Herbal teas for infants45 / 45 / 45 / 440.00640.00060.00710.0006
Herbal and fruit teas for infants60 / 60 / 60 / 600.00710.00110.00450.0005

Source-reported high points and risk-assessment values:

  • Pb: infant formula and follow-on formula mean MB 0.0051 mg/kg, P90 MB 0.0099 mg/kg; biscuits mean MB 0.0126 mg/kg, P90 MB 0.0282 mg/kg; rice gruel mean MB 0.0083 mg/kg, P90 MB 0.0146 mg/kg. The discussion reports a highest pure-rice-gruel Pb value of 0.120 mg/kg.
  • Cd: vegetable meals mean MB 0.0096 mg/kg, P90 MB 0.0174 mg/kg; biscuits mean MB 0.0066 mg/kg, P90 MB 0.0109 mg/kg; wheat gruel mean MB 0.0047 mg/kg, P90 MB 0.0090 mg/kg; rice gruel mean MB 0.0041 mg/kg, P90 MB 0.0119 mg/kg. The discussion reports a pure-rice-gruel Cd value of 0.0490 mg/kg, above the source-cited 0.040 mg/kg EU maximum level for cereal-based infant foods at the time.
  • tAs: rice gruel mean MB 0.0595 mg/kg, P90 MB 0.1404 mg/kg; fish-based infant foods mean MB 0.0666 mg/kg, P90 MB 0.1781 mg/kg. The discussion reports the highest tAs values as 0.297 mg/kg in rice gruel and 0.195 mg/kg in a cod-fish-and-vegetables dinner.
  • tHg: fish-based infant foods mean MB 0.0063 mg/kg, P90 MB 0.0127 mg/kg; other categories were at or below 0.0009 mg/kg mean MB. The discussion reports the highest mercury value as 0.0185 mg/kg in a vegetable-and-fish infant dinner.
  • Dietary exposure estimates from the abstract and Results: mean Pb exposure 0.09 to 0.53 microgram/kg bw/day for 3- and 12-month infants; mean Cd exposure 0.02 to 0.39-0.4 microgram/kg bw/day; mean tAs exposure 0.11 to 0.99 microgram/kg bw/day; mean organic-Hg worst-case exposure 0.01 to 0.08 microgram/kg bw/day.

Methods (brief)

The National Institute of Public Health - National Institute of Hygiene coordinated a 2009-2013 monitoring programme in which Polish sanitary-epidemiological stations sampled infant foods from retail markets in all provinces. Sampling followed Commission Regulation No. 333/2007 for official control of Pb, Cd, Hg, inorganic tin, 3-MCPD, and benzo(a)pyrene in foodstuffs. All products were analyzed as sold, without reconstitution.

Lead and cadmium were determined by atomic absorption spectrometry after either microwave digestion according to EN 14083:2003 or dry ashing based on EN 14082:2003, using FAAS after APDC extraction or GFAAS. Arsenic was determined by hydride-generation AAS after dry ashing according to EN 14546:2005. Mercury was determined by cold-vapour AAS either directly or after pressure digestion according to EN 13806:2002. The paper reports total arsenic and total mercury only; it does not speciate inorganic arsenic, methylmercury, or inorganic mercury in the samples.

Participating laboratories were accredited to EN ISO/IEC 17025:2005. Quality assurance included certified reference materials, internal and external quality procedures, and interlaboratory proficiency tests including NIPH-NIH, FAPAS, and EU-RL-HM/JRC-IRMM programmes. The paper does not provide individual LOD or LOQ values; it reports left-censored statistics using the EFSA lower-bound, middle-bound, and upper-bound substitution approach.

Implications

Standards work: This source contributes a broad Polish-market occurrence dataset for infant formulae, infant cereals, baby snacks, ready-to-eat infant meals, fish-containing baby foods, fruit products, juices, and infant teas. For the gap-targeted non-rice dry baby cereal cell, the directly relevant groups are wheat gruel and mixed cereals; rice gruel is separately relevant to the rice-based dry baby cereal cell.

Courses: Useful for teaching why infant-food monitoring needs both product-form stratification and metal speciation discipline. The same source reports low total mercury in most cereal and formula categories but a distinct fish-food mercury signal, and it reports total arsenic without inorganic-arsenic speciation.

App: Supports Polish-market occurrence context for infant cereals and several ready-to-eat baby-food categories, with as-sold concentrations rather than prepared-as-fed concentrations.

Microbiome: Not addressed in this study.

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Verification notes

  • Ingested 2026-05-18 from the gap-driven auto-fetch queue. The same PDF was downloaded four times for baby-cereals-dry-non-rice Cd, iAs, tAs, and tHg wishlist cells; all four files have identical SHA-256 7d521247d2ced1b880a35d0648b4362666a3e8d0b813ce99bb5aac6fb90a74f8. This page uses the Cd-targeted ingested path as raw_path and treats the other three paths as duplicate fetches for the same DOI.
  • DOI identity check found no existing wiki source page for 10.15244/pjoes/59306; matches were only reference-list citations in other source markdown and wishlist-audit rows.
  • Speciation: frontmatter uses tAs and tHg because the paper measures total arsenic and total mercury. The exposure section discusses methylmercury and inorganic mercury as risk-assessment assumptions, not measured species.
  • Product routing follows the source’s product groups. Rice gruel and milk/rice-based products route to rice-based baby cereal context; wheat gruel and mixed cereals route to non-rice baby cereal context; biscuits route to teething/snack context; ready-to-eat vegetable, vegetable-meat, fish, fruit, and juice categories route to the closest infant-food product pages.

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