Overview
Dried herbs — the dehydrated leaves, flowers, and aerial plant parts of culinary and medicinal aromatic plants (oregano, basil, thyme, parsley, sage, rosemary, mint, chamomile, lemon balm, dill, marjoram, savory) — share the drying-concentration heavy-metals pattern with the broader Herbs And Spices category. The dominant feature is concentration: fresh herbs at 80-90% moisture content dry down to product at 8-12% moisture, producing a 7-10× per-mass concentration uplift on Pb, Cd, and other metals relative to the fresh-weight baseline. The current corpus loads 3 routed sources plus broader herbs-and-spices corpus reachable via the routing layer: Angelon-Gaetz 2018 NC home-investigation cohort (n=386, Lead in Spices, Herbal Remedies, and Ceremonial Powders Sampled from Home Investigations for Children with Elevated Blood Lead Levels — North Carolina, 2011–2018), Chime 2025 Nigerian-market spice trace-metal work (n=7, Assessment of toxic trace metal contamination in food spices sold in Nigerian markets), Cicero 2022 multi-origin 8-metal panel (n=13, Mineral and Microbiological Analysis of Spices and Aromatic Herbs), Fischer 2022 Polish mercury in spice plants (n=48, The Mercury Concentration in Spice Plants), Huff 2025 Lancaster PA spice survey (n=116, Heavy metals in spices from Lancaster, PA: arsenic, cadmium, and lead exposure risks and the need for regulation), Kowalska 2021 Polish 240-sample herb-spice-tea-coffee panel (The Safety Assessment of Toxic Metals in Commonly Used Herbs, Spices, Tea, and Coffee in Poland), LHAAC 2025 Australian Coordinated Sampling Project 41 (n=380, Coordinated Sampling Project 41: Microbial and Heavy Metal Detections in Herbs and Spices), NYS DOH 2019 spice-specific health-based guidance values (Technical Support Document for Derivation of Health-Based Guidance Values for Metals in Spices).
Why this commodity accumulates heavy metals
Dried herbs accumulate metals through two combined pathways: the live plant’s soil-uptake of Cd, Cr, Ni, and trace metals plus atmospheric deposition of Pb onto the leaf surface during the growing cycle, and the drying step that concentrates these metals on a per-mass basis by 7-10× through moisture removal. Drying is not contamination but a basis change; reporting consistency (dry weight vs fresh weight) matters when comparing values across sources. Atmospheric deposition is particularly relevant for herbs harvested in roadside or industrial-corridor settings, where surface Pb-and-Cd accumulate on the leaf during the growing cycle and then concentrate per-mass during drying. The Kowalska 2021 Polish dataset (n=240 across 37 herb species and 12 spice species) identified valerian root, lemon balm leaves, common sage, and chamomile flowers as higher-Pb species (The Safety Assessment of Toxic Metals in Commonly Used Herbs, Spices, Tea, and Coffee in Poland). The Cicero 2022 multi-origin work (n=13 across IT, SA, IN, IR, ID, VN) provides the strongest within-non-adulterated baseline across the full 8-metal panel (Mineral and Microbiological Analysis of Spices and Aromatic Herbs). The Australian Coordinated Sampling Project 41 (n=380 retail-and-import samples) is the largest single-jurisdiction recent dataset and demonstrates the population-scale per-species variance within commercial dried-herb product (Coordinated Sampling Project 41: Microbial and Heavy Metal Detections in Herbs and Spices). The Winiarska-Mieczan 2023 Polish n=432 herbs-and-single-component-spices Pb-Cd panel is referenced through the Fresh Herbs page as a paired-product comparison.
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) | Confidence | Key sources |
|---|---|---|---|---|
| Pb | n=7 | 100–2000 | medium | 1, 2 |
| Cd | n=6 | 50–500 | medium | 1, 2 |
| iAs | n=1 | 10–200 | low | — |
| tAs | n=4 | 20–300 | medium | 1 |
| tHg | n=3 | 1–50 | medium | 1, 2 |
| Ni | n=2 | 200–3000 | low | — |
| Al | n=2 | 1000–20000 | low | — |
| Cr | n=2 | 50–1000 | low | — |
| Sn | n=1 | — | — | — |
| U | data gap | — | — | — |
Ranges by source, region, and variety
The corpus characterises dried herbs through both directly-routed studies and the broader herbs-and-spices corpus. The Polish Kowalska 2021 dataset is the most species-diverse with 37 herb species and 12 spice species, identifying within-species variance of 2-3 orders of magnitude across Pb and Cd (The Safety Assessment of Toxic Metals in Commonly Used Herbs, Spices, Tea, and Coffee in Poland). The Australian LHAAC 2025 Coordinated Sampling Project 41 covers 380 retail-and-import samples with the 7-metal panel including Al specifically (Coordinated Sampling Project 41: Microbial and Heavy Metal Detections in Herbs and Spices). The North Carolina Angelon-Gaetz 2018 home-investigation cohort identified dried-herbs among the elevated-Pb spice samples in homes of children with elevated blood-lead levels (Lead in Spices, Herbal Remedies, and Ceremonial Powders Sampled from Home Investigations for Children with Elevated Blood Lead Levels — North Carolina, 2011–2018). The Lancaster PA Huff 2025 retail survey (n=116) included dried-herbs within the broader spice panel and reported the regulatory-gap analysis for the US market (Heavy metals in spices from Lancaster, PA: arsenic, cadmium, and lead exposure risks and the need for regulation). The Polish Fischer 2022 mercury-in-spice-plants work (n=48) provides the strongest single-jurisdiction tHg data for the dried-herb category (The Mercury Concentration in Spice Plants). Within-species pattern: valerian root, lemon balm leaves, common sage, and chamomile flowers consistently sit at the higher end of the Pb distribution; thyme, oregano, basil, and rosemary at the middle; parsley, dill, and chives at the lower end. Country-of-origin matters: Mediterranean dried herbs (Italy, Greece, Spain, Turkey) sit at the lower-to-middle of the distribution; some South Asian and Middle Eastern origins carry higher loads driven by soil and atmospheric Pb.
Processing effects
Drying is the dominant processing-driven concentration event, with fresh-to-dried transitions concentrating metals on a per-mass basis by 7-10× through moisture removal. This is a basis change rather than contamination. Sun-drying, oven-drying, and freeze-drying produce similar per-mass concentration outcomes; freeze-drying preserves color and flavor better but does not differ on metal load. Grinding and blending introduce minor metal pickup from equipment surfaces. Steam sterilisation, irradiation, and ethylene-oxide-based microbial-control treatments do not affect metal load. The dried-herbs category does not have the adulteration risk that ground-spices (turmeric, paprika, cinnamon) face; the adulteration mechanism (lead chromate pigment addition) does not apply to the green-and-grey-colored dried-leaf products that dominate the dried-herb category.
Ingredient-derivative risk
Whole-leaf dried herbs (whole dried oregano, whole basil leaves, whole sage) carry the baseline dry-weight metal load. Ground dried herbs (ground oregano, ground thyme) carry the same per-mass load. Herbal-tea preparations (dried chamomile flowers, dried lemon balm, dried mint) inherit the dried-herb load; brewing extracts a partial fraction into the cup (see Herbal/Botanical Infusions for the prepared-infusion view). Herbal-tincture and herbal-supplement preparations concentrate the parent herb’s metal load proportional to extraction concentration; supplement-grade herbal product from non-audited supply chains can carry Pb-and-Cd at concentrations of regulatory concern. Italian-seasoning, herbes-de-Provence, and similar blends inherit the highest-load component’s metals weighted by the inclusion ratio.
Mitigation options
Sourcing levers
Species selection within the dried-herbs category shifts the per-mass Pb-and-Cd distribution. Sourcing thyme, oregano, basil, rosemary, and parsley over valerian root, lemon balm leaves, and chamomile flowers reduces the per-mass load for buyers without species-specific functional requirements. Origin-country sourcing matters: Mediterranean-origin product sits at the lower-to-middle of the distribution. Specify supplier transparency on the species mix in blended product.
Agronomic levers
For brand-controlled-supply operations, soil pH management around 6.5 and avoidance of phosphate fertilisers with elevated Cd impurity reduce upstream Cd loading. Avoid sourcing from roadside or industrial-corridor production. Most agronomic interventions live with herb producers.
Processing levers
Validate equipment surfaces in grinding and blending operations. The drying method (sun, oven, freeze-dry) does not meaningfully differ on metal load. Avoid extended storage in unsealed bulk bins where atmospheric Pb dust deposition can accumulate on surface.
Formulation levers
For herb-blend formulations, characterise the metal load of each ingredient input on a dry-weight basis and weight to keep aggregate Pb-and-Cd at the lowest achievable per-serving level. Dilution with lower-metal carrier ingredients reduces per-serving exposure proportionally.
Testing and QC levers
Lot-level ICP-MS testing of every dried-herb lot at intake, with detection floors ≤ 100 ppb Pb and ≤ 50 ppb Cd. The LHAAC 2025 protocol is a useful population-screening reference (Coordinated Sampling Project 41: Microbial and Heavy Metal Detections in Herbs and Spices).
Packaging and storage levers
Packaging is not the dominant pathway for dried herbs. Standard food-grade glass, plastic, or paperboard does not affect the metal load.
Regulatory limits that apply
The Codex Alimentarius General Standard CXS 193-1995 does not set a dried-herbs-specific maximum. The EU Regulation 2023/915 applies a 1.5 mg/kg Pb maximum for “dried herbs and spices” (a slightly different category than the broader “spices” maximum) and 0.5 mg/kg Cd for the same category. The NYS Department of Health 2019 Technical Support Document derived health-based guidance values (Pb 0.21, Cd 0.21, Cr 0.41, iAs 0.10 mg/kg) that apply to dried herbs as well as spices (Technical Support Document for Derivation of Health-Based Guidance Values for Metals in Spices). FDA has issued occasional import alerts and enforcement actions on dried-herb product but does not maintain a category-specific action level.
References
Works cited in this page’s text, in first-appearance order. This is not the full corpus for this page; it is only what the prose above draws on. The complete set of sources is listed under Sources below. 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.
- Lead in Spices, Herbal Remedies, and Ceremonial Powders Sampled from Home Investigations for Children with Elevated Blood Lead Levels — North Carolina, 2011–2018Government
- Assessment of toxic trace metal contamination in food spices sold in Nigerian marketsReview
- Mineral and Microbiological Analysis of Spices and Aromatic HerbsReview
- The Mercury Concentration in Spice PlantsReview
- Heavy metals in spices from Lancaster, PA: arsenic, cadmium, and lead exposure risks and the need for regulationReview
- The Safety Assessment of Toxic Metals in Commonly Used Herbs, Spices, Tea, and Coffee in PolandReview
- Coordinated Sampling Project 41: Microbial and Heavy Metal Detections in Herbs and SpicesGovernment
- Technical Support Document for Derivation of Health-Based Guidance Values for Metals in SpicesGovernment
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 | Winiarska-Mieczan et al. 2023. The Content of Cd and Pb in Herbs and Single-Component Spices Used in Polish Cuisine, Biological Trace Element Research | 2023 | Peer-reviewed | Cd and Pb in 100 dried-herb samples across 9 species from Polish retail, with dried form carrying highest Cd and Pb among herb forms |
| 2 | Fischer et al. 2022. The Mercury Concentration in Spice Plants, Processes | 2022 | Peer-reviewed | Polish mercury in 48 spice-and-herb plant samples; strongest tHg data |
| 3 | Gill et al. 2021. The Trouble With Spices: Heavy Metals in 15 Herbs and Spices, Consumer Reports | 2021 | NGO report | US Pb, Cd, tAs occurrence in 126 individual products covering 38 brands and 15 herb/spice types from the US retail market (n=126) |
| 4 | Kowalska 2021. The Safety Assessment of Toxic Metals in Commonly Used Herbs, Spices, Tea, and Coffee in Poland, International Journal of Environmental Research and Public Health | 2021 | Peer-reviewed | Polish 37-herb-12-spice (n=240) 4-metal panel; species-variance evidence |
| 5 | Liu et al. 2018. Speciation and bioaccessibility of arsenic in traditional Chinese medicines and assessment of its potential health risk, Science of the Total Environment | 2018 | Peer-reviewed | CN tAs, iAs occurrence in Twenty-four Chinese patent medicines and sixty Chinese herbal medicines purchased from a Beijing drugstore. The patent medicines included… (n=84) |
| 6 | Adams et al. 2017. Genotoxic studies of cooked and uncooked processed spices using Allium cepa Test, International Journal of Advanced Research in Biological Sciences | 2017 | Peer-reviewed | NG Pb, Cd, Cr, Ni occurrence in Market-sold curry, thyme, suya, and pepper-soup spices purchased in Ogun State, Nigeria (n=4) |
| 7 | Kočevar et al. 2017. Accumulation of heavy metals from soil in medicinal plants, Arhiv za higijenu rada i toksikologiju | 2017 | Peer-reviewed | SI/EU Pb, Cd, Zn, Cu, Fe, Mn occurrence in Above-ground parts of four medicinal plant species collected at eight Meža Valley locations in Slovenia, with paired topsoil… (n=32) |
| 8 | Mirosławski et al. 2017. Determination of the Cadmium, Chromium, Nickel, and Lead Ions Relays in Selected Polish Medicinal Plants and Their Infusion, Biological Trace Element Research | 2017 | Peer-reviewed | PL Cd, Cr, Ni, Pb occurrence in Five peppermint-leaf preparations and five chamomile-blossom preparations from Polish pharmacy retail, with three package-level samples per producer; all… (n=10) |
| 9 | Dghaim et al. 2015. Determination of Heavy Metals Concentration in Traditional Herbs Commonly Consumed in the United Arab Emirates, Journal of Environmental and Public Health | 2015 | Peer-reviewed | AE Pb, Cd, Cu, Fe, Zn occurrence in Seven traditional herbs (parsley n=13, basil n=11, sage n=11, oregano n=11, mint n=13, thyme n=13, chamomile n=9) purchased… (n=81) |
| 10 | Khan et al. 2013. Toxic and some essential metals in medicinal plants used in herbal medicines: A case study in Pakistan, African Journal of Pharmacy and Pharmacology | 2013 | Peer-reviewed | PK Pb, Ni, Cd, Cr occurrence in Eight medicinal plant species collected from two locations within a 20 km radius of Kallar Kahar Lake, Punjab,… (n=48) |
| 11 | Kulhari et al. 2013. Investigation of heavy metals in frequently utilized medicinal plants collected from environmentally diverse locations of north western India, SpringerPlus | 2013 | Peer-reviewed | IN Mn, Cr, Pb, Fe, Cd, Ni, Co, Zn, Hg occurrence in Stem and leaf samples from ten medicinal plant species collected from Haryana and Rajasthan, India, including Jhunjhunu, Churu,… (n=20) |
| 12 | Shah et al. 2013. Comparative Study of Heavy Metals in Soil and Selected Medicinal Plants, Journal of Chemistry | 2013 | Peer-reviewed | PK Fe, Ni, Mn, Zn, Cu, Cd, Cr, Pb occurrence in Leaves, stems, and roots of four medicinal plant species collected from polluted and unpolluted sampling points in District… (n=24) |
| 13 | Barthwal et al. 2008. Heavy Metal Accumulation in Medicinal Plants Collected from Environmentally Different Sites, Biomedical and Environmental Sciences | 2008 | Peer-reviewed | IN Pb, Cd, Cr, Ni occurrence in Five medicinal plant species collected from three Lucknow, India site types (heavy traffic area, residential area, industrial area),… (n=15) |
| 14 | Khan et al. 2007. Effect of Environmental Pollution on Heavy Metals Content of Withania somnifera, Journal of the Chinese Chemical Society | 2007 | Peer-reviewed | PK Cr, Pb, Cu, Cd, Fe, Ni, Mn occurrence in Withania somnifera roots, stems, leaves, and fruits, plus paired soils, collected from three locations of N.W.F.P./Peshawar Valley, Pakistan;… |
| 15 | Divrikli et al. 2006. Trace heavy metal contents of some spices and herbal plants from western Anatolia, Turkey, International Journal of Food Science and Technology | 2006 | Peer-reviewed | TR Cu, Cd, Pb, Ni, Cr, Fe, Mn, Zn occurrence in Eleven spice and herbal plant species collected from 50 farmers in western Anatolia, Turkey, June-October 2003; four samples… (n=44) |
Update history
The five most recent substantive edits to this page, classified major (evidence or structure moved), correction (a published value or statement was wrong and has been fixed), or minor (narrative rewritten without changing the underlying evidence). Each description is derived from what the edit did to this page; the linked commit is the authoritative record, routine regeneration passes are excluded, and 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 | Change | Description |
|---|---|---|---|
| e317189 | 2026-08-11 | correction | 8 sources added; contamination-profile values revised; 17 sections added |