Frozen peas

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.

FSA/Fera measured this ingredient or non-infant-specific food composite in Table 6 of the FS102048 survey. Exact concentration values remain in progress until Table 6 is parsed into structured ingredient rows with less-than and semi-quantitative flags preserved. fsa2016-infant-food-formula-metals-survey

Why this commodity accumulates heavy metals

Peas (Pisum sativum) are a leguminous crop that form symbiotic relationships with nitrogen-fixing bacteria in root nodules, a root architecture that also facilitates contact with soil metal fractions including cadmium and lead. Legumes as a plant family generally accumulate Cd from soil at higher rates than cereal crops on equivalent soils, because the organic acids and phytosiderophores exuded from legume roots to support nitrogen fixation also mobilize divalent metals including Cd from the rhizosphere. However, within the legume family, peas accumulate Cd at lower rates than dried beans or lentils because the commercially harvested portion (the immature green seed and pod) is taken earlier in the plant’s growth cycle before maximum mineral accumulation in the mature seed. The pod and immature seed together carry less Cd than mature dried peas from the same plant, providing a natural dilution relative to dried legume products. Lead uptake in peas occurs primarily through soil contact and atmospheric deposition onto pod surfaces and is largely a surface contamination pathway, so the contribution of Pb to total plant burden is related to soil Pb and atmospheric deposition at the field site rather than to plant physiology specifically. Nickel is detected in frozen peas at concentrations higher than most metals in this matrix, consistent with Ni being a cofactor in the legume nitrogen-fixation enzyme system (urease), which may facilitate Ni accumulation in legume tissues at rates higher than in non-leguminous crops.

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.

Routing

This node is linked from the ingredient index and source routing list.

Contamination Profile State

The machine-readable contamination profile is in_progress. Ingredient-level values belong here once parsed; finished-product values belong on the relevant product-category page.

FDA TDS FY2018-FY2020 Evidence

FDA’s FY2018-FY2020 Total Diet Study dataset includes this page’s routed matrix as TDS Food 46, “Peas, green, frozen, boiled.” The normalized row-level data is stored in data/evidence/fda_tds_fy2018_2020_element_results_samples.csv, with per-food/per-analyte summaries in data/evidence/fda_tds_fy2018_2020_summary_by_food_analyte.csv. Concentrations are retained as FDA reported them, with reporting limits preserved separately; reported zeroes are not rewritten as <LOD without a source-specific rule. fda2022-tds-elements-fy2018-fy2020

FDA TDS FY2018-FY2020 Occurrence Values

FDA Total Diet Study FY2018-FY2020 reports prepared/composite-food concentration distributions for this ingredient as TDS food “Peas, green, frozen, boiled” (fda2022-tds-elements-fy2018-fy2020). Values are in ppb-equivalent on the basis FDA reported. The full sample-level data are stored in data/evidence/fda_tds_fy2018_2020_element_results_samples.csv; per-analyte distributions in data/evidence/fda_tds_fy2018_2020_summary_by_food_analyte.csv. These distributions count as one source under persistent-wiki-ingest-rule synthesis discipline; numerical values stay in body scratch until a second independent source is integrated.

Ranges by source, region, and variety

Geographic variation in frozen pea metal concentrations is primarily driven by soil Cd and soil Pb levels in the producing region. Peas grown on intensively phosphate-fertilized soils carry higher Cd than those grown on organically managed or low-input soils, as phosphate fertilizers are a consistent Cd source regardless of crop type. European pea production on legacy agricultural soils in intensively farmed regions shows higher Cd than production from lower-input systems, though the difference is moderated by the fact that commercial peas are harvested immature and the Cd accumulation curve is not yet at its maximum. Cultivar-level variation in Cd uptake within peas has been noted in some agronomic studies but is not yet characterized at the product level in the current source corpus. The FDA TDS FY2018-FY2020 measured frozen peas (“Peas, green, frozen, boiled”) as a composite reflecting US production and import sources (n=3) fda2022-tds-elements-fy2018-fy2020, providing one reference distribution; UK and European distributions from the FSA/Fera survey represent a separate sourcing context.

Processing effects

Blanching before freezing is standard practice for frozen peas; the blanching step involves brief immersion in hot water or steam to inactivate enzymes and preserve color and texture. Blanching leaches water-soluble metal fractions from pea tissue into the blanch water. For cadmium, which is present partly in water-soluble organic complexes in plant tissue, blanching may reduce Cd concentrations by a modest percentage relative to the raw pea, though the effect is not well characterized quantitatively in the peer-reviewed literature at the level of commercial processing conditions. Boiling of blanched frozen peas before consumption (as captured in the FDA TDS prepared-food measurement) adds a further leaching step; the FDA TDS value for “Peas, green, frozen, boiled” therefore represents the cumulative effect of all processing and preparation steps and is likely lower in Cd and Pb than raw field peas would show. Nickel in the boiled product reflects the retained fraction after blanching and boiling, though the magnitude of the leaching reduction for Ni specifically is not quantified in the current corpus.

Ingredient-derivative risk

Frozen peas used as an ingredient in composite ready meals, baby food purees, and vegetable blends carry metal concentrations into those products proportional to the pea weight fraction. Pea protein concentrate, produced by extracting and drying the protein fraction from field or marrowfat peas, would be expected to concentrate metals relative to whole peas, since protein-binding concentrations metals during isolation, though this derivative is produced from mature dried peas rather than from the frozen immature pea represented by this commodity page. Split peas and pea flour derived from mature dry peas carry higher Cd than frozen green peas.

Mitigation options

Sourcing levers

Specifying field origin from regions with documented low soil Cd, or from production systems subject to fertilizer Cd limits (such as the EU limit for Cd in phosphate fertilizers), reduces the intrinsic Cd burden in the raw peas. Suppliers operating within EU Regulation frameworks for fertilizer Cd are subject to a maximum of 60 mg Cd per kg P2O5 in phosphate fertilizers (with a trajectory to tighten to 40 mg/kg P2O5 in coming years), providing a supply-chain lever that acts upstream of the crop.

Agronomic levers

Cultivar selection favoring low-Cd-accumulation pea varieties can reduce Cd uptake on a given soil, but the agronomic literature on within-species Cd variation in peas is less developed than for wheat and rice, and specific cultivar recommendations are not available from the current corpus.

Processing levers

Optimizing blanching conditions (water volume, temperature, and duration) to maximize cadmium leaching into blanch water, with subsequent disposal of that water, offers a processing-stage reduction opportunity. The effect magnitude has not been characterized for commercial frozen pea processing in the current corpus, so this is a research-supported hypothesis rather than a quantified lever.

Formulation levers

No quantified data on this lever in the current corpus; section will be expanded when relevant evidence is ingested.

Testing and QC levers

Lot-level testing of incoming raw peas by ICP-MS for Cd and Ni before blanching and freezing provides the most actionable quality signal for manufacturers. Given the low Cd concentrations observed in the FDA TDS (median approximately 1.5 ppb, max 3.2 ppb, n=3) fda2022-tds-elements-fy2018-fy2020, routine lot testing should focus on Ni as the analyte most frequently above detection in this matrix, followed by Cd where a certified program standard or customer specification requires it.

Packaging and storage levers

No quantified data on this lever in the current corpus; section will be expanded when relevant evidence is ingested.

Regulatory limits that apply

Under EU Regulation as updated in eu2023-contaminants-maximum-levels, the maximum level for Pb in vegetables (general) is 0.10 mg/kg wet weight, and for Cd in vegetables (general) it is 0.050 mg/kg wet weight. These limits apply to frozen peas as a vegetable product placed on the market. There is no specific EU maximum level for Ni in vegetables at the time of this writing, despite Ni being the most consistently detectable analyte in this matrix in the FDA TDS data. In the United States, FDA has not established action levels for metals in frozen vegetables; the FDA TDS provides a reference distribution against which new measurements can be compared, but no enforcement threshold exists for this matrix.

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]*.

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.