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Heavy Metal Index

Uptake and dietary toxicity of arsenic in rice genotypes: Effect of organic and inorganic amendments

Source

This open book chapter reports total arsenic uptake in two rice genotypes, Kainat and Basmati-385, under gypsum, farmyard manure, cow dung, lignite, biogas slurry, biomaterial, and untreated control conditions.

Page snapshot
Cited by4 pages
Metals measured1
Evidence tierB
Year2024

Overview

This open book chapter reports total arsenic uptake in two rice genotypes, Kainat and Basmati-385, under gypsum, farmyard manure, cow dung, lignite, biogas slurry, biomaterial, and untreated control conditions. The routeable food endpoint is rice grain total As on a dry-weight basis, not rice milk. Cow dung and biomaterial treatments produced the lowest grain As values in the printed table, including 0.04 mg/kg for Kainat under biomaterials and 0.09 mg/kg for Basmati-385 under biomaterials.

Key numbers

  • Experiment scope: two rice genotypes (Kainat and Basmati-385) across seven treatments: control, gypsum, farmyard manure, cow dung, lignite, biogas slurry, and biomaterials.
  • Irrigation challenge: arsenic-contaminated irrigation water reported as 45 mg/L, applied at transplanting, tillering, and milking stages.
  • Grain As concentrations from Table 1, dry weight, mg/kg:
    • Control: Kainat 1.2; Basmati-385 1.2.
    • Gypsum: Kainat 0.5; Basmati-385 0.9.
    • Farmyard manure: Kainat 0.7; Basmati-385 0.7.
    • Cow dung: Kainat 0.2; Basmati-385 0.1.
    • Lignite: Kainat 1.1; Basmati-385 1.4.
    • Biogas slurry: Kainat 1.6; Basmati-385 1.0.
    • Biomaterials: Kainat 0.04; Basmati-385 0.09.
  • The abstract states that mean grain As for cow-dung and biomaterial treatments in both genotypes was below the cited WHO/FAO rice-grain limit of 0.2 mg/kg dry weight.
  • The abstract reports shoot As ranges of 3.1-28 mg/kg dry weight for Kainat and 1.7-16 mg/kg dry weight for Basmati-385, with the minimum under cow dung and biomaterials.

Methods (brief)

The authors grew two contrasting rice genotypes in an amendment experiment with arsenic-contaminated irrigation water. Root, shoot, and grain samples were digested with nitric acid, and plant-tissue arsenic was determined by hydride generation atomic absorption spectrometry. The chapter reports total arsenic in tissues; it does not separate inorganic arsenic, DMA, MMA, or other arsenic species. Statistical comparison between treatments used analysis of variance.

Implications

  • Rice: provides treatment-level dry-weight grain total-As values for two Pakistani rice genotypes under an experimental arsenic-irrigation challenge.
  • Mitigation: cow dung and biomaterials are the main low-As treatments in the printed grain table.
  • Standards workbench: not a market-occurrence survey and not an iAs measurement; do not substitute these tAs values for inorganic arsenic.
  • Product routing: despite the auto-fetch target, this is rice-grain evidence, not rice-milk evidence.

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Verification notes

  • The text layer has OCR ambiguity for some shoot As values in Table 1, so this page anchors only the legible grain As values and the abstract’s shoot-range statement.
  • The conclusion section appears to contain a copy-editing carryover about mushroom fruit bodies; this conflicts with the rest of the chapter and is not used for routing.
  • The source reports total As only. It cannot support an inorganic-arsenic row without a separate speciation assumption, which is not allowed.

Update history

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