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Hao et al. 2022 — Probabilistic health risk from metals in rice, Xiangtan County, China

Hao and colleagues measured total arsenic (tAs), inorganic arsenic (iAs), Pb, Cd, Cr, and total Hg in 220 rice samples from Xiangtan County, Hunan Province, China, a multi-mining county with rice cultivation. The paper is routeable as rice-bulk-grain occurrence evidence because Table 2 reports rice concentrations directly; mining and soil context should be treated as source-attribution context rather than product concentration data. The rice occurrence finding is dominated by Cd, tAs, and iAs, with iAs kept separate from tAs and total Hg kept separate from methylmercury.

Key numbers

Table 2 reports concentration characteristics for rice (N=220):

Element/speciesMean ± SD, mg·kg−1Range, mg·kg−1Limited value, mg·kg−1PELCVSkewnessProbability distribution
tAs0.34±0.20[0.125,1.84]0.299.1%167.9%4.26Lognormal
iAs0.15±0.09[0.045,0.83]0.222.7%168.5%3.39Lognormal
Pb0.08±0.15[0.001,1.02]0.210.5%53.8%3.72Lognormal
Cd0.48±0.50[0.001,2.73]0.272.7%96.2%2.38Lognormal
Cr0.6±1.56[0.001,12.38]110.0%38.4%5.18Lognormal
tHg0.0023±0.0020[0.0001,0.0106]0.020.0%117.7%1.91Normal

Additional source-reported values:

  • The source states that the iAs/tAs ratio in the study was 44.1%.
  • Method detection limits were tAs 0.01 mg·kg−1, iAs 0.02 mg·kg−1, Hg 0.003 mg·kg−1, Pb 0.02 mg·kg−1, Cd 0.002 mg·kg−1, and Cr 0.05 mg·kg−1.
  • Table 1 reports bioaccessibility inputs from related studies: iAs 39.90±8.30% with range [8.63,68.5], Pb 23.94±11.00% with range [7.58,48.34], Cd 35.25±20.06% with range [6.67,87.50], and Cr 9.87±5.66% with range [3.26,32.04].
  • The source reports probability of non-carcinogenic risk exceeding 1 via rice consumption as 72% for adults and 78% for children. It reports probability of carcinogenic risk as 100%.
  • Table 4 reports total HI/TCR point estimates and uncertainty values: adult HI point estimate 2.74, P5 0.67, P50 1.43, P95 5.50; child HI point estimate 2.86, P5 0.43, P50 1.49, P95 6.21; adult TCR point estimate 5.2E-03, P5 7.4E-04, P50 2.8E-03, P95 2.1E-02; child TCR point estimate 5.4E-03, P5 5.5E-04, P50 2.9E-03, P95 2.3E-02.

Methods (brief)

The authors collected rice from 220 sampling sites in Xiangtan County, with five subsamples per site mixed into one sample. Rice was dried to less than 13% moisture, threshed to brown rice, ground, and homogenized. Total Pb, Cd, and Cr were measured after HNO3-HClO4 digestion by ICP-MS; total As used HNO3-HClO4 wet digestion and AFS; Hg used microwave digestion and AFS; and iAs was extracted with 0.15 mol/L HNO3 and quantified by LC-AFS. Quality control used national rice reference material GBW10043, one reference material per 10 samples, and triplicate analyses with RSD less than 5%. The study also used a bioaccessibility-adjusted health-risk model, Monte Carlo simulation with 10,000 iterations, sensitivity analysis, and ArcGIS spatial mapping.

Implications

This source contributes China-market rice occurrence evidence for tAs, iAs, Cd, Pb, Cr, and total Hg, with arsenic speciation resolved and the product matrix tied to brown rice from a multi-mining county. It is useful for rice geographic-variance and supply-chain-context work, especially because the paper links rice concentrations to mining-area spatial patterns. It should not be silently pooled into a United States rice benchmark without an explicit cross-market rationale, and its total Hg result should not be treated as methylmercury.

Wiki pages this source may touch

Verification notes

  • This was a DOI duplicate of an existing source page, so the page was merge-enhanced from the manual-fetch PDF at raw/Manual Fetch Kimi /June 8 New Folder With Items 3 2/Probabilistic-health-risk-assessment-of-inorganic-arsenic-and-some-heavy-metals-in-rice-produced.pdf; the MFK handle was added to near_duplicates.
  • PDF text extracted with pdftotext -layout; the extracted text contained the title, DOI, methods, Table 1, Table 2, Table 4, discussion, and conclusions.
  • DOI verified from the PDF as 10.1007/s11356-021-16583-7; DOI grep found this existing page before enhancement.
  • Table 2 values were checked against the extracted text. Units are preserved as mg·kg−1; the previous page’s ppb/µg/kg conversions were removed.
  • Speciation: arsenic is reported as both tAs and iAs, which are kept separate. Mercury is total Hg only; no methylmercury value is reported. Chromium is total Cr only; no Cr-VI value is reported.
  • Soil and mining-area information is source-attribution context. Only rice concentration values were routed as product occurrence evidence.
  • Frontmatter product and ingredient slugs were checked against docs/gpt-collaboration/taxonomy-snapshot.md; no new slug was invented.
  • Autonomous audit 2026-06-09: removed mining-area-rice from matrices because it is a study-context descriptor, not a standard matrix slug; mining-area provenance is captured in the body and in this notes block.
  • Autonomous audit 2026-06-09 flagged Adult HI P95 as 5.51 (per narrative on p.11515) vs the wiki’s 5.50 (per Table 4 on p.11517); verified against PDF — Table 4 reports 5.50 and Table 4 is the canonical tabular source. The narrative line (“5.51 for adults and … 6.16 for children”) is internally inconsistent with the table (6.21 for children), so the wiki tracks Table 4 throughout. Finding rejected as false positive.

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.

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b0f3d382026-06-12batch | corpus rescreen b04 old terminal skips