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Yu 2023 - Zhejiang beans toxic elements

Yu, Pan, and Han measured arsenic, cadmium, chromium, mercury, and lead in 692 dried bean samples from local commercial markets in Zhejiang Province, southeast China. The bean panel included black bean, broad bean, mung bean, soybean, red bean, kidney bean, and pea. The occurrence measurements are total/unspecified arsenic and total/unspecified mercury; the paper’s health-risk model estimates inorganic arsenic from total arsenic using a 72% assumption from prior crop literature, but it does not measure inorganic arsenic speciation in these bean samples.

Key numbers

The abstract reports average levels across all 692 bean samples of As 0.0349 mg kg−1, Cd 0.0379 mg kg−1, Cr 0.246 mg kg−1, Hg 0.0019 mg kg−1, and Pb 0.0246 mg kg−1. Table 3 reports bean-type statistics in mg/kg:

Bean typenElementMedianMeanMaximumP95No. > ML
Black bean307Cd0.03360.04810.980.1134
Black bean307Cr0.160.3224.61.0611
Black bean307Hgnot reported0.00190.0370.00437not applicable
Black bean307Pb0.00450.02530.30.1033
Black bean307As0.009870.06015.710.052not applicable
Broad bean88Cd0.0050.01590.290.04481
Broad bean88Cr0.10.181.050.672
Broad bean88Hgnot reported0.001460.00590.00156not applicable
Broad bean88Pbnot reported0.01880.1350.06870
Broad bean88As0.0030.01970.290.083not applicable
Mung bean43Cd0.004090.02740.4630.0772
Mung bean43Cr0.07210.1010.3790.2410
Mung bean43Hgnot reported0.0006320.001650.00085not applicable
Mung bean43Pb0.01390.03020.3530.06771
Mung bean43Asnot reported0.01370.10.09not applicable
Soybean104Cd0.02260.04980.4890.1694
Soybean104Cr0.1860.2671.510.723
Soybean104Hgnot reported0.002130.03710.0088not applicable
Soybean104Pbnot reported0.02670.1960.1380
Soybean104Asnot reported0.01330.170.05not applicable
Red bean51Cd0.004530.03010.6480.1771
Red bean51Cr0.1260.1640.9650.4360
Red bean51Hgnot reported0.00120.01430.00513not applicable
Red bean51Pb0.008610.03080.190.170
Red bean51As0.006130.01380.140.042not applicable
Kidney bean12Cd0.01650.03640.160.160
Kidney bean12Cr0.1320.2221.61.61
Kidney bean12Hgnot reported0.002580.01940.0194not applicable
Kidney bean12Pb0.02740.04980.1830.1830
Kidney bean12Asnot reported0.00640.0180.018not applicable
Pea87Cd0.0190.02230.2520.0521
Pea87Cr0.06690.1521.180.66not reported
Pea87Hgnot reported0.002740.0380.0079not applicable
Pea87Pbnot reported0.01450.07570.050
Pea87Asnot reported0.01390.120.066not applicable

The Results text identifies the highest mean concentrations as Cd 0.0498 mg/kg in soybean, Cr 0.322 mg/kg in black bean, Hg 0.0027 mg/kg in pea, Pb 0.0498 mg/kg in kidney bean, and As 0.0601 mg/kg in black bean. It also states that all bean types except pea and kidney beans had at least one Cd result exceeding the maximum limit used by the authors, and Cr exceedances occurred in black bean, broad bean, soybean, and kidney bean.

Table 4 reports Monte Carlo target hazard quotients as exposure context, not occurrence values. At P95, total hazard-index sums were children 1.1, teens 1.05, and adults 0.54; the certainty of HI greater than 1 was 12.64% for children, 11.54% for teens, and 1.01% for adults. The model used total arsenic measurements but converted them to inorganic arsenic by assuming 72% of total As was inorganic As.

Methods (brief)

Bean samples were purchased from local commercial markets in Hangzhou, Huzhou, Jiaxing, Jinhua, Lishui, Ningbo, Quzhou, Shaoxing, Taizhou, Wenzhou, and Zhoushan. Ground samples were digested by closed microwave-assisted nitric-acid digestion, dried near dryness at 150 °C, re-diluted to 20 mL, and analyzed by ICP-MS for As, Cd, Cr, Hg, and Pb. Quality control used soybean flour certified reference material GBW10013; reported LOQs were As 0.0006 mg/kg, Cd 0.0008 mg/kg, Cr 0.0006 mg/kg, Hg 0.0001 mg/kg, and Pb 0.0008 mg/kg.

Implications

This source supplies Zhejiang-market dried-bean occurrence evidence for total arsenic, cadmium, total chromium, total mercury, and lead. It is especially useful for beans and soy routing because the sample set includes 104 soybean samples and several other legume categories. Downstream synthesis should keep measured total arsenic separate from the paper’s modeled inorganic-arsenic assumption, and should not treat total chromium as Cr(VI).

Verification notes

  • PDF text was extracted with pdftotext -layout; abstract, sampling section, quality-control Table 1, Table 3, Table 4, and the results prose were checked in /tmp/f3_texts/foods-12-03300.txt.
  • DOI 10.3390/foods12173300, raw handle MFK_foods-12-03300, and cite-key checks found no existing source page before creation.
  • Table 3 values are preserved as mg/kg; no conversion to dry-weight normalized or wet-weight units was performed.
  • Speciation: arsenic was measured as total/unspecified As and mercury as total/unspecified Hg. The source’s health-risk model assumes 72% inorganic arsenic, but the occurrence data are not measured iAs.
  • Brand firewall: samples were purchased from markets but no brand-level contamination values are reported.
  • Frontmatter slugs were checked against docs/gpt-collaboration/taxonomy-snapshot.md; narrow slugs for black bean, broad bean, mung bean, red bean, kidney bean, and pea are not available, so broad beans/legumes routing is used with soy added for soybean rows.

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.

CommitDateDescription
1476f442026-06-09ingest: cacic2019-hemp-heavy-metals fresh from MFK/June 9