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Heavy Metal Index

mycotoxins and heavy metals in rice, maize,

Source

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Page snapshot
Cited by8 pages
Metals measured5
Evidence tierB
Year2024

Overview

This source page is a mechanical bulk-ingest record for a PDF in the research-pulls corpus. It preserves source-level identity, routeable product/analyte scope, and exact extracted numeric lines for later human or fresh-context audit. It does not derive HMTc thresholds, percentiles, or brand-by-brand comparisons.

Key numbers

The worker extracted the full PDF text with layout preservation twice and compared extraction hashes before commit. The following lines are copied from numeric/table-bearing regions of the PDF and retain the source units and wording where legible:

  • A total of 300 samples consisting of rice (n = 82), maize (n = 50), soybeans (n = 78), and
  • vortexed for 5 min. Then, 8.4 mL of ACN containing 1% HCOOH was added, and the
  • the digestion was as shown in Table S1. After the digestion, the temperature was reduced to
  • with 0.1% HCOOH to detect three FBs and 5 mmol/L CH3COONH4 in H2O for the remaining
  • mycotoxins. The gradient elution program was as follows: 0-3 min, 10% A; 3-5 min, 70%-
  • 90% A; 5-6 min, 90% A; 6-6.1 min, 90%-10% A; and 6.1-8 min, 10% A. The flow rate was
  • high-purity nitrogen (99.99%). The collision gas was high-purity argon, and the capillary
  • parameters are detailed in Table S2. Heavy metal analysis was performed on an ICAP RQ
  • Alimentarius Commission (CAC), the European Union, and the U.S. were used. Table S3
  • between mean values using SPSS 16.0 (SPSS Inc., IL, USA), with P<0.05 indicating
  • LOD, it was considered as “not detected” and replaced by 1/2 LOD when calculating the
  • mean value of the contaminants (38).
  • The LOD and LOQ values for the developed method are shown in Table S4. As for
  • the slope ratio ranged from 0.31 to 3.6 (Table S5), demonstrating a matrix effect. Therefore,
  • all standard curves). The LODs ranged from 0.05 to 4.0 μg/kg for the 12 mycotoxins
  • 0.8% and 9.7%, respectively. For ICP-MS analysis, the LODs ranged from 0.001 to 0.02
  • mg/kg, and the R2 prepared with standard solutions for Pb, Cd, Cr, As, and Hg were ≥ 0.994.
  • and 9.5%, respectively. All the contaminations of spiked recovery rate were between
  • 80~120%, and the RSDr and RSDR were all < 10%.
  • (72.33%) was the highest, followed by OTA (59.33%), 3-ADON (39.00%), and FB3
  • for each), FB2 (19.67%), ZEN (18.00%), and AFG2 (6.33%). For heavy metals, As had the
  • highest detection rate (91.33%), while for Cd, Cr, and Pb, the contamination rates were
  • 85.00%, 39.00%, and 18.67%, respectively. Hg minimally contaminated the samples, as
  • detected in only 2 (0.67%) samples. Within the rice samples (n = 82), OTA was the most
  • common detected mycotoxin (73.17%), followed by DON (48.78%), and the remaining
  • metals analyzed, As had the highest detection rate (100.00 %) in rice. The detection rates for
  • the other heavy metals were as follows: Cd at 90.24%, Cr at 26.83%, Pb at 12.20%, and Hg at
  • 1.22% (Figure 2B). For maize samples (n = 50), FB1 (98.00%) was the most detected
  • mycotoxin, followed by DON and FB2 (80.00% for each), OTA (68.00%), and the remaining
  • mycotoxin detection rates ranged from 4.00% to 58.00%, while 15-ADON was not detected.
  • On the other hand, As had the highest detection rate (88.00%), and the rest were in the order
  • of Cd (30.00%), Pb (10.00%), and Cr (6.00%), while Hg was not detected (Figure 2C). In
  • OTA, which was detected in 66.67% of the samples. Other mycotoxins were detected in a
  • range between 1.28% to 46.15%. The detection rate of Cd among the five heavy metals was
  • the highest (98.72%), and the remaining were in the order of Cr > As > Pb > Hg, with
  • wheat flour samples (n = 90), DON was at the highest detected rate of all mycotoxins
  • (86.67%), while the remaining mycotoxins were detected in a range between 3.33% and
  • 35.56%. Among the heavy metals, Cd was found at the highest rate of 98.89%, and the rest
  • was in the order of As > Pb > Cr, with detection rates of 83.33%, 26.67%, and 21.11%,
  • detection rates of 98.00% and 80.00%, respectively. ZEN had an overall low detection rate
  • but was more frequently found in rice samples at a detection rate of 34.15%. OTA was
  • frequently in wheat flour (35.56%). Furthermore, the highest detection rate for Cr was found

Methods (brief)

  • chromatography-tandem mass spectrometry (UPLC-MS/MS) and inductively coupled plasma
  • mass spectrometry (ICP-MS) methods to quantify the concentration of 12 mycotoxins and
  • five heavy metals in rice, maize, soybeans, and wheat flour samples marketed in Shanghai.
  • samples (100%) were contaminated with two or more contaminants, and 77.3% of the
  • samples were co-contaminated with more than four contaminants. In cereals and cereal
  • tandem mass spectrometry (UPLC-MS/MS) and inductively coupled plasma mass
  • spectrometry (ICP-MS) to analyze four typical grains and grain products (rice, maize,
  • had a purity > 98%. The high-purity solvents (HPLC grade) of methanol (MeOH),
  • (Waters, MA, USA) was used for the UPLC-MS/MS analysis. An ICP-MS spectrometer
  • Sample digestion was conducted using a MARS6 microwave digestion system (CEM, NC,
  • Instrument (Troody Analytical Instrument Co., Ltd, Shanghai, China). The sample solution
  • China) was used for supersonic-assisted extraction. Samples were weighed on an AL104
  • 2.2 Sample collection and extraction
  • A total of 300 samples consisting of rice (n = 82), maize (n = 50), soybeans (n = 78), and
  • wheat flour (n = 90) were collected from over 100 supermarkets and farmers’ markets located
  • (the map was drawn using Adobe Photoshop CC-Adobe Inc, USA, CA). The collected
  • samples can be traced back to 232 manufacturers and 219 sample origins. To ensure sample
  • representativeness, various samples of the same batch were randomly selected at each site.

Implications

This page makes the source discoverable for category-level evidence routing. Values remain source-native and should be used only with the stated matrix, species, basis, geography, and censoring context from the paper. The page does not convert total mercury to methylmercury or use total arsenic as inorganic arsenic.

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Verification notes

  • Identity check: DOI, raw handle, candidate cite-key, and SHA-256 were compared against existing wiki/sources/ pages before creation.
  • Full-PDF read: pdftotext -layout was run on the full PDF twice; extracted text hashes matched before the page was written.
  • Numeric verification: numeric/table-bearing lines were selected mechanically from the verified extraction and preserved without unit conversion or rounding.
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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.

CommitDateChangeDescription
b01ec52c2026-08-04major2 sections added
d49e450f2026-08-03major5 sections added; narrative text revised