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Heavy Metal Index

The Case for Visual Analytics of Arsenic Concentrations in

Source

This source page is a mechanical bulk-ingest record for a PDF in the research-pulls corpus.

Page snapshot
Cited by5 pages
Metals measured2
Evidence tierB
Year2010

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:

  • humans of water soluble inorganic arsenic are presented in Table 1. It is now well recognized that
  • Table 1. Selected toxicity features of water soluble inorganic arsenic compounds a.
  • Excretion Urine at rates as high as 80%
  • (pH around 6.5, free calcium carbonate absent) was 4.85 to 12.20 mg/kg while that of calcareous soil
  • (pH around 7.6, free calcium carbonate present) was 11.60 to 24.40 mg/kg (22). Furthermore, in soil
  • from 40 to 60 mg/kg (22). In a investigation of rice grain samples from 214 households in 25 arsenic-
  • endemic Bangladeshi villages, the Rahman et al. (23) found that total arsenic content ranged from
  • 2 µg/kg to 557 µg/kg dry weight (dw). The arsenic concentrations in control samples obtained from
  • South Australia ranged from 3 µg/kg to 87 µg/kg dw, significantly lower (p < 0.001) than those
  • 5 to 540 µg/kg, with a mean of 54.5 µg/kg. Furthermore, the concentration of total arsenic in
  • freshwater fish ranged between 97 and 1318 µg/kg, with a mean value of 350 µg/kg. In the case of
  • freshwater fish, Puti (Puntius gonionotus) had a very high arsenic concentration of 1,318 µg/kg with a
  • mean of 580 µg/kg in its dried forms. The total arsenic concentrations of some selected vegetables
  • Union (EU) showed the mean and range of arsenic concentrations to be 24.2 and 5 to 87 µg/kg
  • vegetables (92 and 123 µg/kg), cereals and baked goods (156 and 294 µg/kg) and spices (92 and
  • 201 µg/kg) (mean arsenic concentrations for Jalangi and Domkal blocks respectively).
  • over 1.3 ppm regulatory limit by the United States Environmental Protection Agency (EPA).
  • larger questions. The focus areas of visual analytics are summarized in Table 2. The perception is that
  • Table 2. Visual Analytics Focus Area Techniques a.
  • Zealand Total Diet Survey (NZTDS) (55). The tabulated data in Table 3 was processed using
  • Tableau (34), a visual analytics software, to visualize groupings of foods according to total arsenic
  • Table 3. Total arsenic content (mg/kg) of selected foods from a study in New Zealand a.
  • Figure 2. Screenshot of visual analytics interface for grouping arsenic content (mg/kg) of
  • The process included connecting the spreadsheet file containing Table 3 into Tableau and
  • Figure 3. Screenshot of visual analytics of arsenic content (mg/kg) of food from a study in
    1. Smith, E.; Juhasz, A.L.; Weber, J. Arsenic Uptake and Speciation in Vegetables Grown Under
  • Metals by Vegetables Grown in Mine Wastes. Environ. Toxicol. Chem. 2000, 19, 600-607.

Methods (brief)

  • second methylation to generate dimethylarinic acid (DMAv). Inorganic arsenic and its methylated
  • samples around arsenic-enriched Singair areas of Bangledesh, the inorganic arsenic content ranged
  • from 40 to 60 mg/kg (22). In a investigation of rice grain samples from 214 households in 25 arsenic-
  • 2 µg/kg to 557 µg/kg dry weight (dw). The arsenic concentrations in control samples obtained from
  • collected in the contaminated areas.
  • Roychowdhurg et al. (24) surveyed total arsenic content in food collected in Jalangi and Domkal

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.

Wiki pages this source may touch

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.
  • Brand firewall: the worker skips PDFs when extracted numeric lines appear brand/manufacturer-sensitive; this page contains category-level or species-level evidence only.
  • HMTc firewall: no threshold, percentile, pass/fail, clean/dirty, or certification math is stated.

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