Skip to content
Heavy Metal Index

BIO-ACCUMULATION OF HEAVY METALS IN SOME NORTH

Source

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

Page snapshot
Cited by7 pages
Metals measured3
Evidence tierB
Year2022

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:

  • and accumulated levels of metals in leafy vegetables varied as: Pb (2.16-3.16) > Cr (1.54-2.84) > Cu
  • vegetables cultivated in the walled garden were much lower and varied as: Pb (1.11-1.46) > Cr (0.66-
  • vegetables (Agrawal et al., 2007). Usually, the et al., 2010). Prolong intake of metal contaminated
  • BIO-ACCUMULATION OF HEAVY METALS IN SOME NORTH INDIAN LEAFY VEGETABLES 981
  • al., 2010). Since, dietary consumption of vegetables Farmers of the area mostly use dug wells, hand
  • metals, to evaluate the quantum of human health irrigate the vegetable crops (Kulshrestha, 2021). For
  • Singh et al., 2010). vegetable crops are grown under ideal conditions for
  • (Perkin Elmer), using air-acetylene flame, in (Ametepey et al., 2018). Leaf vegetables generally
  • standard stock solutions of metal ions used were non-leaf vegetables (Luo et al., 2011). Thus, metal
  • of analytical grade (Kulshrestha et al., 2012). Doubly- al., 2007). The leafy vegetables have great tendency
  • are presented in Table-2. The levels of tested metals local venders, the levels of all tested metals were
  • garden are given in parenthesis. 2000; WHO, 2007). However, all the vegetables
  • Root system of the plants bio-accumulates certain vegetables (Table-2, Fig.1) was: Chaulayi (0.51±0.020)
  • Table 2. Bio-accumulated levels (mg/ Kg, dw) of Cd, Cr, Cu, Ni and Pb found in Leafy Vegetable Samples (n = 5)
  • BIO-ACCUMULATION OF HEAVY METALS IN SOME NORTH INDIAN LEAFY VEGETABLES 983
  • (0.34±0.016) >Fenugreek (0.33±0.014, mg/Kg, d.w.). Bathua: Cd (0.34±0.016) <Ni (0.38±0.015) < Cu
  • (1.54±0.030 mg/Kg, d.w.). The order of accumulated (0.68±0.023) < Cr (2.57± 0.034) < Pb (2.68±0.028); in
  • (0.46±0.016) > Fenugreek (0.39±0.014 mg/Kg, d. w.). (0.61±0.018) < Cr (2.52±0.028) < (2.61±0.028) and in
  • vegetables was: Rayi (0.79±0.026) > Chaulayi (0.43±0.014), Cr (1.54±0.030) < Pb (2.26±0.024).
  • (0.43±0.014) > Bathua (0.38±0.015 mg/Kg, d.w.). The grown on North Indian soil e.g. Cd and Cu in
  • order of Lead in vegetables was: Rayi (3.16±0.040) > Spinach and Radish leaves (Singh et al., 2010); Cu and
  • accumulation in studied leafy vegetables (Table 2). the reported results of Cd in Spanich (Tamrakar and
  • The overall range of studied metals in vegetables Richhariya, 2012); Cd, Cu, Ni and Pb in Spinach
  • area of vegetables (Chang et al., 2014) as first three as: Cd from 0.19 to 0.29, Cr from 0.66 to 1.22, Cu
  • vegetables (Rayi, Chaulayi and Spinach) have broad from 0.21 to 0.42, Ni from 0.22 to 0.33 and Pb varied
  • observed levels of studied metals in Spinach (Table 2, results are comparable with earlier results (Kumar et
  • Fig.1) was: Cd (0.47±0.018) < Ni (0.58±0.016) < Cu al., 2017) reported in leafy vegetables from ground
  • minimum vegetable requirement of 100 g vegetables
  • computed values of DIM are presented in Table 3.
  • vegetable species (Kumar et al., 2017). Among all
  • The human health risk in terms of health risk tested metals (Table 3) was recorded in Rayi and
  • metal contaminated vegetables under study and oral (2.1040) > Bathua (2.0905). The daily intake of metals
  • reference dose (Cui et al., 2004, US –EPA Tech. due to Cadmium in studied leafy vegetables varied
  • concentration (mg/Kg, dw) in edible parts of Chromium was 0.001, 0.004, 0.04 and 1.5 mg/kg/
  • used for conversion of fresh weight of vegetable to 2006) and the RfD for Nickel was 0.02 mg/Kg/day
  • Table 3. Daily intake of metals (DIM, mg/Kg/day/person) through consumption of studied leafy vegetables collected
  • BIO-ACCUMULATION OF HEAVY METALS IN SOME NORTH INDIAN LEAFY VEGETABLES 985
  • from Table -3 and R fD (US –EPA, 1997; 2010) in Fenugreek; Copper was: Rayi > Chauleyi > Spinach ~
  • vegetables (Mahmood and Malik, 2014). Individual Fenugreek >Bathua. Table 4 reveals the potential
  • vegetables (Ametepey et al., 2018). The computed contaminated with Cd, Cr, Cu, Ni and Pb.
  • consumption (USEPA IRIS., 2006), while the health risk index (HRI) due to dietary intake of vegetables
  • (Table 4, Fig. 3) was: Pb (229.5 - 335.8) > Cd (140.2 to (0.33) >Cd (0.22) >Pb (0.17) >Cu (0.17) (Mahmood

Methods (brief)

  • fenugreek (Trigonella foenum-graecum) collected from local venders were evaluated. The daily
  • index (HRI) due to tested metals on dietary intake of studied vegetables collected from local
  • vegetables may lead to the deposition of heavy The samples of selected leafy vegetables were
  • metals in the human tissues and sensitive internal collected during July 2015 to March 2016 from five
  • risk through dietary intake of vegetables, has gained comparison purpose, samples of leafy vegetables
  • importance (Tripathi et al., 1997; Zhuang et al., 2009; were also collected from a walled garden where
  • most consumed in North India, in terms of young, soft and fresh samples of spinach, bathua,
  • dietary intake of metals (DIM) (Chary et al., 2008). were collected much before the flowering stage.
  • 1989, 1993; Rattan et al., 2005) by estimating the samples were cleaned 2-3 times with tap water and
  • studied vegetables collected from local venders. For mud and soil particles. The cleaned samples were
  • bio-accumulated metals in the studied vegetables. In make samples moisture free. The air dried samples
  • conditions, without using chemical fertilizers, waste days at 800C to a constant weight. The dried samples
  • water and street runoff. The description and dietary were grinded to powder and kept in labeled sample
  • Sample Collection grinded samples (1.0 g) were subjected to HNO3 –
  • HClO4 (5:1, v/v) digestion at nearly 800C for several system near the plant roots, characteristics of farm
  • and Pb in vegetable samples were determined on in the kidney and liver of human beings leading to
  • Atomic Absorption Spectrometer, Analyst 200 cardiovascular, bone, kidney and CNS diseases
  • collected from local market, namely Spinach, Bathua, soil and rainwater (Chang et al., 2014).

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