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Heavy Metal Index

under multi-metal exposure

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
Year2026

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:

  • 2021)-are cost-effective, highly reactive, and suitable for large-scale et al., 2022b). The detailed process of plant extract preparation and
  • 65 ± 5%. After 45 days of sowing, various morphological and performed, cytoskeleton-associated processes were indirectly in-
  • phyll concentration. (0.5 g) was homogenized in 3 mL of 5% (v/v) sulfosalicylic acid and
  • with 2% ninhydrin. The reaction mixture was incubated at 95 °C for
  • lipid peroxidation (MDA) content by (Khan et al., 2020), and it represented the ADI of vegetables
  • fresh leaf sample (0.5 g) was homogenized in 5 mL of 0.1% Cmeatal  IRintake  Cft
  • at 6952 × g for 20 minutes in 10% potassium phosphate buffer. The
  • a fresh leaf sample was homogenized in 10 mL 0.1% TCA. by an individual; Cmetal: The concentration of heavy metal in
  • 14000 × g. After mixing with 0.5% thiobarbituric acid (TBA) and 6 The rate at which vegetables are consumed by an individual; Cft
  • mL of 20% TCA, the supernatant (1.5 mL) was heated to 95 °C for (Conversion Factor): The factor used to convert fresh vegetable
  • (2020). Supplementary Table 1 contains a complete listing of the ized (Z-score transformation). Pearson’s r values were computed
  • sample was filtered and adjusted to a volume of 50 ml using logical replicates (n = 3), with each replicate represented by one pot
  • Thermo Scientific UK; (Sharma et al., 2022)). For the determination cate where applicable, and mean values were used for
  • structures (Zhang et al., 2012). This aggregation behavior is likely primary level is within the nanoscale range, while secondary
  • rearrangement (Patil et al., 2023). The contrasting morphologies Moreover, the applied amendments significantly enhanced soil
  • aggregation, resulting in porous clusters, whereas ZnONPs exhibit (N), phosphorus (P), and potassium (K) increased by 24.80%,
  • for functional performance (Noimark et al., 2015). For instance, the (Mg) levels were elevated by 44.65% and 35.67%, respectively. These
  • et al., 2015). Accordingly, the use of soil passivators that stabilize the FPS+ZnONPs treatment (58.42%, 35.04%, and 42.73% for Cr, Cu,
  • respectively. Moreover, there was a significant increase of 59.29%,
  • witnessed increments of 65.69%, 145.66%, and 185.69% in the
  • sediments applied at a rate of 35% (w/w); FPS+SiNPs = fishpond incorporation of FPS, FPS+SiNPs, and FPS+ZnONPs significantly
  • increased chlorophyll a by 34.36%, 44.08%, and 67.35%, chlorophyll
  • synthesized zinc oxide nanoparticles. Values represent mean ± b by 21.29%, 45.04%, and 71.27%, carotenoids by 38.05%, 88.02%,
  • standard deviation (SD) of three biological replicates (n = 3). Bars and 272.53%, and SPAD index by 9.40%, 15.31%, and 38.86%,
  • metabolism FPS amendments. As shown in Table 1, soils contaminated with Cr,
  • tion, inhibit seedling development, and ultimately reduce plant reductions, leading to increases in Pn by 28.21%, 35.20%, and
  • biomass and yield (Stambulska et al., 2018). However, the applica- 37.07%; E by 32.88%, 40.89%, and 52.73%; Ci by 1.19%, 2.08%,
  • tion of FPS, FPS+SiNPs, and FPS+ZnONPs caused substantial and 3.27%; and Gs by 107.08%, 182.03%, and 272.53%, respectively.
  • increase in plant length, with improvements of 32.28%, 33.81%, Notably, the application of FPS+ZnONPs demonstrated the highest
  • and 56.44% in shoots and 108.11%, 100.40%, and 113.03% in roots, effectiveness in significantly enhancing leaf Pn, E, Ci, and Gs. This
  • (n = 3). Bars with different letters indicate significant differences among treatments at p < 0.05 according to one-way ANOVA followed by Tukey’s
  • 145.54%, POD by 120.34%, CAT by 225.62%, and APX by FPS+SiNPs, and FPS+ZnONPs effectively increased protein and
  • (SoSOD, SoPOD, SoCAT, and SoAPX) are key components of +ZnONPs treatment, which resulted in a 190.53% rise in total
  • those in amended soils (Supplementary Table 2), indicating that 2020; Li et al., 2025). The extent of the increase, however, varies
  • +ZnONPs led to a decrease in proline levels by 40.69%, 66.60%, and FPS, FPS + SiNPs, and FPS + ZnONPs significantly lowered H2O2
  • 77.59%, respectively than control. Moreover, it was noted that FPS by 36.12%, 60.79%, and 68.80%, and reduced MDA by 39.56%,
  • +ZnONPs was most efficient treatment for reducing the levels of 40.11%, and 69.31%, respectively, relative to the unamended control
  • nanoparticles. Values represent mean ± standard deviation (SD) of three biological replicates (n = 3). Bars with different letters indicate significant
  • standard deviation (SD) of three biological replicates (n = 3). Bars with different letters indicate significant differences among treatments at p < 0.05
  • tion in the shoots by 39.63%, 47.47%, and 59.32%, respectively, and transporters, facilitating vesicular trafficking, and maintaining cel-
  • in the roots by 24.92%, 38.35%, and 60.53%, respectively. lular polarity, all of which are associated with regulated ion uptake
  • (n = 3). Bars with different letters indicate significant differences among treatments at p < 0.05 according to one-way ANOVA followed by Tukey’s

Methods (brief)

  • have demonstrated the agronomic potential of remediated FPS for cm. The fishpond sediments (FPS) were collected from Hainan,
  • analyses, plants from each replicate pot were sampled and analyzed framework
  • weight) of leaf was crushed and grounded under liquid nitrogen, treated samples was assessed using the nitro blue tetrazolium (NBT)
  • fresh leaf sample (0.5 g) was homogenized in 5 mL of 0.1% Cmeatal  IRintake  Cft
  • a fresh leaf sample was homogenized in 10 mL 0.1% TCA. by an individual; Cmetal: The concentration of heavy metal in
  • and shoots, plant samples underwent a washing process with glassware was rinsed at least three times with ultrapure water, oven-
  • soil. Dry plant material samples from each treatment were subjected personnel wore cotton coats and nitrile gloves, and all unused
  • to digestion in a triacid mixture (HNO3, H2SO4, and HClO4) at 80 ° instruments were properly covered to maintain a clean working
  • sample was filtered and adjusted to a volume of 50 ml using logical replicates (n = 3), with each replicate represented by one pot
  • using an Atomic Absorption Spectrometer (AAS; iCE 3000 series, metric analyses, technical measurements were performed in tripli-

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