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Heavy Metal Index

Ecological and Human Health Risk Assessment of Heavy Metal in Sediment and

Source

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

Page snapshot
Cited by8 pages
Metals measured5
Evidence tierB
Year2023

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:

  • species were below the regulation range of 1.0 × 10−6 to 1.0 × 10−4 set by the USEPA. The cluster analysis revealed two clusters. Cluster
  • Table 1. Sediment Quality Guidelines (SQG) of Heavy Metals and Metalloid (Unit: mg/kg)
  • deionized water. The solution was filtered through Whatman with 21% probability of being toxic, mPEL Q = 1.51 ~ 2.3 in-
  • were performed for initial and periodic verification of calibra- contamination with 73% probability of being toxic respectively
  • terized compared the effects range low (ERL), effects range me- guideline of threshold effects level (Long et al., 2006; Paul et al.,
  • (MET) (Table 1). Equation (2) shows the formulae used to calcu- < 10 indicates moderate hazards; HQ > 10 indicates high hazards
  • late the mean PEL quotient: (Feng et al., 2011; Benson et al., 2018).
  • The newly mHQ was computed to ascertain the degree of ate severity; 1.0 < mHQ < 1.5 means low severity, and 0.5 < mHQ
  • 3.5 means extreme severity; 3.0 < mHQ < 3.5 indicates very high (7) of USEPA Region III Risk-Based Concentration (USEPA,
  • severity; 2.5 < mHQ < 3.0 means high severity; 2.0 < mHQ < 2.5 2011) which estimates non-carcinogenic health risk associated
  • (Mc  FIR  10−3  EF  ED) 3). The mean PCI for As (0.01), Hg (0.10), and Pb (0.06) were
  • slope, oral (mg/kg bw-1 day-1) for Pb, and Cd are 0.009 and 0.6
  • ing SPSS v.25 and PAST 4.10 (Hammer et al., 2001). ArcGIS 3.3. Ecotoxicological Assessment and Mean Effect Level
  • heavy metals/metalloid in sediment. Levels of Cd were higher than TEL by 100%, As by 3%,
  • Hg by 24%, and Pb in 3.6% in sediment across all stations. For
    1. Results and Discussion PEL, As was higher by 1.04%, Hg by 8.4%, Cd by 18.2%, and
  • Pb by 1.4% in sediment. The estimated mean probable effects
  • The heavy metals concentrations geospatial distribution as presented in Figure 4. Generally, the mean probable effects
  • (green) and Hg (white) showed significant increase in concentra- 0.1) notably with 8% minimal probability of being toxic, except
  • significant increase in concentrations at station 3. Generally, tion (0.11 ~ 1.5) with 21% probability of being toxic which cor-
  • Figure 5. Mean variations of heavy metals/metalloids in muscle of fish species. Note: (*) indicates significant differences (p <
  • priority indicating low degree of contamination across all sta- Hg values ranged from 0.021 to 0.74, Cd values ranged from
  • tions with 9% probability of being toxic in the sediment 0.66 to 1.51, Pb values ranged from 0.02 to 0.05 (Table 2). As
  • Quotient for Sediment As, Hg, and Pb was generally below 0.5, while Cd ranged from
  • The estimated HQ of As values ranged from 0.002 to 0.067, 0.56 to 1.30 across all stations off western Nigeria coast (Table
  • Table 3. Estimated THQ, HI And TCR of Metals in Demersal Fish Species
  • and 4 respectively fell within the range of 1 < HQ < 10 which once it is, it is slowly eliminated, much like other metals, and
  • of contamination, while Cd ranged between 0.5 and 1.0 which
  • The EDI values for As ranged from 0.19 × 10 -9 (Rhizopri-
  • onodon acutus) to 8 × 10-9 (Sardinella maderensis), Hg ranged
  • maderensis), Cd ranged from 0.12 × 10-9 (Pagellus ehrenbergi)
  • to 1.45 × 10 -8 (Galeoides decadactylus) and Pb ranged from
  • The heavy metal levels in the muscle tissues of demersal loid in demersal marine fish species are shown in Table 3. The
  • marine fish species are presented in Figure 5. Mean levels of THQ values in demersal marine fish species from the western
  • As, Hg, Cd, and Pb in muscles of the demersal fish species fell off Nigeria coast ranged from 0.01 × 10-5 to 8.99 × 10-5. The
  • Clarias anguillaris, had As ranged from 0.05 ± 0.01 ~ 0.15 ± cation to consumers over a period time. These findings also cor-
  • Studies in Marine Science, 18, 44-56. https://doi.org/10.1016/j.rsm and uses of mean sediment quality guideline quotients: A critical re-
  • Santos, J.L., Malvar, J.L., Martín, J., Aparicio, I. and Alonso, E. (2020). Table: November (2011). http://www.epa.gov/regshwmd/risk/hum

Methods (brief)

  • with fish consumption from western Nigeria offshore in the Gulf of Guinea. Triplicate samples of demersal marine fish species and
  • sediments were collected from five stations (fishing ground) and analysed for heavy metals (mercury (Hg), cadmium (Cd), and lead (Pb))
  • and metalloid (arsenic (As)) using ICP-OES (inductively coupled plasma optical emission spectrometry) adopted USEPA 200.7 standard
  • grounds of the Western Offshore Nigeria, Gulf of Guinea. 2.2. Sample Collection
  • and 04°35′ E, and latitudes of 06°00′ and 06°15′ N, which is and surface sediments were collected. Demersal fishes were
  • fish stock assessments were carried out on five sampling hotspots was collected using 0.1 m2 van Veen grab sediment sampler. Trip-
  • (fishing grounds) along western offshore Nigeria, Gulf of Guinea licates of each fish species were collected in Ziploc bags, and
  • the Delta flank consists of three main subsurface lithostrati- Sample (surface sediments and fish muscle) preparation
  • and analyses of As, Hg, Cd, and Pb in samples were performed
  • with USEPA. 200.7 standard method using ICP-OE spectrom- mPELQ = i =1
  • cle size < 2 mm) of sediment and fish muscle samples, were tion, and PEL is probable effect level value of the individual
  • placed into a digestion vessel. Then 2 mL (1:1) HNO3 and 5 mL metal (Darwish et al., 2021).The mPELQ is categorized (Paches
  • in Cd, Pb, and As of the fish species across sampled stations 0.43 × 10-5 which fell within the recommended threshold dose
  • sessment of heavy metals in fish species collected from catchments Palaeontologia Electronica, 4(1), 1-9. https://palaeoelectronica.org

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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