Adsorption of heavy metal ions on soils and soils constituents
Abstract
The article focuses on adsorption of heavy metal ions on soils and soils constituents such as clay minerals, metal (hydr)oxides, and soil organic matter. Empirical and mechanistic model approaches for heavy metal adsorption and parameter determination in such models have been reviewed. Sorption mechanisms in soils, the influence of surface functional groups and surface complexation as well as parameters influencing adsorption are discussed. The individual adsorption behavior of Cd, Cr, Pb, Cu, Mn, Zn and Co on soils and soil constituents is reviewed.
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The complexity of metal adsorption increases with increases in the number of metals present due to competition between metals for binding sites, so different metals do not necessarily exhibit the same behavior under identical conditions.
“These findings illustrate that the complexity of metal adsorption increases with increases in the number of metals present due to competition between metals for binding sites, so different metals do not necessarily exhibit the same behavior under identical conditions (Bradl, 2004).”
From Dissolved metal adsorption capacities and fractionation in filter materials for use in stormwater bioretention facilities (2019) · cites this paper as Bradl, 2004
Cr(III) is rapidly adsorbed by soil, specifically by Fe and Mn oxides, having particularly high affinities for Fe oxides; Cr adsorption increases with increases in pH and OM content, but decreases in the presence of competing cations, including ions of the other five metals considered.
“However, Cr(III) is rapidly adsorbed by soil, specifically by Fe and Mn oxides, having particularly high affinities for Fe oxides (Bradl, 2004). Furthermore, Cr adsorption increases with increases in pH and OM content, but decreases in the presence of competing cations, including ions of the other five metals considered here (Bradl, 2004).”
From Dissolved metal adsorption capacities and fractionation in filter materials for use in stormwater bioretention facilities (2019) · cites this paper as Bradl, 2004
The availability of organic matter constituents reduces potentially toxic element mobility in soils.
“The availability of these constituents thus reduces PTE mobility in soils (Bradl, 2004).”
From Soil amendments for immobilization of potentially toxic elements in contaminated soils: A critical review (2020) · cites this paper as Bradl, 2004
Under reduced Eh soil environments, Cr(VI) can be converted to Cr(III), making it less bioavailable and thus less toxic to organisms.
“For example, under reduced Eh soil environments, Cr (VI) can be converted to Cr (III), making it less bioavailable and thus less toxic to organisms (Bradl, 2004).”
From Soil amendments for immobilization of potentially toxic elements in contaminated soils: A critical review (2020) · cites this paper as Bradl, 2004
For oxyanions such as As, solubility might increase as pH increases, mainly due to desorption of anionic potentially toxic elements with a reduction of positive charges on soil surfaces with increasing pH.
“For oxyanions such as As, solubility might increase as pH increases, which can be mainly ascribed to desorption of anionic PTEs with a reduction of positive charges on soil surfaces with increasing pH (Bradl, 2004).”
From Soil amendments for immobilization of potentially toxic elements in contaminated soils: A critical review (2020) · cites this paper as Bradl, 2004
Element hydrolysis at high soil pH levels leads to formation of metal hydroxo complexes, resulting in strong and preferential adsorption of potentially toxic elements.
“In contrast, element hydrolysis at high soil pH levels leads to formation of metal hydroxo complexes, resulting in strong and preferential adsorption of PTEs (Bradl, 2004).”
From Soil amendments for immobilization of potentially toxic elements in contaminated soils: A critical review (2020) · cites this paper as Bradl, 2004
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Biochar physicochemical properties: pyrolysis temperature and feedstock kind effects
Tomczyk, A., Sokołowska, Z., & Boguta, P. (2020) · Reviews in Environmental Science and Bio/Technology · doi:10.1007/s11157-020-09523-3 · Cited by 2,948 · see citing works
“…as on the kind of interfering ions (Bogusz et al. 2015), pH of the solution, the dosage of biochar applied (Kılıç et al. 2013; Tomczyk et al. 2019), soil type, soil pH, contact time, metal concentration and temperature (Bradl 2004; Dube et al. 2001; Srivastava et al. 2005) as well as biochar type.”
BackgroundPalansooriya, K. N., Shaheen, S. M., Chen, S. S., Tsang, D. C. W., Hashimoto, Y., Hou, D., Bolan, N. S., Rinklebe, J., & Ok, Y. S. (2020) · Environment International · doi:10.1016/j.envint.2019.105046 · Cited by 1,272 · see citing works
Role of organic amendments on enhanced bioremediation of heavy metal (loid) contaminated soils
Park, J. H., Lamb, D., Paneerselvam, P., Choppala, G., Bolan, N., & Chung, J.-W. (2011) · Journal of Hazardous Materials · doi:10.1016/j.jhazmat.2010.09.082 · Cited by 936 · see citing works
Chemical stabilization of metals and arsenic in contaminated soils using oxides–a review
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Competitive sorption and desorption of heavy metals by individual soil components
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Global profile of heavy metals and semimetals adsorption using drinking water treatment residual
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Trace element phytoextraction from contaminated soil: a case study under Mediterranean climate
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“…demonstrated to govern a large part of the contamination patterns, and by the ability of soil organic matter (and specifically humic substances) to enhance metal retention due to chemisorption, i.e. short-range interactions between metals and surface reactive groups acting as ligands (Bradl, 2004).”
BackgroundPathirana, C., Ziyath, A. M., Jinadasa, K. B. S. N., Egodawatta, P., Sarina, S., & Goonetilleke, A. (2019) · Chemosphere · doi:10.1016/j.chemosphere.2019.06.074 · Cited by 55 · see citing works
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“These findings illustrate that the complexity of metal adsorption increases with increases in the number of metals present due to competition between metals for binding sites, so different metals do not necessarily exhibit the same behavior under identical conditions (Bradl, 2004).”
BackgroundInfluentialMafakheri, N., Shamsipur, M., & Babajani, N. (2024) · Microchemical Journal · doi:10.1016/j.microc.2024.110010 · Cited by 47 · see citing works
- Authors
- Bradl, H. B.
- Affiliations
- Trier University of Applied Sciences (DE)
- Corresponding author
- Bradl, Heike B
- Venue
- Journal of Colloid and Interface Science
- Publisher
- Elsevier BV
- Published
- 2004-09
- Volume
- 277
- Issue
- 1
- Pages
- 1-18
- ISSN
- 0021-9797 (ISSN-L)
- OpenAlex
- W2013132106
- Cited by
- 2,064
- References
- 162
- Citations by year
- 2026: 128 · 2025: 130 · 2024: 101 · 2023: 111 · 2022: 127 · 2021: 153 · 2020: 120 · 2019: 126 · 2018: 141 · 2017: 130 · 2016: 119 · 2015: 115 · 2014: 110 · 2013: 89 · 2012: 71
- FWCI
- 24.47
- Type
- journal article
- Language
- en
- Open access
- closed
- Locations
- Journal of Colloid and Interface Science (publishedVersion)
- PubMed (publishedVersion)
- Topics
- Physical Sciences › Environmental Science › Pollution › Heavy metals in environment
- Physical Sciences › Environmental Science › Water Science and Technology › Adsorption and biosorption for pollutant removal
- Physical Sciences › Environmental Science › Water Science and Technology › Environmental and Analytical Chemistry Studies
- Keywords
- heavy metal adsorption, soil sorption, clay minerals, soil organic matter, surface complexation, surface functional groups, sorption mechanism, adsorption modeling, cadmium, chromium, lead, copper, manganese, zinc, cobalt
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