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Solid−Solution Speciation and Phytoavailability of Copper and Zinc in Soils
Abstract
The soil solution speciation and solid-phase fractionation of copper (Cu) and zinc (Zn) in 11 typical uncontaminated soils of South Australia were assessed in relation to heavy metal phytoavailability. The soils were analyzed for pH (4.9-8.4), soil organic matter content (3.5 to 23.8 g of C kg(-1)), total soil solution metal concentrations, Cu8 (49-358 microg kg(-1)) and Zn8 (121-582 microg kg(-1)), and dissolved organic matter (DOM) (69-827 mg of C L(-1)). The solid-liquid partition coefficient (Kd) ranged from between 13.9 and 152.4 L kg(-1) for Cu and 22.6 to 266.3 L kg(-1) for Zn. The phytoavailability of Cu and Zn could be predicted significantly using an empirical model with the solid-phase fractions of Cu and Zn, as obtained from selective sequential extraction scheme, as components. Phytoavailable Cu and Zn were found to significantly correlate with fulvic complex Cu (r= 0.944, P < 0.0001) and exchangeable Zn (r = 0.832, P = 0.002), respectively. The fulvic complex Cu was found to explain 89.2% of the variation in phytoavailable Cu, where as, the exchangeable Zn together with fulvic complex Zn could explain 78.9% of the variation in phytoavailable Zn. The data presented demonstrate the role of solid-phase metal fractions in understanding the heavy metal phytoavailability. The assessment of the role of solid-phase fractions in heavy metal phytoavailability is a neglected area of study and deserves close attention.
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Inclusion of solution element concentration in the regression analysis did not improve the predictability of phytoavailable element.
“Inclusion of solution element concentration in the regression analysis was not found to improve the predictability of phytoavailable element.”
From MOBILITY AND BIOAVAILABILITY OF HEAVY METALS AND METALLOIDS IN SOIL ENVIRONMENTS (2010) · cites this paper as Krishnamurti and Naidu, 2002
The metal-fulvate complex-bound element together with exchangeable element could explain 92% of variation in phytoavailable Cd.
“79% and 92% of variation in phytoavailable Zn and Cd, respectively.”
From MOBILITY AND BIOAVAILABILITY OF HEAVY METALS AND METALLOIDS IN SOIL ENVIRONMENTS (2010) · cites this paper as Krishnamurti and Naidu, 2002
Fulvic complex Cu could explain 89% of variation in phytoavailable Cu.
“fulvic complex Cu could explain 89% of variation in phytoavailable Cu”
From MOBILITY AND BIOAVAILABILITY OF HEAVY METALS AND METALLOIDS IN SOIL ENVIRONMENTS (2010) · cites this paper as Krishnamurti and Naidu, 2002
Phytoavailable Zn was significantly correlated with exchangeable Zn (r=0.832, p=0.002).
“exchangeable Zn (r=0.832, p=0.002)”
From MOBILITY AND BIOAVAILABILITY OF HEAVY METALS AND METALLOIDS IN SOIL ENVIRONMENTS (2010) · cites this paper as Krishnamurti and Naidu, 2002
Phytoavailable Cd was significantly correlated with the metal-fulvate complex-bound Cd (r = 0.824, p=0.002).
“the metal-fulvate complex-bound Cd (r = 0.824, p=0.002).”
From MOBILITY AND BIOAVAILABILITY OF HEAVY METALS AND METALLOIDS IN SOIL ENVIRONMENTS (2010) · cites this paper as Krishnamurti and Naidu, 2002
Mobility and bioavailability, and hence potential toxicity of metal in soil depend on its concentration in soil solution, the nature of its association with other soluble species, and soil ability to release the metal from the solid phase to replenish that removed from soil solution by plants.
“The mobility and bioavailability, and hence potential toxicity of metal in the soil depend on its concentration in soil solution, the nature of its association with other soluble species, and soil ability to release the metal from the solid phase to replenish that removed from soil solution by the plants (Krishnamurti and Naidu, 2002; Huang and Gobran, 2005; Krishnam”
From MOBILITY AND BIOAVAILABILITY OF HEAVY METALS AND METALLOIDS IN SOIL ENVIRONMENTS (2010) · cites this paper as Krishnamurti and Naidu, 2002
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“…on its concentration in soil solution, the nature of its association with other soluble species, and soil ability to release the metal from the solid phase to replenish that removed from soil solution by the plants (Krishnamurti and Naidu, 2002; Huang and Gobran, 2005; Krishnamurti et al., 2007).”
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Metadata
- Authors
- Krishnamurti, G. S. R., & Naidu, R.
- Affiliations
- CSIRO Land and Water (AU)
- Commonwealth Scientific and Industrial Research Organisation (AU)
- Corresponding author
- Naidu, Ravendra
- Venue
- Environmental Science & Technology
- Publisher
- American Chemical Society (ACS)
- Published
- 2002-05-10
- Volume
- 36
- Issue
- 12
- Pages
- 2645-2651
- ISSN
- 0013-936X (ISSN-L)
- 1520-5851
- OpenAlex
- W2064100597
- Cited by
- 134
- References
- 30
- Citations by year
- 2025: 1 · 2024: 2 · 2023: 3 · 2022: 4 · 2021: 2 · 2020: 4 · 2019: 4 · 2018: 5 · 2017: 8 · 2016: 3 · 2015: 7 · 2014: 6 · 2013: 5 · 2012: 11
- FWCI
- 5.18
- Type
- journal article
- Language
- en
- Open access
- closed
- Locations
- Environmental Science & Technology (publishedVersion)
- PubMed (publishedVersion)
- Adelaide Research & Scholarship (AR&S) (University of Adelaide) (submittedVersion)
- Topics
- Physical Sciences › Environmental Science › Pollution › Heavy metals in environment
- Life Sciences › Agricultural and Biological Sciences › Plant Science › Plant Micronutrient Interactions and Effects
- Physical Sciences › Environmental Science › Water Science and Technology › Environmental and Analytical Chemistry Studies
- Keywords
- copper, zinc, exchangeable zinc, solid-liquid partition coefficient, selective sequential extraction, dissolved organic matter, South Australia
- MeSH terms
- Benzopyrans, Biological Availability, Carbon, Copper, Forecasting, Hydrogen-Ion Concentration, Plants, Soil Pollutants, Solubility, Zinc
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