2009•Acta Scientiae CircumstantiaeRequires access

Effect of redox processes on soil Cd activity under submerged conditions

Zhou Quansuo

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Abstract

Cadmium activity in soils may vary considerably under submerged conditions, yet the mechanisms are not well understood. In this study, a red soil (pH=4.46) and a fluvo-aquic soil (pH=7.10) were submerged and incubated under a nitrogen atmosphere at constant temperature ((25.0±0.5)℃) to study the variation of Cd activity. The pH increased to 5.92 after 60 days for the red soil and decreased to 6.62 after 3 days and then rose to 6.89 for the fluvo-aquic soil. The pe+pH for both soils decreased from 14.16 to 5.38. The variation of pH and pe+pH caused the Fe redistribution in exchangeable (Exc-), carbonate-bound (Carb-), oxide-bound (Oxide-) and organic matter-bound (Org-) fractions, and transformation of Exc-Cd to Carb-, Oxide-and Org-Cd. The negative correlations were significant or highly significant between Exc-Cd and Exc-Fe, as well as between Exc-Cd and (Carb-Cd+Oxide-Cd+Org-Cd) or (Carb-Fe+Oxide-Fe+Org-Fe), indicating that Fe redistribution controlled Cd redistribution in the soil solid phase and also affected the concentrations of Fe and Cd in soil solution. During the first 7 days following flooding in the red soil, Exc-Cd was the major fraction in the solid phase and the Cd concentration in the solution phase increased as the pe+pH decreased. From days 15 to 60 after submergence for the red soil and over the whole incubation period for the fluvo-aquic soil, Carb-Cd and Oxide-Cd were the dominant forms in the solid phase. The soluble Cd concentration declined as pe+pH decreased. Dissolved Organic Matter (DOM) did not significantly affect Cd solubility in the submerged soils.

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What this paper is about

Cadmium activity in soils may vary considerably under submerged conditions, yet the mechanisms are not well understood. In this study, a red soil (pH=4.46) and a fluvo-aquic soil (pH=7.10) were submerged and incubated under a nitrogen atmosphere at constant temperature ((25.0±0.5)℃) to study the variation of Cd activity. The pH increased to 5.92 after 60 days for the red soil and decreased to 6.62 after 3 days and then rose to 6.89 for the fluvo-aquic soil. The pe+pH for both soils decreased from 14.16 to 5.38. The variation of pH and pe+pH caused the Fe redistribution in exchangeable (Exc-), carbonate-bound (Carb-), oxide-bound (Oxide-) and organic matter-bound (Org-) fractions, and transformation of Exc-Cd to Carb-, Oxide-and Org-Cd. The negative correlations were significant or highly significant between Exc-Cd and Exc-Fe, as well as between Exc-Cd and (Carb-Cd+Oxide-Cd+Org-Cd) or (Carb-Fe+Oxide-Fe+Org-Fe), indicating that Fe redistribution controlled Cd redistribution in the soil solid phase and also affected the concentrations of Fe and Cd in soil solution. During the first 7 days following flooding in the red soil, Exc-Cd was the major fraction in the solid phase and the Cd concentration in the solution phase increased as the pe+pH decreased. From days 15 to 60 after submergence for the red soil and over the whole incubation period for the fluvo-aquic soil, Carb-Cd and Oxide-Cd were the dominant forms in the solid phase. The soluble Cd concentration declined as pe+pH decreased. Dissolved Organic Matter (DOM) did not significantly affect Cd solubility in the submerged soils.

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Available abstract

Cadmium activity in soils may vary considerably under submerged conditions, yet the mechanisms are not well understood. In this study, a red soil (pH=4.46) and a fluvo-aquic soil (pH=7.10) were submerged and incubated under a nitrogen atmosphere at constant temperature ((25.0±0.5)℃) to study the variation of Cd activity. The pH increased to 5.92 after 60 days for the red soil and decreased to 6.62 after 3 days and then rose to 6.89 for the fluvo-aquic soil. The pe+pH for both soils decreased from 14.16 to 5.38. The variation of pH and pe+pH caused the Fe redistribution in exchangeable (Exc-), carbonate-bound (Carb-), oxide-bound (Oxide-) and organic matter-bound (Org-) fractions, and transformation of Exc-Cd to Carb-, Oxide-and Org-Cd. The negative correlations were significant or highly significant between Exc-Cd and Exc-Fe, as well as between Exc-Cd and (Carb-Cd+Oxide-Cd+Org-Cd) or (Carb-Fe+Oxide-Fe+Org-Fe), indicating that Fe redistribution controlled Cd redistribution in the soil solid phase and also affected the concentrations of Fe and Cd in soil solution. During the first 7 days following flooding in the red soil, Exc-Cd was the major fraction in the solid phase and the Cd concentration in the solution phase increased as the pe+pH decreased. From days 15 to 60 after submergence for the red soil and over the whole incubation period for the fluvo-aquic soil, Carb-Cd and Oxide-Cd were the dominant forms in the solid phase. The soluble Cd concentration declined as pe+pH decreased. Dissolved Organic Matter (DOM) did not significantly affect Cd solubility in the submerged soils.

Key concepts: Chemistry, Cadmium, Soil water, Environmental chemistry, Incubation, Soil pH, Red soil, Oxide

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