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Effect of Flooding on the Eh, pH, and Concentrations of Fe and Mn in Several Manitoba Soils
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1973
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Redox SystemOrganic GeochemistryEnvironmental ChemistryBiogeochemistrySeveral Manitoba SoilsEngineeringSoil PropertyEnvironmental EngineeringSoil ChemistryEnvironmental RemediationSoil ContaminationSoil MineralogyMn 2HydrologySoil Solution
Abstract The changes in Eh, pH, and concentrations of Fe and Mn in the solutions extracted from six Manitoba soils saturated with water were studied at various times of incubation at room temperature. Gradual reduction of the extracts was observed during the first 3 to 4 weeks of incubation. After this period, the extracts, in many instances, gradually returned to relatively oxidized states with occasional reduction. Somes changes in pH were observed but the magnitude of change was relatively small in soils with a relatively high cation exchange capacity. Both Fe and Mn concentrations generally increased with increased reduction. This trend was more pronounced for Mn than for Fe. E 0 values calculated from experimentally measured Eh, pH, and concentrations of Mn appeared to indicate the presence of the Mn 2 O 3 − Mn 2+ redox system. The calculated values of E 0 based on the assumption that the Fe 2 O 3 − Fe 2+ redox system was operative were far greater than the theoretical value. Almost all the Fe in soil solution was complexed with organic matter whereas Mn was either not complexed or only weakly complexed. The metal‐organic matter complexes were negatively charged. The soil solutions had a greater affinity for Fe than did 10 ‐4 M EDTA. It is suggested that the very high degree of complexing of Fe in soil solution was most probably responsible for failure to obtain the theoretical E 0 values for the Fe 2 O 3 — Fe 2+ redox system from the experimental data.