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Kinetics and pH Dependence of Chromium(VI) Reduction by Iron(II)
454
Citations
24
References
1997
Year
EngineeringPh 2ChemistryChemical EngineeringEnvironmental ChemistryPh DependenceElectron Reduction PotentialInorganic ChemistryGaseous ReductionChemical FormRate LawChemisorptionSoil ContaminationWater QualityEcotoxicologyEnvironmental FateEnvironmental EngineeringEnvironmental RemediationEnvironmental ToxicologyChemical KineticsGroundwater Remediation
Iron(II) is one of the most important reductants of chromium(VI), a severe, toxic contaminant of natural waters, sediments, and soils. We studied the reaction kinetics between pH 2 and pH 7.2 with UV−VIS and multicomponent fitting, a method without the interference of added reagents. The reaction rate was minimal around pH 4. A rate increase with decreasing pH below 4 is documented in the literature. However, a pH-dependent kinetic expression for environmentally relevant, higher pH conditions has not been reported yet. For pH 4.4−7.2 (solutions buffered with acetate, MES, and PIPES, initial 10−20 μM Cr(VI) and 30−60 μM Fe(II), I = 0.01 M KCl, 23 ± 3 °C), we derived the following rate law: −d[Cr(VI)]/dt = kobs(pH)[Fe(II)][Cr(VI)], with kobs = (0.34 ± 0.47) M-1 s-1 + (3.29 ± 0.66) × 109 M-2 s-1 [OH-] + (4.82 ± 1.53) × 1016 M-3 s-1 [OH-]2 (standard deviations), where Cr(VI) to Cr(V) is the rate-determining step. The equivalent expression −d[Cr(VI)]/dt = (k1[Fe2+] + k2[FeOH+] + k3[Fe(OH)20])[Cr(VI)], with k1 = (0.34 ± 0.47) M-1 s-1, k2 = (1.41 ± 0.28) × 105 M-1 s-1, k3 = (2.84 ± 0.90) × 109 M-1 s-1, provides a plausible interpretation. The kinetic constants (log k) are related to the electron reduction potential of the corresponding aquo- and hydroxo-Fe(III)/Fe(II) redox couples, probably in a linear free enthalpy relation. Comparison to the analogous kinetic expression for Fe(II) oxygenation shows that Cr(VI) oxidizes Fe(II) faster than O2 (for [Cr(VI)] = [O2] by a factor of ≈ 3 × 104 at pH 4, 6 × 103 at pH 6, and 1 × 103 at pH 8).
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