Abstract:The kinetics of reduction and oxidation of soluble chromium in various soils (peat, clay, sand, and luvi-chromic cambisols) were studied at constant soil moisture and constant temperature. A total of 1500 g of each soil was incubated with different concentrations of aqueous solutions of K 2 Cr 2 O 7 or CrCl 3 [1-1000 µg (g of dry soil) -1 ]. The total exchangeable chromium and Cr(VI) were analyzed in soil extracts over a period of up to 10 days. The parameters influencing the reduction and oxidation of soluble… Show more
“…Esse processo de redução é ainda mais acentuado quando se tem solos com pH ácido. [21][22][23] Para elucidar os resultados obtidos e considerando-se um possível processo redox entre Cr(VI) e matéria orgânica, determinaram-se os teores de matéria orgânica nas amostras de solo contaminadas (Tabela 3).…”
Section: Resultados E Discussão Estabilidade Do íOn Cr(vi)unclassified
Recebido em 3/10/07; aceito em 15/2/08; publicado na web em 13/8/08 CHROMIUM REDOX SPECIATION IN SOIL ACCIDENTALLY CONTAMINATED WITH SULPHOCHROMIC SOLUTION. Determination of Cr(VI) and Cr(III) was studied in soil samples accidentally contaminated with sulphochromic solution. Molecular absorption spectrophotometry based on the diphenylcarbazide method was used for the determination of Cr(VI) after its alkaline extraction. The total chromium concentration was determined using ICP OES. The quantification of Cr(III) was accomplished by subtracting the Cr(VI) concentration from the total chromium concentration. Regardless of the known contamination of the soil samples by sulphochromic solution, concentrations of Cr(VI) were below the detection limit. Addition and recovery experiments for Cr(VI) in soil samples with and without organic matter indicated its influence on the reduction of Cr(VI) to Cr(III).
“…Esse processo de redução é ainda mais acentuado quando se tem solos com pH ácido. [21][22][23] Para elucidar os resultados obtidos e considerando-se um possível processo redox entre Cr(VI) e matéria orgânica, determinaram-se os teores de matéria orgânica nas amostras de solo contaminadas (Tabela 3).…”
Section: Resultados E Discussão Estabilidade Do íOn Cr(vi)unclassified
Recebido em 3/10/07; aceito em 15/2/08; publicado na web em 13/8/08 CHROMIUM REDOX SPECIATION IN SOIL ACCIDENTALLY CONTAMINATED WITH SULPHOCHROMIC SOLUTION. Determination of Cr(VI) and Cr(III) was studied in soil samples accidentally contaminated with sulphochromic solution. Molecular absorption spectrophotometry based on the diphenylcarbazide method was used for the determination of Cr(VI) after its alkaline extraction. The total chromium concentration was determined using ICP OES. The quantification of Cr(III) was accomplished by subtracting the Cr(VI) concentration from the total chromium concentration. Regardless of the known contamination of the soil samples by sulphochromic solution, concentrations of Cr(VI) were below the detection limit. Addition and recovery experiments for Cr(VI) in soil samples with and without organic matter indicated its influence on the reduction of Cr(VI) to Cr(III).
“…(Rauret et al, 1999;Bacon and Davidson, 2008) Step Fraction Extraction solution Table 2). 그러나, Fe(II)로 환원이 완료되어 (Kozuh et al, 2000;Kumpiene et al, 2008;Landrot et al, 2010). 토양시 료를 대상으로 XANES의 분석을 실시하여 토양 중 Mn(IV)이 존재함을 확인하였다 (Fig.…”
In this study, a remedial investigation using reductive stabilization was conducted to treat Cr(VI)-contaminated soil. The influences of various operational parameters, including reaction time and the mass of ferrous iron, were also evaluated. The study site was contaminated with a large amount of Cr(III) and Cr(VI), and the selected treatment method was to stabilize Cr(VI) with ferrous iron, which reduced Cr(VI) to Cr(III) and stabilized the chromium, although a greater mass of ferrous iron than the stoichiometric amount was required to stabilize the Cr(VI). However, some Cr(III) re-oxidized to Cr(VI) during the drying process, and addition of a strong reducing agent was required to maintain reducing conditions. With this reducing agent, the treated soil met the required regulatory standard, and the mass of Cr(III) re-oxidized to Cr(VI) was significantly reduced, compared to the use of only Fe(II) as a reducing agent.
“…Compared with 16% for the control, bioaccessible Cr decreased to 13% for 1:0.5 Mn and P; 12% for 1:2 Mn and P; and 13% for 1:5 Mn and P. After 30 days, the bioaccessible fraction increased slightly and was no longer significantly different than the control at p<5%, but was different at p<10%. Manganese can rapidly oxidize Cr(III) to Cr(VI) (Kozuh et al, 2000). This was a concern in this project, since there was a slight increase in the bioaccessible fraction of Cr with the addition of Mn.…”
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