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首页> 外文期刊>Hydrometallurgy >Kinetics of iron(III)-catalyzed oxidation of arsenic(III) in acidic solutions with SO2/O-2 gas mixture using different iron sources
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Kinetics of iron(III)-catalyzed oxidation of arsenic(III) in acidic solutions with SO2/O-2 gas mixture using different iron sources

机译:铁(III)的动力学 - 使用不同的铁源的SO2 / O-2气体混合物催化砷(III)氧化砷(III)氧化溶液

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Oxidation of arsenic(III) to arsenic(V) is very important in arsenic removal and immobilization operations. Limited studies on arsenic(III) oxidation at pH below 1.5 as is the case of acid plant and leaching process effluents have been reported. In this work, the kinetics of As(III) oxidation with SO2/O-2 gas mixture at low pH (0.3-1.0) sulfuric acid solutions was investigated in the presence of different iron sources as catalyst: (i) Fe(III); (ii) Fe(II); and (iii) FeOOH residue. In the absence of Fe(III) the initial rate of As(III) oxidation at 90 degrees C is 0.6 mmol/L.min increasing to 1.1 mmol/L.min with Fe(III)/As(III) molar ratio = 0.1. Higher additions of Fe(III) bring only modest increase in rate. In the presence of Fe(II) the oxidation of As(III) is delayed initially due to competing oxidation of Fe(II) subsequently accelerating with the build-up of Fe(III), which acts as catalyst. Use of FeOOH (industrial goethite residue) provides a cost-effective source of Fe(III) catalytic species while simultaneously acts as neutralizing agent. A complex kinetic behavior is followed. Oxidation is reaction-controlled over the temperature range 25-50 degrees C shifting to mixed regime control from 70 to 80 degrees C becoming finally fully mass-transfer controlled at 90 degrees C. The catalytic role of Fe(III) is rationalized on the basis of a radical chain mechanism.
机译:砷(III)对砷(Ⅴ)的氧化在砷除去和固定操作中非常重要。对砷(III)氧化在低于1.5以下的砷(III)氧化的有限研究与酸性植物的情况和浸出工艺发出的情况。在这项工作中,在不同的铁源作为催化剂的存在下,研究了用SO2 / O-2气体混合物在低pH(0.3-1.0)硫酸溶液中进行氧化的动力学:(i)Fe(iii) ; (ii)Fe(ii); (iii)FeOOH残留物。在没有Fe(iii)的情况下,90℃下氧化的初始速率为0.6mmol / l.min增加到1.1mmol / l.min,用Fe(iii)/ As(iii)摩尔比= 0.1 。较高的Fe(iii)的增加速度增加了速度。在Fe(ii)的存在下,由于Fe(II)的竞争氧化,随后与催化剂充当Fe(III)的竞争,最初是由于Fe(II)的竞争氧化而延迟。使用FeOOH(工业碎石残留)提供了Fe(III)催化物质的经济有效源,同时充当中和剂。遵循复杂的动力学行为。氧化在25-50℃的温度范围内反应控制,从70至80℃的混合调节控制变得最终完全传质在90摄氏度下控制。Fe(III)的催化作用是基于合理的激进的链条机制。

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