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Kinetics of adsorption and redox processes on iron and manganese oxides: reactions of As(III) and Se(IV) at goethite and birnessite surfaces

机译:铁和锰氧化物上吸附和氧化还原过程的动力学:针铁矿和水钠锰矿表面上As(III)和Se(IV)的反应

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摘要

Selenium and arsenic are naturally-occurring, non-metallic elements with complex chemical and biological behavior in aquatic environments. In this study, rates and mechanisms of adsorption, desorption, and electron transfer reactions involving selenium and arsenic oxyanions and two naturally occurring metal oxides, goethite (α-FeOOH) and birnessite (δ-MnO_2), have been investigated. Adsorption of Se(IV), As (III) , and As(V) on goethite and of Se(IV) and As(III) on birnessite occurs within a time scale of minutes. Equilibrium is achieved within a few hours. Adsorption behavior can be described accurately with a surface complexation model. ududGoethite does not oxidize Se(IV) or As(III) in solution at pH 4 and above. However, redox products (Mn(II), Se(V), As(V) are observed when Se(IV) or As(III) is added to aqueous suspensions of birnessite. In the arsenite-birnessite system, the rate of As(V) appearance in solution is equal to the rate of As(III) disappearance from solution while the appearance of Mn(II) in solution is slightly slower. In the selenite-birnessite system, uptake of Se(IV) occurs in minutes. Extent of adsorption decreases with increasing pH. The appearance of measurable Se(VI) occurs slowly (time scale of days to weeks) and is a function of adsorbed selenite. This indicates that the rate of selenite oxidation by birnessite is limited by the rate of electron transfer. Rate data from both arsenic and selenium redox systems are successfully described by a reversible four-step kinetic model that accounts for adsorption of the reduced species, electron-transfer, release of the oxidized species, and release of reduced Mn(II).ududThe data suggest that iron oxides provide an adsorptive sink for mobile Se and As oxyanions, while manganese oxides playa major role in accelerating the oxidation of Se(IV) and As (III). Results on the rates of key chemical processes affecting selenium and arsenic should be useful in understanding complex geochemical cycles and in finding solutions to problems in pollutant transport and accumulation in water-sediment systems.
机译:硒和砷是天然存在的非金属元素,在水生环境中具有复杂的化学和生物学行为。在这项研究中,研究了涉及硒和砷氧阴离子以及两种天然存在的金属氧化物针铁矿(α-FeO​​OH)和水钠锰矿(δ-MnO_2)的吸附,解吸和电子转移反应的速率和机理。针铁矿上Se(IV),As(III)和As(V)的吸附以及水钠锰矿中Se(IV)和As(III)的吸附在几分钟内发生。几个小时内即可达到平衡。吸附行为可以用表面络合模型精确描述。 ud ud针铁矿不会在pH 4及以上的溶液中氧化Se(IV)或As(III)。然而,当将Se(IV)或As(III)加入到水钠锰矿的水悬浮液中时,会观察到氧化还原产物(Mn(II),Se(V),As(V)。溶液中(V)的出现等于溶液中As(III)的消失速率,而溶液中Mn(II)的出现则稍慢;在亚硒酸盐-水钠锰矿体系中,Se(IV)的吸收在数分钟内发生。吸附程度随pH的升高而降低,可测量的Se(VI)的出现缓慢(几天到几周的时间尺度),并且是被吸附的亚硒酸盐的函数,这表明水钠锰矿对亚硒酸盐氧化的速率受到水合速率的限制。砷和硒氧化还原系统的速率数据已通过可逆的四步动力学模型成功描述,该模型解释了还原物种的吸附,电子传递,氧化物种的释放以及还原性Mn(II)的释放。 ud ud数据表明氧化铁提供了吸附性S用作移动性Se和As氧阴离子的油墨,而锰氧化物在加速Se(IV)和As(III)的氧化中起主要作用。有关影响硒和砷的关键化学过程速率的结果,对于理解复杂的地球化学循环以及寻找解决水沉积系统中污染物迁移和累积问题的方法应该是有用的。

著录项

  • 作者

    Scott Michael James;

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  • 年度 1991
  • 总页数
  • 原文格式 PDF
  • 正文语种 {"code":"en","name":"English","id":9}
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