Effects of pH, dissolved oxygen, and aqueous ferrous iron on the adsorption of arsenic to lepidocrocite

被引:104
作者
Wang, Lin [1 ]
Giammar, Daniel E. [1 ]
机构
[1] Washington Univ, Dept Energy Environm & Chem Engn, St Louis, MO USA
基金
美国国家科学基金会;
关键词
Arsenic adsorption; Electrocoagulation; Surface complexation modeling; Fe(II)-mediated arsenic oxidation; INITIO MOLECULAR GEOMETRIES; DRINKING-WATER; SURFACE COMPLEXATION; REMOVAL; OXIDATION; GOETHITE; ELECTROCOAGULATION; SORPTION; FE(II); GROUNDWATER;
D O I
10.1016/j.jcis.2015.02.047
中图分类号
O64 [物理化学(理论化学)、化学物理学];
学科分类号
070304 ; 081704 ;
摘要
The adsorption of arsenic to iron oxyhydroxides strongly depends on water chemistry. Iron(III) oxyhydroxides can also participate in the oxidation of As(III) to As(V), which changes arsenic's toxicity and adsorption behavior. As(III) and As(V) adsorption to lepidocrocite (gamma-FeOOH) were examined in batch experiments that explored the effects of lepidocrocite dose, pH, availability of dissolved oxygen, and the presence of aqueous Fe(II) on adsorption. Lepidocrocite is an iron oxyhydroxide found in soils, and it is one of the major products of iron electrocoagulation for water treatment. A surface complexation model was able to describe the adsorption of both As(III) and As(V) to lepidocrocite over a broad range of conditions. The concentration and oxidation states of arsenic in solution were measured over the course of the reactions. At both oxic and anoxic conditions. As(III) was oxidized to As(V) in systems that contained lepidocrocite together with Fe(II): this oxidation led to overall enhanced arsenic adsorption at near neutral pH. With oxygen the pH-dependent generation of oxidants from the Fenton reaction drove the As(III) oxidation. In the absence of oxygen the As(III) was probably oxidized by Fe(III) in lepidocrocite that had become more reactive upon reaction with Fe(II). (C) 2015 Elsevier Inc. All rights reserved.
引用
收藏
页码:331 / 338
页数:8
相关论文
共 57 条
[1]   Redox Transformation of Arsenic by Fe(II)-Activated Goethite (α-FeOOH) [J].
Amstaetter, Katja ;
Borch, Thomas ;
Larese-Casanova, Philip ;
Kappler, Andreas .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2010, 44 (01) :102-108
[2]   Effects of pH and ionic strength on the adsorption of phosphate and arsenate at the goethite-water interface [J].
Antelo, J ;
Avena, M ;
Fiol, S ;
López, R ;
Arce, F .
JOURNAL OF COLLOID AND INTERFACE SCIENCE, 2005, 285 (02) :476-486
[3]   Removal of arsenic from aqueous solution using electrocoagulation [J].
Balasubramanian, N. ;
Kojima, Toshinori ;
Basha, C. Ahmed ;
Srinivasakannan, C. .
JOURNAL OF HAZARDOUS MATERIALS, 2009, 167 (1-3) :966-969
[4]   Photoinduced Oxidation of Arsenite to Arsenate in the Presence of Goethite [J].
Bhandari, Narayan ;
Reeder, Richard J. ;
Strongin, Daniel R. .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2012, 46 (15) :8044-8051
[5]   Photoinduced Oxidation of Arsenite to Arsenate on Ferrihydrite [J].
Bhandari, Narayan ;
Reeder, Richard J. ;
Strongin, Daniel R. .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2011, 45 (07) :2783-2789
[6]   Iron(II)-catalyzed oxidation of arsenic(III) in a sediment column [J].
Bisceglia, KJ ;
Rader, KJ ;
Carbonaro, RF ;
Farley, KJ ;
Mahony, JD ;
Di Toro, DM .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2005, 39 (23) :9217-9222
[7]   CRITICAL-REVIEW OF RATE CONSTANTS FOR REACTIONS OF HYDRATED ELECTRONS, HYDROGEN-ATOMS AND HYDROXYL RADICALS (.OH/.O-) IN AQUEOUS-SOLUTION [J].
BUXTON, GV ;
GREENSTOCK, CL ;
HELMAN, WP ;
ROSS, AB .
JOURNAL OF PHYSICAL AND CHEMICAL REFERENCE DATA, 1988, 17 (02) :513-886
[8]  
DAVIS JA, 1990, REV MINERAL, V23, P177
[9]   Comparison of arsenic(V) and arsenic(III) sorption onto iron oxide minerals: Implications for arsenic mobility [J].
Dixit, S ;
Hering, JG .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2003, 37 (18) :4182-4189
[10]  
Dzombak D.A., 1990, SURFACE COMPLEXATION