Batch study of arsenate (V) adsorption using Akadama mud: Effect of water mineralization

被引:29
作者
Chen, Rongzhi [1 ]
Zhang, Zhenya [1 ]
Feng, Chuanping [2 ]
Lei, Zhongfang [3 ]
Li, Yuan [1 ]
Li, Miao [1 ,2 ]
Shimizu, Kazuya [1 ]
Sugiura, Norio [1 ]
机构
[1] Univ Tsukuba, Grad Sch Life & Environm Sci, Tsukuba, Ibaraki 3058572, Japan
[2] China Univ Geosci, Sch Water Resources & Environm, Beijing 100083, Peoples R China
[3] Fudan Univ, Dept Environm Sci & Engn, Shanghai 200433, Peoples R China
基金
日本科学技术振兴机构;
关键词
Arsenate batch adsorption; Akadama mud; Langmuir isotherms; Sorption kinetics; Water mineralization; CONTAMINATED WATER; AQUEOUS-SOLUTION; REMOVAL; GROUNDWATER; MECHANISM; REMEDIATION; ARSENIC(V); KINETICS; SORPTION;
D O I
10.1016/j.apsusc.2009.11.058
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
Akadama mud, consisting mainly of different forms of iron and aluminum oxide minerals, was used for arsenate (V) adsorption from aqueous solutions. The adsorption process fitted the first-order kinetic equation and the Langmuir monolayer model well. The adsorption capacity, estimated by the Langmuir isotherm model, was 5.30 mg/g at 20 +/- 0.5 degrees C. The effects of the solution properties (initial concentration of As (V), pH, temperature, and mineralization degree) on As (V) removal were investigated. Various mineralization degrees in underground water were simulated by adjusting the ionic strength of the solution or adding coexisting ions to the contaminated solution. It was found that mineralization of the water significantly influenced the arsenic adsorption. The existence of multivalent metallic cations significantly enhanced the As (V) adsorption ability, whereas competing anions such as fluoride and phosphate greatly decreased the As (V) adsorption. This result suggests that Akadama mud is more suitable for arsenic adsorption in low-level phosphate and fluoride solutions. The loaded Akadama mud could be desorbed at polar pH conditions, especially in acidic conditions, and more than 65% As (V) sorption has been achieved at pH 1. (C) 2009 Elsevier B. V. All rights reserved.
引用
收藏
页码:2961 / 2967
页数:7
相关论文
共 38 条
  • [1] Agency for toxic substances and disease registry ATSDR, 2005, TOP 20 HAZ SUBST ATS
  • [2] A biomaterial based approach for arsenic removal from water
    Al Rmalli, SW
    Harrington, CF
    Ayub, M
    Haris, PI
    [J]. JOURNAL OF ENVIRONMENTAL MONITORING, 2005, 7 (04): : 279 - 282
  • [3] Removal of arsenic from water by zero-valent iron
    Bang, S
    Korfiatis, GP
    Meng, XG
    [J]. JOURNAL OF HAZARDOUS MATERIALS, 2005, 121 (1-3) : 61 - 67
  • [4] Investigations on arsenic(V) removal by modified calcined bauxite
    Bhakat, P. B.
    Gupta, A. K.
    Ayoob, S.
    Kundu, S.
    [J]. COLLOIDS AND SURFACES A-PHYSICOCHEMICAL AND ENGINEERING ASPECTS, 2006, 281 (1-3) : 237 - 245
  • [5] Arsenic in groundwater: A threat to sustainable agriculture in South and South-east Asia
    Brammer, Hugh
    Ravenscroft, Peter
    [J]. ENVIRONMENT INTERNATIONAL, 2009, 35 (03) : 647 - 654
  • [6] Biomass waste-derived activated carbon for the removal of arsenic and manganese ions from aqueous solutions
    Budinova, T.
    Savova, D.
    Tsyntsarski, B.
    Ania, C. O.
    Cabal, B.
    Parra, J. B.
    Petrov, N.
    [J]. APPLIED SURFACE SCIENCE, 2009, 255 (08) : 4650 - 4657
  • [7] Arsenic adsorption from aqueous solution on synthetic zeolites
    Chutia, Pratap
    Kato, Shigeru
    Kojima, Toshinori
    Satokawa, Shigeo
    [J]. JOURNAL OF HAZARDOUS MATERIALS, 2009, 162 (01) : 440 - 447
  • [8] Sorption materials for arsenic removal from water: A comparative study
    Daus, B
    Wennrich, R
    Weiss, H
    [J]. WATER RESEARCH, 2004, 38 (12) : 2948 - 2954
  • [9] Arsenic geochemistry and health
    Duker, AA
    Carranza, EJM
    Hale, M
    [J]. ENVIRONMENT INTERNATIONAL, 2005, 31 (05) : 631 - 641
  • [10] Uptake of arsenite and arsenate by clinoptilolite-rich tuffs
    Elizalde-González, MP
    Mattusch, J
    Wennrich, R
    Morgenstern, P
    [J]. MICROPOROUS AND MESOPOROUS MATERIALS, 2001, 46 (2-3) : 277 - 286