Arsenic pollution in groundwater: a self-organizing complex geochemical process in the deltaic sedimentary environment, Bangladesh

被引:84
|
作者
Tareq, SM [1 ]
Safiullah, S
Anawar, HM
Rahman, MM
Ishizuka, T
机构
[1] Nagoya Univ, Grad Sch Environm Studies, Div Earth & Environm Sci, Chikusa Ku, Nagoya, Aichi 4648601, Japan
[2] Jahangirnagar Univ, Dept Environm Sci, Dhaka 1342, Bangladesh
[3] Jahangirnagar Univ, Dept Chem, Dhaka 1342, Bangladesh
[4] Niigata Univ, Grad Sch Sci & Technol, Niigata 9502181, Japan
[5] Univ Tokyo, Ocean Res Inst, Tokyo 1138654, Japan
关键词
arsenic pollution; alluvial aquifer; arsenic leaching; mobilization; vertical distribution; Bangladesh;
D O I
10.1016/S0048-9697(03)00266-3
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The presence of considerable concentrations of As (Sonargaon: below detection limit (bdl)-1.46 mg/l; Faridpur: bdl-1.66 mg/l) and some other elements (like B, F, U) in groundwater of the Ganges-Meghna-Brahmaputra (G-M-B) rivers flood plain indicate that several millions of people are consuming contaminated water. Conditions regulating the mobilization and diagenetic behavior of arsenic in sediments are not well characterized, although understanding these conditions is essential in order to predict the modes of transfer of this contaminant from sediments to groundwater. Analyses of vertical profiles of total arsenic and iron as well as easily soluble As and reducible (reactive) iron concentrations in sediments of the Ganges and Meghna flood plains show no arsenic-enriched layer up to 36-m depth. However, arsenic content in sediments is relatively higher than mean crustal concentration, showing some peaks (Sonargaon: 27.9 mg/kg; 3m, 31.5 mg/kg; 9 m, 27.30 mg/kg; 16 m, 37.70 mg/kg; 29.5 m, Faridpur: 19.80 mg/kg; 6 m, 26.60 mg/kg; 14.5 m, 29.40 mg/kg; 25 m) depending on the periodical differences in sedimentary cycling of arsenic, metal (hydr)oxides and organic matter. Seasonal changes have no clear or consistent effect on the groundwater arsenic concentrations; with the exception of a small-scale localized irregular change (10-16%). However, easily reducible metal oxides and hydroxides were significant factors affecting the retention of arsenic by sediments during leaching. The biogeochemical cycling of arsenic and iron is closely coupled in deltaic systems where iron oxy-hydroxides provide a carrier phase for the deposition of arsenic in sediments. Analytical results of mimic leaching experiments strongly supported the reduction (Fe oxy-hydroxides) mechanism for arsenic mobilization in alluvial aquifer of deltaic sedimentary environment of G-M-B rivers flood plain. (C) 2003 Elsevier Science B.V. All rights reserved.
引用
收藏
页码:213 / 226
页数:14
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