Compost-based permeable reactive barriers for the source treatment of arsenic contaminations in aquifers:: Column studies and solid-phase investigations

被引:15
作者
Köber, R
Daus, B
Ebert, M
Mattusch, J
Welter, E
Dahmke, A
机构
[1] Univ Kiel, Inst Geosci, D-24098 Kiel, Germany
[2] UFZ Helmholtz Ctr Environm Res, D-04318 Leipzig, Germany
[3] DESY, Hamburger Synchrotronstrahlungslabor, D-22603 Hamburg, Germany
关键词
D O I
10.1021/es0503579
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The bulk of arsenic (As) at contaminated sites is frequently associated with iron (hydr)oxides. Various studies ascribe increasing dissolved As concentrations to the transformation of iron (hydr)oxides into iron sulfides, which is initiated by dissolved sulfide. We investigated whether this processes can be utilized as a source treatment approach using compost-based permeable reactive barriers (PRB), which promote microbial sulfate reduction. Arsenic-bearing aquifer sediment from a contaminated industrial site showed a decrease in As content of < 10% after 420 days of percolation with sulfide-free artificial groundwater. In contrast, water that had previously passed through organic matter and exhibited sulfide concentrations of 10-30 mg/L decreased As content in the sediment by 87% within 360 days. X-ray diffraction showed no arsenic sulfides, but XANES spectra (X-ray absorption near edge structure) and associated linear combinations revealed that adsorbed arsenate of the original sediment was in part reduced to arsenite and indicated the formation of minor amounts of a substance that contains As and sulfur. The speciation of dissolved As changed from initially As(V)-dominated to As(III)-dominated after sulfide flushing was started, which increases the mobility of As. Because sulfide can be supplied not only by compost-based PRBs but also by direct injection, sulfide flushing has a wide range of application for the source treatment of arsenic.
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页码:7650 / 7655
页数:6
相关论文
共 30 条
[1]   Microbial mobilization of arsenic from sediments of the Aberjona Watershed [J].
Ahmann, D ;
Krumholz, LR ;
Hemond, HF ;
Lovley, DR ;
Morel, FMM .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1997, 31 (10) :2923-2930
[2]   Extraction of arsenic in a synthetic arsenic-contaminated soil using phosphate [J].
Alam, MGM ;
Tokunaga, S ;
Maekawa, T .
CHEMOSPHERE, 2001, 43 (08) :1035-1041
[3]   INTERACTIONS BETWEEN ARSENIC AND IRON OXYHYDROXIDES IN LACUSTRINE SEDIMENTS [J].
BELZILE, N ;
TESSIER, A .
GEOCHIMICA ET COSMOCHIMICA ACTA, 1990, 54 (01) :103-109
[4]   Geochemistry of a permeable reactive barrier for metals and acid mine drainage [J].
Benner, SG ;
Blowes, DW ;
Gould, WD ;
Herbert, RB ;
Ptacek, CJ .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1999, 33 (16) :2793-2799
[5]   REACTIVE IRON IN MARINE-SEDIMENTS [J].
CANFIELD, DE .
GEOCHIMICA ET COSMOCHIMICA ACTA, 1989, 53 (03) :619-632
[6]   THE REACTIVITY OF SEDIMENTARY IRON MINERALS TOWARD SULFIDE [J].
CANFIELD, DE ;
RAISWELL, R ;
BOTTRELL, S .
AMERICAN JOURNAL OF SCIENCE, 1992, 292 (09) :659-683
[7]   Effects of pH and phosphate competition on the transport of arsenate [J].
Darland, JE ;
Inskeep, WP .
JOURNAL OF ENVIRONMENTAL QUALITY, 1997, 26 (04) :1133-1139
[8]   Sorption materials for arsenic removal from water: A comparative study [J].
Daus, B ;
Wennrich, R ;
Weiss, H .
WATER RESEARCH, 2004, 38 (12) :2948-2954
[9]  
DETHLEFSEN F, 2004, THESIS U KIEL KIEL G
[10]   THE SOLUBILITY OF AMORPHOUS AS2S3 FROM 25 TO 90-DEGREES-C [J].
EARY, LE .
GEOCHIMICA ET COSMOCHIMICA ACTA, 1992, 56 (06) :2267-2280