Geochemical study of arsenic release mechanisms in the Bengal Basin groundwater

To investigate arsenic mobility in the Bengal Basin groundwater, we sampled water wells and sediments throughout the region. There are strong correlations among high levels of dissolved arsenic and iron, ammonia, and methane, especially in samples from a single site (Laxmipur). No linkage is seen between As and agricultural tracers such as phosphate. The association of As and Fe occurs because arsenic strongly adsorbs onto FeOOH particles in river water. They flocculate with other fine‐grained particles at the freshwater/saltwater transition zone. Subsequent bacterially mediated reduction of FeOOH in the clay releases the adsorbed arsenic. Weathering of As‐bearing mica plays a significant role in the As budget. The “correlated” presence of As, CH4, and NH4 in water supply wells is the result of diffusion out of organic‐rich clay into the more permeable zones. Arsenic is mainly released from recent sediments at <50 m depth deposited in the GBR floodplain as sea level rose throughout the Holocene.

[1]  M. Thirlwall,et al.  Arsenic in groundwater: Testing pollution mechanisms for sedimentary aquifers in Bangladesh , 2001 .

[2]  U. Fehn,et al.  Dating of pore waters with (129)I: relevance for the origin of marine gas hydrates , 2000, Science.

[3]  S. Acharyya,et al.  Arsenic toxicity of groundwater in parts of the Bengal basin in India and Bangladesh: the role of Quaternary stratigraphy and Holocene sea-level fluctuation , 2000 .

[4]  S. Kuehl,et al.  The significance of large sediment supply, active tectonism, and eustasy on margin sequence development: Late Quaternary stratigraphy and evolution of the Ganges–Brahmaputra delta , 2000 .

[5]  M. Karim Arsenic in groundwater and health problems in Bangladesh , 2000 .

[6]  A. Smith,et al.  Contamination of drinking-water by arsenic in Bangladesh: a public health emergency. , 2000, Bulletin of the World Health Organization.

[7]  S. Lahiri,et al.  Arsenic poisoning in the Ganges delta , 1999, Nature.

[8]  J. W. Ball,et al.  New Method for the Direct Determination of Dissolved Fe(III) Concentration in Acid Mine Waters , 1999 .

[9]  R. Rosenzweig,et al.  Arsenic Mobilization by the Dissimilatory Fe(III)-Reducing Bacterium Shewanella alga BrY , 1999 .

[10]  R. T. Nicksona,et al.  Mechanism of arsenic release to groundwater , Bangladesh and West Bengal , 1999 .

[11]  Awwa,et al.  Standard Methods for the examination of water and wastewater , 1999 .

[12]  M. Allison Historical Changes in the Ganges-Brahmaputra Delta Front , 1998 .

[13]  K. Ahmed,et al.  Arsenic poisoning of Bangladesh groundwater , 1998, Nature.

[14]  Christian Hübscher,et al.  The submarine delta of the Ganges–Brahmaputra: cyclone-dominated sedimentation patterns , 1998 .

[15]  D. Chakraborti,et al.  Impact of safe water for drinking and cooking on five arsenic-affected families for 2 years in West Bengal, India. , 1998, The Science of the total environment.

[16]  N. Lundberg,et al.  Cenozoic history of the Himalayan-Bengal system: Sand composition in the Bengal basin, Bangladesh , 1998 .

[17]  D. Chakraborti,et al.  DETAILED STUDY REPORT OF SAMATA, ONE OF THE ARSENIC-AFFECTED VILLAGES OF JESSORE DISTRICT, BANGLADESH , 1998 .

[18]  D. Chakraborti,et al.  Groundwater arsenic calamity in Bangladesh , 1997 .

[19]  G. Bennett Arsenic in the environment — Part I: Cycling and characterization , 1996 .

[20]  D. Chakraborti,et al.  Arsenic in groundwater in six districts of West Bengal, India , 1996, Environmental geochemistry and health.

[21]  N. R. Rajagopal,et al.  GROUNDWATER DEVELOPMENT IN THE ARSENIC-AFFECTED ALLUVIAL BELT OF WEST BENGAL : SOME QUESTIONS , 1996 .

[22]  D. Chakraborti,et al.  ARSENIC IN GROUNDWATER IN SEVEN DISTRICTS OF WEST BENGAL, INDIA : THE BIGGEST ARSENIC CALAMITY IN THE WORLD , 1996 .

[23]  D. Lovley,et al.  Growth of Strain SES-3 with Arsenate and Other Diverse Electron Acceptors , 1995, Applied and environmental microbiology.

[24]  Michael H. Ramsey,et al.  Sequential extraction of soils for multielement analysis by ICP-AES , 1995 .

[25]  D. Chakraborti,et al.  Arsenic in ground water in six districts of West bengal, India: the biggest arsenic calamity in the world. Part 2. Arsenic concentration in drinking water, hair, nails, urine, skin-scale and liver tissue (biopsy) of the affected people. , 1995, The Analyst.

[26]  Dianne Ahmann,et al.  Microbe grows by reducing arsenic , 1994, Nature.

[27]  S. Schiff,et al.  A validation of the 3H/3He method for determining groundwater recharge , 1993 .

[28]  Masatomo Umitsu,et al.  Late quaternary sedimentary environments and landforms in the Ganges Delta , 1993 .

[29]  K. Farley,et al.  Rare gases in Samoan xenoliths , 1992 .

[30]  John A. Cherry,et al.  Tritium and helium: 3 as groundwater age tracers in the Borden Aquifer , 1992 .

[31]  J. Walsh,et al.  The Effects of Fault Geometries and Slip-Surface Characteristics on 3-D Reservoir Connectivity , 1991 .

[32]  A. Hulbert,et al.  Sequence Stratigraphy and the Evolution of the Ganges-Brahmaputra Delta Complex (1) , 1991 .

[33]  S. E. Long,et al.  Method 200. 8 determination of trace elements in waters and wastes by inductively coupled plasma: Mass spectrometry. Revision 4. 3 , 1990 .

[34]  W. Moore,et al.  Major ion chemistry of the Ganga-Brahmaputra river system: Weathering processes and fluxes to the Bay of Bengal , 1989 .

[35]  R. Poreda,et al.  Tritium and helium isotopes as hydrologic tracers in a shallow unconfined aquifer , 1988 .

[36]  R. H. Meade,et al.  World-Wide Delivery of River Sediment to the Oceans , 1983, The Journal of Geology.

[37]  V. Subramanian Chemical and suspended-sediment characteristics of rivers of India , 1979 .

[38]  W. Jenkins,et al.  Determination of tritium by mass spectrometric measurement of 3He , 1976 .

[39]  James M. Coleman,et al.  Brahmaputra River : Channel processes and sedimentation , 1969 .

[40]  John N. Holeman The Sediment Yield of Major Rivers of the World , 1968 .

[41]  Marianne Hanson,et al.  The International Atomic Energy Agency , 2021, Nature.