742-6 Coupled Biogeochemical and Hydrologic Processes Governing Arsenic Transport within Evolving Sedimentary Basins of Southeast Asia.

See more from this Division: S02 Soil Chemistry
See more from this Session: Oxyanions in Soil Environments: II

Wednesday, 8 October 2008: 2:45 PM
George R. Brown Convention Center, 360C

Benjamin Kocar1, Samantha Ying1, Matthew Polizzotto1, Shawn Benner2, Mengieng Ung3, Bunseang Suy3, Kongkea Phan3, Mickey Sampson3 and Scott Fendorf1, (1)School of Earth Sciences, Stanford University, Stanford, CA
(2)Department of Geosciences, BoiseState University, Boise, ID
(3)Resource Development International, Kean Svay, Cambodia
Abstract:
Weathering of As-bearing rocks in the Himalayas has resulted in the transport of sediments down the major river systems such as the Brahmaputra, Ganges, Red, Irrawaddy, and Mekong.  Groundwater in these river basins commonly has As concentrations exceeding the World Health Organization’s recommended drinking water limit (10 μg/L) by more than two orders of magnitude.  Understanding the reason(s) for these elevated concentrations of As within the sediments of Southeast Asia has remained a challenge, owing to the difficulty of separating mechanisms responsible for As release (e.g. As and Fe reduction) and local to region hydrology. We deciphered, using a combination of field and laboratory measurements of biogeochemical and hydrologic factors, dominant mechanisms of As release and transport within surficial soils/sediments within an As-afflicted field area of the Mekong delta. Our results illustrate that clay (0-12m deep) underlying oxbow and wetland environments are subjected to continuously reducing conditions due to ample carbon input and saturated conditions. Ensuing reductive dissolution of As-bearing Fe (hydr)oxides releases As, which then migrates to the underlying sandy aquifer (>12m deep). Reactive transport modeling using PHREEQC and MIN3P was constrained with chemical and hydrologic field measurements, and provides a calibrated illustration of As release and transport within our field site. Our resulting simulations indicate that As release occurs within the clays underlying organic-rich, permanently inundated locations providing sufficient As to the aqueous phase for widespread contamination of the aquifer, and that release occurs for several thousand years prior to depletion of As from the solid phase.

See more from this Division: S02 Soil Chemistry
See more from this Session: Oxyanions in Soil Environments: II