H107-04
Geochemical controls on mobilization and transport of tungsten in sediments from Fallon, Nevada: The importance of a possible anthropogenic tungsten source

Friday, 11 December 2020: 04:12
Virtual
Saugata Datta, University of Texas at San Antonio, GEOLOGICAL SCIENCES, San Antonio, TX, United States, Harshad Vijay Kulkarni, University of Texas at San Antonio, San Antonio, TX, United States, Chad Hobson, Kansas State University, Geology, Manhattan, KS, United States, Karen Johannesson, University of Massachusetts Boston, School for the Environment, Boston, MA, United States, Anthony J Bednar, US Army Corps of Engineers - ERDC/EL, Vicksburg, MS, United States and Ganga Hettiarachchi, Kansas State University, Agronomy, Manhattan, KS, United States
Abstract:
Elevated tungsten (W) levels in human body fluids have been linked to a childhood leukemia cluster in Fallon, Nevada. We studied the occurrence and speciation of W in sediments from Fallon, NV in order to understand mobilization of W in the environment. Sedimentary W concentration was measured by total and sequential extraction followed by high resolution inductively coupled plasma mass spectrometer (HR-ICP-MS) analysis, whereas the speciation was determined by μ-XANES. The water extractable fraction of sedimentary W was determined by HR-ICP-MS and the aqueous species of W were identified by size exclusion chromatography. Our results indicate that sedimentary W concentrations ranged between 37 and 25,908 mg/kg at Fallon, NV, of which 20 – 50% occurred as metallic W0 and the rest occurred as oxide (WVIO3) based on μ-XANES analysis. Only 0.21-1.36% of the sedimentary W was extractable with water at neutral pH (i.e. 0.1–352 µg/L) and it primarily occurred as the tungstate oxyanion (WO42-). These findings are consistent with earlier studies that reported mobilization of up to 1,070 µg/L W from contaminated soil with deionized water (Bednar et al., 2008) as well as studies that reported groundwater W concentrations in the range of 0.27-742 µg/L (Seiler et al., 2005; Cutler, 2011; Mohajerin et al., 2014) and 3 – 610 µg/L (Walker and Fosbury, 2009). These findings suggest that that metallic W0 particles from currently unknown but local anthropogenic source(s) are deposited onto surface sediments and are oxidized by meteoric water to form WVIO3. Oxidized W forms soluble tungstate oxyanions that are transported along the groundwater flow path. Polymeric species of dissolved W appear to be more mobile, whereas monomeric W species sorbs onto the sediments during the transport. Our study (Hobson et al., 2020) proposes a model to illustrate mobilization of W from sediments to groundwater, which is important to constrain the link between environmental W levels and human health.