Shakib Ahmed Earth and Environmental Sciences Boston College δD AND δ 18 O FRACTIONATION IN GROUNDWATER IN THE VICINITY OF AN ARSENIC CONTAMINATED LANDFILL.

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Presentation transcript:

Shakib Ahmed Earth and Environmental Sciences Boston College δD AND δ 18 O FRACTIONATION IN GROUNDWATER IN THE VICINITY OF AN ARSENIC CONTAMINATED LANDFILL PLUME IN CENTRAL MASSACHUSETTS

ARSENIC CONTAMINATION Hazim Tugun, University of Texas, 2000 Ravenscroft et al., 2008

 Poses two questions:  What are the main sources of arsenic in that particular region  How is it mobilized? ARSENIC NEAR LANDFILL LEACHATE PLUMES Arsenic occurrence in groundwater in New England (from Ayotte et al., 2003). Landfill site

 Compare the behaviors of δD and δ18O fractionation with groundwater composition to better understand the various geochemical processes that are involved in the mobilization of arsenic. OBJECTIVE

HOW WILL THAT BE DONE? Isotopic properties of GW Arsenic Sources

HOW WILL THAT BE DONE? Arsenic Sources Geochemical processes and other groundwater properties Indirectly Related Isotopic properties of GW

δ 18 O AND δD IN GROUNDWATER (IAEA T.R.S. No. 228, 1983; Hackley et al., 1996)

 Contoured and capped  Created on marshland  Hydrogeology  Part of Nashua River watershed  Consists Pleistocene glacial lake-bottom sediments SHEPLEY’S HILL LANDFILL (SHL) Google Maps,2012

 Potential sources of As at SHL:  Waste deposits within the landfill  Peat layer below the landfill  Unconsolidated glacial lake sequences  Bedrock SHL ARSENIC CONTAMINATION (Xie, 2011)

PRELIMINARY ISOTOPE DATA

A S CONCENTRATION VS. ISOTOPIC FRACTIONATION 80ft (Log)

WELL: CH-1D (As concentration: Hildum, 2012)

WELL: CAP-1B

 SHL landfill contains multiple potential sources of As.  Isotopic data compared with groundwater composition data may show the dominant source of As.  This type of approach has not been previously explored.  This small scale research can be applied to bigger scale issues that are occurring around the world. CONCLUSION

 I’d like to thank:  My advisor: Professor Rudolph Hon  Others I’d like to thank:  Stable Isotopes Lab:  BU Stable Isotope Lab  Isotech Laboratories Inc.  UW Stable Isotope Facility  NAU Stable Isotope Laboratory  Wellesley College Chemistry Lab ACKNOWLEDGEMENTS

 Hackley K.C., Liu C.L., Coleman D.D. (1996) Environmental Isotope Characteristics of Landfill Leachates and Gases, Groundwater 34,  Hendry M.J., Wassenaar L.I. (1999) Implications of the distribution of δD in pore waters for groundwater flow and the timing of geologic events in a thick aquitard system, Water Resources Research 35, No. 2,  Hildum, Brendan (2012) Close association within the department, Earth & Environmental Science, Boston College.  International Atomic Energy Agency (1994) Environmental Isotope Data No. 1-10: World Survey of Isotope Concentration in Precipitation, IAEA.  Vuataz F.D., Goff F. (1986) Isotope Geochemistry of Thermal and Nonthermal Waters in the Valles Caldera, Jemez Mountains, Northern New Mexico, Journal of Geophysical Research 91, REFERENCES