4.7 Article

Immobilization of mercury by pyrite (FeS2)

Journal

ENVIRONMENTAL POLLUTION
Volume 156, Issue 2, Pages 504-514

Publisher

ELSEVIER SCI LTD
DOI: 10.1016/j.envpol.2008.01.011

Keywords

Mercury; Pyrite; Remediation; Sulfide

Funding

  1. Environmental Protection Agency (EPA) [GR832212]
  2. U.S. Department of Energy-Basic Energy Sciences
  3. NSERC
  4. University of Washington
  5. Simon Fraser University
  6. Pacific Northwest National Laboratory
  7. Advanced Photon Source
  8. U.S. Department of Energy
  9. Office of Science
  10. Office of Basic Energy Sciences [DE-AC02-06CH11357]
  11. EPA [909571, GR832212] Funding Source: Federal RePORTER

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Elemental mercury (Hg-0) is a metal with a number of atypical properties, which has resulted in its use in myriad anthropogenic. However, these same properties have also led to sever local subsurface contamination at many places where it has been used. As such, we studied the influence of various parameters on Hg(II) sorption onto (pH, time, Hg(II) concentration), a potential subsurface reactive barrier. Batch sorption studies revealed that total Hg(II) removal increase with both pH and time. X-ray absorption spectroscopy analysis showed that a transformation in the coordination environment at low pH occurred during aging over 2 weeks, to form an ordered monolayer of monodentate Hg-Cl complex on pyrite. In column studies packed with pure quartz sand, the transport of Hg(II) was significantly retarded by the presence of a thin pyrite-sand reactive barrier, although dissolved oxygen inhibited Hg(II) sorption onto pyrite in the column. (C) 2008 Elsevier Ltd. All rights reserved.

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