Speciation of Selenium, Arsenic, and Zinc in Class C Fly Ash

Yun Luo, Daniel E. Giammar, Brittany L. Huhmann, and Jeffrey G. Catalano*
Department of Earth and Planetary Sciences, and Department of Energy, Environmental and Chemical Engineering, Washington University in St. Louis, 1 Brookings Drive, St. Louis, Missouri 63130, United States
Energy Fuels, 2011, 25 (7), pp 2980–2987
DOI: 10.1021/ef2005496
Publication Date (Web): June 7, 2011
Copyright © 2011 American Chemical Society
Telephone: +1-314-935-6015. Fax: +1-314-935-7361. E-mail: catalano@wustl.edu.

§ Author Present Address

Gemological Institute of America, Carlsbad, California 92008, United States.

Abstract

A major environmental concern associated with coal fly ash is the mobilization of trace elements that may contaminate water. To better evaluate proper use of fly ash, determine appropriate disposal methods, and monitor postdisposal conditions, it is important to understand the speciation of trace elements in fly ash and their possible environmental impact. The speciation of selenium, arsenic, and zinc was determined in five representative Class C fly ash samples from combustion of sub-bituminous Powder River Basin coal using synchrotron-based X-ray absorption spectroscopy to provide an improved understanding of the mechanisms of trace element association with the fly ash. Selenium in all fly ash samples occurs predominantly as Se(IV), with the exception of one sample, in which there was a minor amount of Se(0). Se(0) is likely associated with the high content of unburned coal in the sample. Arsenic exists in the fly ash as a single phase most consistent with calcium pyroarsenate. In contrast, zinc occurs as two distinct species in the silicate glass matrix of the fly ash. This work demonstrates that residual carbon in fly ash may reduce potential Se mobility in the environment by retaining it as less soluble elemental Se instead of Se(IV). Further, this work suggests that As and Zn in Class C fly ash will display substantially different release and mobilization behaviors in aquatic environments. While As release will primarily depend upon the dissolution and hydrolysis of calcium pyroarsenate, Zn release will be controlled by the dissolution of alkaline aluminosilicate glass in the ash.

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History

  • Published In Issue July 21, 2011
  • Article ASAPJune 23, 2011
  • Just Accepted ManuscriptJune 07, 2011
  • Received: April 11, 2011
    Revised: May 31, 2011

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