Sequestration of Hydrophobic Organic Contaminants by Geosorbents

Richard G. Luthy*
Department of Civil and Environmental Engineering, Carnegie Mellon University, Pittsburgh, Pennsylvania 15213-3890
George R. Aiken
U.S. Geological Survey, Water Resources Division, 3215 Marine Street, Boulder, Colorado 80303-1066
Mark L. Brusseau
Soil, Water and Environmental Science Department, 429 Shantz Building, 38, The University of Arizona, Tucson, Arizona 85721
Scott D. Cunningham
DuPont Environmental Biotechnology, Glasgow Building 300, P.O. Box 6101, Newark, Delaware 19714-6101
Philip M. Gschwend
Department of Civil and Environmental Engineering, 48-415, 15 Vassar Street, Massachusetts Institute of Technology, Cambridge, Massachusetts 02139
Joseph J. Pignatello
The Connecticut Agricultural Experimental Station, 123 Huntington Street, P.O. Box 1106, New Haven, Connecticut 06504
Martin Reinhard
Department of Civil and Environmental Engineering, Stanford University, Stanford, California 94305-4020
Samuel J. Traina
School of Natural Resources, The Ohio State University, 410B Kottman Hall, 2021 Coffey Road, Columbus, Ohio 43210-1086
Walter J. Weber, Jr.
Department of Civil and Environmental Engineering, Environmental and Water Resources Engineering Building, The University of Michigan, Ann Arbor, Michigan 48109-2125
John C. Westall
Department of Chemistry, Oregon State University, Corvallis, Oregon 97331
Environ. Sci. Technol., 1997, 31 (12), pp 3341–3347
DOI: 10.1021/es970512m
Publication Date (Web): November 26, 1997
Copyright © 1997 American Chemical Society

Abstract

The chemical interactions of hydrophobic organic contaminants (HOCs) with soils and sediments (geosorbents) may result in strong binding and slow subsequent release rates that significantly affect remediation rates and endpoints. The underlying physical and chemical phenomena potentially responsible for this apparent sequestration of HOCs by geosorbents are not well understood. This challenges our concepts for assessing exposure and toxicity and for setting environmental quality criteria. Currently there are no direct observational data revealing the molecular-scale locations in which nonpolar organic compounds accumulate when associated with natural soils or sediments. Hence macroscopic observations are used to make inferences about sorption mechanisms and the chemical factors affecting the sequestration of HOCs by geosorbents. Recent observations suggest that HOC interactions with geosorbents comprise different inorganic and organic surfaces and matrices, and distinctions may be drawn along these lines, particularly with regard to the roles of inorganic micropores, natural sorbent organic matter components, combustion residue particulate carbon, and spilled organic liquids. Certain manipulations of sorbates or sorbent media may help reveal sorption mechanisms, but mixed sorption phenomena complicate the interpretation of macroscopic data regarding diffusion of HOCs into and out of different matrices and the hysteretic sorption and aging effects commonly observed for geosorbents. Analytical characterizations at the microscale, and mechanistic models derived therefrom, are needed to advance scientific knowledge of HOC sequestration, release, and environmental risk.

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History

  • Published In Issue November 26, 1997
  • Received for review June 10, 1997
    Revised manuscript received August 20, 1997
    Accepted August 22, 1997

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