Technical Papers
Apr 11, 2011

Critical Review on Chemical Stabilization of Metal Contaminants in Shooting Range Soils

Publication: Journal of Hazardous, Toxic, and Radioactive Waste
Volume 16, Issue 3

Abstract

Shooting ranges have come under increased scrutiny in recent years as a potential source of contamination owing to the high loading of lead in the soil. Stabilization by the addition of chemical amendments has been examined as a viable risk-based approach to managing shooting range contamination. Amendments have been shown to immobilize metals to varying degrees, determined by the target contaminant, the amendment used, soil properties, and the reaction kinetics in the contaminated soil and amendment system. Field scale evaluation of the effectiveness of chemical amendments for the stabilization of metal contaminants in shooting range soil is limited. Doubt remains over effectiveness and long-term stability under the varying conditions found in the field, which affect the kinetics of immobilization and dissolution in amended soil.

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Go to Journal of Hazardous, Toxic, and Radioactive Waste
Journal of Hazardous, Toxic, and Radioactive Waste
Volume 16Issue 3July 2012
Pages: 258 - 272

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Received: Aug 28, 2010
Accepted: Apr 7, 2011
Published online: Apr 11, 2011
Published in print: Jul 1, 2012

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Peter Sanderson
Centre for Environmental Risk Assessment and Remediation/Cooperative Research Centre (CERAR/CRC) Care, Univ. of South Australia, Mawson Lakes, South Australia, Australia.
Ravi Naidu, M.ASCE [email protected]
Cooperative Research Centre/Centre for Environmental Risk Assessment and Remediation (CRC Care/CERAR), Univ. of South Australia, Mawson Lakes, South Australia, Australia (corresponding author). E-mail: [email protected]
Nanthi Bolan
Centre for Environmental Risk Assessment and Remediation/Cooperative Research Centre (CERAR/CRC) Care, Univ. of South Australia, Mawson Lakes, South Australia, Australia.
Mark Bowman
Directorate of Environmental Impact Management, Dept. of Defence, Canberra, Australia 2600.

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