Open AccessStabilization and solidification of chromium-contaminated soil
Author(s) -
C. A. Cherne,
Bruce M. Thomson,
R. Conway
Publication year - 1997
Language(s) - English
Resource type - Reports
DOI - 10.2172/555255
Subject(s) - chromium , hexavalent chromium , sulfuric acid , ferrous , leaching (pedology) , toxicity characteristic leaching procedure , chemistry , sulfate , contamination , chromium compounds , metallurgy , soil contamination , environmental chemistry , chromate conversion coating , nuclear chemistry , inorganic chemistry , materials science , environmental science , soil water , heavy metals , ecology , biology , soil science
Chromium-contaminated soil is a common environmental problem in the United States as a result of numerous industrial processes involving chromium. Hexavalent chromium [Cr(VI)] is the species of most concern because of its toxicity and mobility in groundwater. One method of diminishing the environmental impact of chromium is to reduce it to a trivalent oxidation state [Cr(III)], in which it is relatively insoluble and nontoxic. This study investigated a stabilization and solidification process to minimize the chromium concentration in the Toxicity Characteristic Leaching Procedure (TCLP) extract and to produce a solidified waste form with a compressive strength in the range of 150 to 300 pounds per square inch (psi). To minimize the chromium in the TCLP extract, the chromium had to be reduced to the trivalent oxidation state. The average used in this study was an alluvium contaminated with chromic and sulfuric acid solutions. The chromium concentration in the in the in situ soil was 1212 milligrams per kilogram (mg/kg) total chromium and 275 mg/kg Cr(VI). The effectiveness of iron, ferrous sulfate to reduce Cr(VI) was tested in batch experiments