|
|||||||||||||
|
|||||||||||||
In situ chemical fixation of arsenic-contaminated soils: An experimental study Li Yang Rona J. Donahoe James C. Redwine
ABSTRACT: This paper reports the results of an experimental study testing a low-cost in situ
chemical fixation method designed to reclaim arsenic-contaminated subsurface soils. Subsurface
soils from several industrial sites in southeastern U.S. were contaminated with arsenic through
heavy application of herbicide containing arsenic trioxide. The mean concentrations of
environmentally available arsenic in soils collected from the two study sites, FW and BH, are 325
mg/kg and 900 mg/kg, respectively. The soils are sandy loams with varying mineralogical and
organic contents. The previous study [Yang L, Donahoe RJ. The form, distribution and mobility of
arsenic in soils contaminated by arsenic trioxide, at sites in Southeast USA. Appl Geochem
2007;22:320 341] indicated that a large portion of the arsenic in both soils is associated with
amorphous aluminum and iron oxyhydroxides and shows very slow release against leaching by
synthetic precipitation. The soil's amorphous aluminum and iron oxyhydroxides content was found to
have the most significant effect on its ability to retain arsenic.Based on this observation,
contaminated soils were reacted with different treatment solutions in an effort to promote the
formation of insoluble arsenic-bearing phases and thereby decrease the leachability of arsenic.
Ferrous sulfate, potassium permanganate and calcium carbonate were used as the reagents for the
chemical fixation solutions evaluated in three sets of batch experiments: (1) FeSO4; (2) FeSO4 and
KMnO4; (3) FeSO4, KMnO4 and CaCO3. The optimum treatment solutions for each soil were identified
based on the mobility of arsenic during sequential leaching of treated and untreated soils using
the fluids described in EPA Method 1311 [USEPA. Method 1311: toxicity characteristic leaching
procedure. Test methods for evaluating solid waste, physical/chemical methods. 3rd ed. Washington,
DC: U.S. Environmental Protection Agency, Office of Solid Waste. U.S. Government Printing Office;
1992] toxic characteristics leaching procedure (TCLP) and EPA Method 1312 [USEPA. Method 1312:
synthetic precipitation leaching procedure. Test methods for evaluating solid waste,
physical/chemical methods. 3rd ed. Washington, DC: U.S. Environmental Protection Agency, Office of
Solid Waste. U.S. Government Printing Office; 1994] synthetic precipitation leaching procedure
(SPLP).Both FW and BH soils showed significant decreases in arsenic leachability for all three
treatment solutions, compared to untreated soil. While soils treated with solution (3) showed the
best results with subsequent TCLP sequential leaching, SPLP sequential leaching of treated soils
indicated that lowest arsenic mobility was obtained using treatment solution (1). Treatment
solution (1) with only FeSO4 is considered the best choice for remediation of arsenic-contaminated
soil because SPLP sequential leaching better simulates natural weathering. Analysis of treated
soils produced no evidence of newly-formed arsenic-bearing phases in either soil after treatment.
Sequential chemical extractions of treated soils indicate that surface complexation of arsenic on
ferric hydroxide is the major mechanism for the fixation process.
SUGGESTED CITATION:
| |||||||||||||
|
|||||||||||||