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Arsenic Immobilization by Calcium Arsenate Formation

Lime additions to arsenic-containing wastes have been proven to be beneficial in reducing the mobility of dissolved arsenic, presumably through the formation of low-solubility calcium arsenates. However, the role of calcium arsenate formation in reducing the concentrations of dissolved arsenic has n...

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Published in:Environmental science & technology 1999-11, Vol.33 (21), p.3806-3811
Main Authors: Bothe, James V, Brown, Paul W
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Language:English
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description Lime additions to arsenic-containing wastes have been proven to be beneficial in reducing the mobility of dissolved arsenic, presumably through the formation of low-solubility calcium arsenates. However, the role of calcium arsenate formation in reducing the concentrations of dissolved arsenic has not been well established. Therefore, slurries with varying Ca/As ratios were equilibrated, and the compounds that formed at elevated pH values were established. In contrast to the literature, Ca3(AsO4)2 was not observed, rather Ca4(OH)2(AsO4)2·4H2O, Ca5(AsO4)3OH (arsenate apatite), and Ca3(AsO4)2·32/3H2O had formed. The equilibrium concentrations of arsenic were found to be the lowest at high pH. Minimum arsenic concentrations in equilibrium with Ca4(OH)2(AsO4)2·4H2O and Ca5(AsO4)3OH were 0.01 and 0.5 mg/L, respectively. Because arsenate apatite is stable to near-neutral pH values, the extent of its solid solubility with Ca5(PO4)3OH was determined. This was done to assess the effects of phosphate ion on the possible release of arsenate ion. Although equilibrium arsenate ion concentrations increased with decreasing pH, solid solution formation did not occur under ambient conditions. Rather, the arsenate apatite formed at the expense of Ca5(PO4)3OH.
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Sci. Technol</addtitle><description>Lime additions to arsenic-containing wastes have been proven to be beneficial in reducing the mobility of dissolved arsenic, presumably through the formation of low-solubility calcium arsenates. However, the role of calcium arsenate formation in reducing the concentrations of dissolved arsenic has not been well established. Therefore, slurries with varying Ca/As ratios were equilibrated, and the compounds that formed at elevated pH values were established. In contrast to the literature, Ca3(AsO4)2 was not observed, rather Ca4(OH)2(AsO4)2·4H2O, Ca5(AsO4)3OH (arsenate apatite), and Ca3(AsO4)2·32/3H2O had formed. The equilibrium concentrations of arsenic were found to be the lowest at high pH. Minimum arsenic concentrations in equilibrium with Ca4(OH)2(AsO4)2·4H2O and Ca5(AsO4)3OH were 0.01 and 0.5 mg/L, respectively. Because arsenate apatite is stable to near-neutral pH values, the extent of its solid solubility with Ca5(PO4)3OH was determined. 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Minimum arsenic concentrations in equilibrium with Ca4(OH)2(AsO4)2·4H2O and Ca5(AsO4)3OH were 0.01 and 0.5 mg/L, respectively. Because arsenate apatite is stable to near-neutral pH values, the extent of its solid solubility with Ca5(PO4)3OH was determined. This was done to assess the effects of phosphate ion on the possible release of arsenate ion. Although equilibrium arsenate ion concentrations increased with decreasing pH, solid solution formation did not occur under ambient conditions. Rather, the arsenate apatite formed at the expense of Ca5(PO4)3OH.</abstract><cop>Washington, DC</cop><pub>American Chemical Society</pub><doi>10.1021/es980998m</doi><tpages>6</tpages></addata></record>
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source American Chemical Society:Jisc Collections:American Chemical Society Read & Publish Agreement 2022-2024 (Reading list)
subjects Applied sciences
ARSENATES
ARSENIC
Calcium
calcium arsenate
CALCIUM OXIDES
ENERGY CONSERVATION, CONSUMPTION, AND UTILIZATION
Environment
Exact sciences and technology
INDUSTRIAL WASTES
Other industrial wastes. Sewage sludge
Pollution
SOLIDIFICATION
Studies
Waste materials
WASTE PROCESSING
WASTE WATER
Wastes
title Arsenic Immobilization by Calcium Arsenate Formation
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