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Continuous bioscorodite crystallization in CSTRs for arsenic removal and disposal

机译:CSTRs中连续的臭葱石结晶,用于砷的去除和处理

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In CSTRs, ferrous iron was biologically oxidized followed by crystallization of scorodite (FeAsO_4-2H_2O) at pH 1.2 and 72 ℃. The CSTRs were fed with 2.8 g L~(-1) arsenate and 2.4 g L~(-1) ferrous and operated at an HRT of 40 h, without seed addition or crystal recirculation. Both oxidation and crystallization were stable for periods up to 200 days. The arsenic removal efficiency was higher than 99% at feed Fe/As molar ratios between 1 and 2, resulting in effluents with 29 ± 18 mg As L~(-1). Arsenic removal decreased to 40% at feed Fe/As molar ratios between 2 and 5. Microorganisms were not affected by arsenic concentrations up to 2.8 g As~(5+) L~(-1). The bioscorodite solid yield was 3.2 g/g arsenic removed. Bioscorodite crystals precipitated as aggregates, causing scaling on the glass wall of the reactor. The observed morphology through SE microscopy of the precipitates appeared amorphous but XRD analysis confirmed that these were crystalline scorodite. Arsenic leaching of bioscorodite was 0.4 mg L~(-1) after 100 days under TCLP conditions, but when jarosite had been co-precipitated leaching was higher at 0.8 g L~(-1). The robustness of the continuous process, the high removal efficiency and the very low arsenic leaching rates from bioscorodite sludge make the process very suitable for arsenic removal and disposal.
机译:在CSTR中,亚铁被生物氧化,然后在pH 1.2和72℃下臭葱石(FeAsO_4-2H_2O)结晶。向CSTR注入2.8 g L〜(-1)砷酸盐和2.4 g L〜(-1)亚铁,并在40 h的HRT下运行,而无需添加晶种或进行晶体再循环。氧化和结晶均稳定长达200天。在进料Fe / As摩尔比为1至2时,砷的去除效率高于99%,导致废水中的L〜(-1)为29±18 mg。在进料Fe / As摩尔比为2至5时,砷的去除率降低至40%。微生物不受砷浓度高达2.8 g As〜(5+)L〜(-1)的影响。除去臭葱石的固体产量为3.2g / g。生物臭葱石晶体沉淀为聚集体,导致在反应器的玻璃壁上结垢。通过SE显微镜观察到的沉淀物形态看起来是无定形的,但XRD分析证实它们是结晶臭葱石。在TCLP条件下100天后,臭葱石的砷浸出为0.4 mg L〜(-1),而黄铁矿共沉淀时的浸出较高,为0.8 g L〜(-1)。连续过程的鲁棒性,高去除效率和从生物臭葱石污泥中砷的极低浸出率使该方法非常适合砷的去除和处理。

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