Jia Yongfeng, Demopoulos George P
Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110016, China.
Water Res. 2008 Feb;42(3):661-8. doi: 10.1016/j.watres.2007.08.017. Epub 2007 Aug 25.
The removal and immobilization of arsenic from industrial mineral-processing effluents typically involves lime neutralization and coprecipitation of arsenate with ferric iron. Despite the wide practice and environmental importance of this technique, no laboratory study has focused on the roles of lime as base and third ions like Ca2+, Ni2+ and SO(2)4(-) on the kinetics of arsenic retention by the coprecipitates. In this work, coprecipitation was performed at 22 degrees C by fast (10 min) neutralization of industrially relevant concentrated arsenate-iron(III) (Fe/As=2, 4) acidic sulfate solutions to different pHs (4, 6, 8) in batch reactors, and the concentration of arsenic was monitored up to 1 year. The tests showed that maximum removal of arsenic was achieved upon neutralization to the target pH. Arsenic was found to be released back into solution from the precipitates upon continuing mild agitation at constant pH. Near-equilibrium was attained at different times depending on the applied pH: 10 days at pH 4, 6 months at pH 6 and 9 months at pH 8. An aging treatment at pH 4 significantly enhanced arsenic retention (arsenic release was reduced by at least 50%) after the system was finally stabilized at pH 8. The retention of arsenic at pH 8 was multifold improved (by a factor x 25) when lime was used instead of NaOH. Similarly, the retention of arsenic was enhanced by the presence of calcium and nickel ions in the starting solution. Finally, evidence of Ca(II)-Fe(III)-As(V) association was found, but not sulfate incorporation at pH 8.
从工业选矿废水中去除并固定砷通常涉及用石灰中和以及砷酸盐与铁离子的共沉淀。尽管该技术应用广泛且具有环境重要性,但尚无实验室研究关注石灰作为碱以及钙离子、镍离子和硫酸根离子等第三类离子对共沉淀物固定砷动力学的作用。在本研究中,通过在间歇式反应器中将工业相关的高浓度砷酸盐 - 铁(III)(铁/砷 = 2、4)酸性硫酸盐溶液在22℃下快速(10分钟)中和至不同pH值(4、6、8)进行共沉淀,并对砷浓度进行长达1年的监测。试验表明,中和至目标pH值时可实现砷的最大去除。发现在恒定pH值下持续温和搅拌时,砷会从沉淀物中重新释放回溶液中。根据所施加的pH值不同,在不同时间达到近平衡状态:pH值为4时10天,pH值为6时6个月,pH值为8时9个月。在系统最终稳定在pH值8后,在pH值4下进行老化处理可显著增强砷的固定(砷释放减少至少50%)。当使用石灰代替氢氧化钠时,在pH值8下砷的固定提高了数倍(提高了25倍)。同样,起始溶液中钙离子和镍离子的存在增强了砷 的固定。最后,发现了Ca(II) - Fe(III) - As(V)缔合的证据,但在pH值8时未发现硫酸根的掺入。