The Key Laboratory of Water and Sediment Sciences, Ministry of Education, School of Environment, Beijing Normal University, Beijing 100875, China.
J Environ Sci (China). 2013 May 1;25(5):986-92. doi: 10.1016/s1001-0742(12)60113-2.
As safe byproducts of drinking water treatment processes, ferric and alum water treatment residuals (FARs) have the potential to be new phosphate (P) immobilization materials. In this study, batch experiments were conducted to investigate and compare the adsorption characteristics of three P species by FARs. The results showed that the kinetic processes of different P species' adsorption by FARs could be described by a pseudo second-order model. The ranking list of the initial adsorption rates with respect to different phosphates was pyrophosphate, phytate, orthophosphate, hexametaphosphate and glycerophosphate. Of the six models considered, the two-site Langmuir model most effectively described the adsorption characteristics of the various P species. Upon fitting the results, the maximum adsorption capacities were determined to be 40.24 mg/g for phytate, 18.04 mg/g for pyrophosphate, 17.14 mg/g for orthophosphate, 15.86 mg/g for hexametaphosphate and 10.81 mg/g for glycerophosphate. In addition, the adsorption processes of the different P species were spontaneous endothermic processes and were favored at lower pH values. The pH dependency was found to be especially true for orthophosphate, where the adsorption capacity decreased by 1.22 mg/g with an increase in pH from 5 to 9. Fractionation of the adsorbed P species from the FARs demonstrated that Al-P and Fe-P were the dominating forms, constituting approximately 80%-90% of the total P fractions, which indicated that the adsorbed P species had a low leaching risk and could stably exist in the FARs. Therefore, the FARs could be effective in controlling pollution in water caused by different P species.
作为饮用水处理过程中的安全副产物,铁和铝水处理残余物(FARs)有可能成为新的磷酸盐(P)固定材料。本研究通过批量实验考察并比较了 FARs 对三种 P 形态的吸附特性。结果表明,不同 P 形态在 FARs 上的吸附动力学过程可用拟二级模型描述。不同磷酸盐的初始吸附速率的排序为焦磷酸盐、植酸盐、正磷酸盐、六偏磷酸盐和甘油磷酸。在所考虑的六个模型中,双位点 Langmuir 模型最有效地描述了各种 P 形态的吸附特征。拟合结果确定了各 P 形态的最大吸附容量分别为:植酸盐 40.24mg/g、焦磷酸盐 18.04mg/g、正磷酸盐 17.14mg/g、六偏磷酸盐 15.86mg/g、甘油磷酸 10.81mg/g。此外,不同 P 形态的吸附过程是自发的吸热过程,在较低的 pH 值下更有利。发现 pH 值依赖性尤其适用于正磷酸盐,当 pH 值从 5 增加到 9 时,吸附容量降低了 1.22mg/g。从 FARs 中吸附的 P 形态的分馏表明,Al-P 和 Fe-P 是主要形态,占总 P 形态的 80%-90%,这表明吸附的 P 形态具有较低的浸出风险,可以在 FARs 中稳定存在。因此,FARs 可以有效地控制不同 P 形态引起的水污染。