Avasarala Sumant, Orta John, Schaefer Michael, Abernathy Macon, Ying Samantha, Liu Haizhou
Department of Chemical and Environmental Engineering, University of California, Riverside, Riverside, CA 92521, USA.
Department of Environmental Sciences, University of California, Riverside, Riverside, CA 92521, USA.
Environ Sci (Camb). 2021 Feb 1;7(2):357-366. doi: 10.1039/d0ew00706d. Epub 2020 Dec 15.
This study investigated the reaction kinetics on the oxidative transformation of lead(ii) minerals by free chlorine (HOCl) and free bromine (HOBr) in drinking water distribution systems. According to chemical equilibrium predictions, lead(ii) carbonate minerals, cerussite PbCO and hydrocerussite Pb(CO)(OH), and lead(ii) phosphate mineral, chloropyromorphite Pb(PO)Cl are formed in drinking water distribution systems in the absence and presence of phosphate, respectively. X-ray absorption near edge spectroscopy (XANES) data showed that at pH 7 and a 10 mM alkalinity, the majority of cerussite and hydrocerussite was oxidized to lead(iv) mineral PbO within 120 minutes of reaction with chlorine (3 : 1 Cl : Pb(ii) molar ratio). In contrast, very little oxidation of chloropyromorphite occurred. Under similar conditions, oxidation of lead(ii) carbonate and phosphate minerals by HOBr exhibited a reaction kinetics that was orders of magnitude faster than by HOCl. Their end oxidation products were identified as mainly plattnerite β-PbO and trace amounts of scrutinyite α-PbO based on X-ray diffraction (XRD) and extended X-ray absorption fine structure (EXAFS) spectroscopic analysis. A kinetic model was established based on the solid-phase experimental data. The model predicted that in real drinking water distribution systems, it takes 0.6-1.2 years to completely oxidize Pb(ii) minerals in the surface layer of corrosion scales to PbO by HOCl without phosphate, but only 0.1-0.2 years in the presence of bromide (Br) due the catalytic effects of HOBr generation. The model also predicts that the addition of phosphate will significantly inhibit Pb(ii) mineral oxidation by HOCl, but only be modestly effective in the presence of Br. This study provides insightful understanding on the effect of residual disinfectant on the oxidation of lead corrosion scales and strategies to prevent lead release from drinking water distribution systems.
本研究调查了饮用水分配系统中游离氯(HOCl)和游离溴(HOBr)对铅(II)矿物氧化转化的反应动力学。根据化学平衡预测,在不存在和存在磷酸盐的情况下,饮用水分配系统中分别形成碳酸铅(II)矿物白铅矿PbCO₃和羟氯铅矿Pb₃(CO₃)₂(OH)₂,以及磷酸铅(II)矿物氯磷灰石Pb₅(PO₄)₃Cl。X射线吸收近边光谱(XANES)数据表明,在pH值为7且碱度为10 mM的条件下,在与氯(Cl与Pb(II)的摩尔比为3:1)反应120分钟内,大部分白铅矿和羟氯铅矿被氧化为四价铅矿物PbO₂。相比之下,氯磷灰石的氧化很少发生。在类似条件下,HOBr对碳酸铅(II)和磷酸矿物的氧化反应动力学比HOCl快几个数量级。根据X射线衍射(XRD)和扩展X射线吸收精细结构(EXAFS)光谱分析,它们的最终氧化产物主要被鉴定为块黑铅矿β-PbO₂和痕量的板铅矿α-PbO。基于固相实验数据建立了动力学模型。该模型预测,在实际饮用水分配系统中,在没有磷酸盐的情况下,HOCl将腐蚀垢表层中的Pb(II)矿物完全氧化为PbO₂需要0.6 - 1.2年,但由于HOBr生成的催化作用,在存在溴化物(Br⁻)的情况下只需0.1 - 0.2年。该模型还预测,添加磷酸盐将显著抑制HOCl对Pb(II)矿物的氧化,但在存在Br⁻的情况下效果有限。本研究为残留消毒剂对铅腐蚀垢氧化的影响以及防止饮用水分配系统中铅释放的策略提供了深刻的理解。