Institute of Groundwater and Earth Sciences, Jinan University, 510632, Guangzhou, China.
Institute of Groundwater and Earth Sciences, Jinan University, 510632, Guangzhou, China.
Ecotoxicol Environ Saf. 2019 Jul 30;176:270-278. doi: 10.1016/j.ecoenv.2019.03.106. Epub 2019 Apr 1.
This study examines the adsorption and desorption characteristics of heavy metals in road dust (RD) for the aspect of integrated stormwater management. The chemical fractionations of Cu, Zn, Ni, and Cd were determined by a three-step sequential extraction protocol. Pseudo-first-order and Pseudo-second-order kinetic models, along with Langmuir, Freundlich, and Temkin isotherms were adopted to simulate the batch experimental data. The proportional shift of metals' chemical fractionations in original RD, adsorption equilibrium, and desorption equilibrium were determined. Results show that RD has a remarkable affinity to adsorb heavy metal within a short time. The adsorption processes were well described by the Pseudo-second-order kinetic model (R = 0.98-0.99) and Freundlich isotherm (R = 0.89-0.98) for most of the given metals indicating that the chemical adsorption was probably the rate-controlling step and the binding energy for each site was not identical. The maximum adsorption capacities for Cu, Cd, Zn, and Ni were 6300 mg kg, 5800 mg kg, 4000 mg kg, and 3200 mg kg, respectively. A linear fit to the equilibrium pH and the total amounts of the adsorbed metals indicates a strong pH-dependent adsorption. According to the proportional shift of metals' chemical fractionations during the adsorption and desorption processes, the exchangeable fractions of heavy metals in RD were irreversible. It suggests that a portion of the surface sites of RD would be not exchangeable once it was occupied.
本研究从综合雨水管理的角度考察了道路灰尘(RD)中重金属的吸附和解吸特性。采用三步连续提取法测定 Cu、Zn、Ni 和 Cd 的化学形态。采用伪一阶和伪二阶动力学模型以及 Langmuir、Freundlich 和 Temkin 等温线对批实验数据进行模拟。确定了金属化学形态在原始 RD、吸附平衡和解吸平衡中的比例变化。结果表明,RD 在短时间内对重金属具有显著的吸附亲和力。吸附过程很好地符合伪二阶动力学模型(R = 0.98-0.99)和 Freundlich 等温线(R = 0.89-0.98),这表明化学吸附可能是速率控制步骤,并且每个位置的结合能并不相同。Cu、Cd、Zn 和 Ni 的最大吸附容量分别为 6300 mg kg、5800 mg kg、4000 mg kg 和 3200 mg kg。平衡 pH 值与吸附金属总量的线性拟合表明吸附强烈依赖 pH 值。根据吸附和解吸过程中重金属化学形态的比例变化,RD 中重金属的可交换分数是不可逆的。这表明一旦 RD 的表面位点被占据,其中一部分将不可交换。