Xue Xiang-Dong, Wang Xing-Yuan, Mei Yu-Chen, Zhuang Hai-Feng, Song Ya-Li, Fang Cheng-Ran
School of Civil Engineering and Architectural, Zhejiang University of Science and Technology, Hangzhou 310023, China.
Key Laboratory of Recycling and Eco-treatment of Waste Biomass of Zhejiang Province, Hangzhou 310023, China.
Huan Jing Ke Xue. 2020 Aug 8;41(8):3675-3683. doi: 10.13227/j.hjkx.202002196.
The interaction between microplastics, heavy metals, and antibiotics can lead to combined pollution, which could result in greater environmental damage. The pathway and mechanism of the interaction between microplastics, heavy metals, and antibiotics are the preconditions for evaluating the associated environmental risk; however, these are not well understood. As probe sorbates, the sorption behaviors of copper ions (Cu) and tetracycline (TC) on two microplastics [high density polyethylene (HPDE) and general-purpose polystyrene (GPPS)] in aqueous solution were investigated and the welding theory with relevant experimental results were discussed. The adsorption capacity of HDPE was greater than that of GPPS in a single Cu solution, whereas the reverse situation occurred in a single TC solution. Moreover, the adsorption capacity of the microplastics in a Cu-TC binary solution was larger than that in the single solutions. The pseudo-second-order kinetic models to describe the adsorption process were reasonable and the entire process could be divided into two phases:surface adsorption and internal diffusion. The Langmuir model provided a better fit of the data than did the Freundlich model. In the single solutions, the saturated adsorption amounts of Cu and TC were 0.178 μmol·g and 0.257 μmol·g, respectively, for GPPS, and 0.334 μmol·g and 0.194 μmol·g, respectively, for HDPE. In the binary solution, the corresponding numerical values were 0.529 μmol·g and 0.411 μmol·g, respectively, for GPPS and 0.471 μmol·g and 0.341 μmol·g, respectively, for HDPE. The variations in the surface morphological characteristics and chemical functional groups were the main reasons for the difference in the adsorption behavior of microplastics. The variation of the pH of the adsorption system could change the existing forms and surface electrical properties of microplastics and adsorbed objects, and subsequently affected the equilibrium adsorption capacity. When the ambient temperature was in the range of 15 to 35℃, increasing the temperature was unfavorable for the adsorption process. Cu and TC could produce a synergistic effect under the conditions of coexistence. The formation of complexes and bridging make Cu and TC more easily adsorbed by microplastics.
微塑料、重金属和抗生素之间的相互作用会导致复合污染,进而可能造成更大的环境破坏。微塑料、重金属和抗生素之间相互作用的途径和机制是评估相关环境风险的前提条件;然而,目前人们对此还了解不足。作为探针吸附质,研究了铜离子(Cu)和四环素(TC)在两种微塑料[高密度聚乙烯(HPDE)和通用聚苯乙烯(GPPS)]上在水溶液中的吸附行为,并结合相关实验结果讨论了吸附理论。在单一Cu溶液中,HDPE的吸附量大于GPPS;而在单一TC溶液中则出现相反的情况。此外,微塑料在Cu-TC二元溶液中的吸附量大于在单一溶液中的吸附量。描述吸附过程的准二级动力学模型合理,整个过程可分为两个阶段:表面吸附和内部扩散。Langmuir模型比Freundlich模型能更好地拟合数据。在单一溶液中,GPPS对Cu和TC的饱和吸附量分别为0.178 μmol·g和0.257 μmol·g,HDPE对Cu和TC的饱和吸附量分别为0.334 μmol·g和0.194 μmol·g。在二元溶液中,GPPS对应的数值分别为0.529 μmol·g和0.411 μmol·g,HDPE对应的数值分别为0.471 μmol·g和0.341 μmol·g。表面形态特征和化学官能团的变化是微塑料吸附行为存在差异的主要原因。吸附体系pH值的变化会改变微塑料和被吸附物的存在形式及表面电学性质,进而影响平衡吸附量。当环境温度在15至35℃范围内时,升高温度对吸附过程不利。Cu和TC在共存条件下会产生协同效应。配合物的形成和桥连作用使Cu和TC更易被微塑料吸附。