The adsorption and release mechanism of different aged microplastics toward Hg(II) via batch experiment and the deep learning method.

Journal: Chemosphere
PMID:

Abstract

Aged microplastics are ubiquitous in the aquatic environment, which inevitably accumulate metals, and then alter their migration. Whereas, the synergistic behavior and effect of microplastics and Hg(II) were rarely reported. In this context, the adsorptive behavior of Hg(II) by pristine/aged microplastics involving polystyrene, polyethylene, polylactic acid, and tire microplastics were investigated via kinetic (pseudo-first and second-order dynamics, the internal diffusion model), Langmuir, and Freundlich isothermal models; the adsorption and desorption behavior was also explored under different conditions. Microplastics aged by ozone exhibited a rougher surface attached with abundant oxygen-containing groups to enhance hydrophilicity and negative surface charge, those promoted adsorption capacity of 4-20 times increment compared with the pristine microplastics. The process (except for aged tire microplastics) was dominated by a monolayer chemical reaction, which was significantly impacted by pH, salinity, fulvic acid, and co-existing ions. Furthermore, the adsorbed Hg(II) could be effectively eluted in 0.04% HCl, simulated gastric liquids, and seawater with a maximum desorption amount of 23.26 mg/g. An artificial neural network model was used to predict the performance of microplastics in complex media and accurately capture the main influencing factors and their contributions. This finding revealed that aged microplastics had the affinity to trap Hg(II) from freshwater, whereafter it released the Hg(II) once transported into the acidic medium, the organism's gastrointestinal system, or the estuary area. These indicated that aged microplastics could be the sink or the source of Hg(II) depending on the surrounding environment, meaning that aged microplastics could be the vital carrier to Hg(II).

Authors

  • Lianghong Li
    School of Resources, Environment and Materials, Guangxi University, Nanning, China.
  • Bin Xue
    Department of Cell Biology, Microbiology and Molecular Biology, School of Natural Sciences and Mathematics, College of Arts and Sciences, University of South Florida, Tampa, FL 33620, USA. binxue@usf.edu.
  • Haiying Lin
    School of Resources, Environment and Materials, Guangxi University, Nanning, China; Guangxi Key Laboratory of Emerging Contaminants Monitoring, Early Warning and Environmental Health Risk Assessment, Guangxi University, Nanning, China. Electronic address: linhaiying@gxu.edu.cn.
  • Wenlu Lan
    Beibu Gulf Marine Ecological Environment Field Observation and Research Station of Guangxi, Beihai, Guangxi, China; Marine Environmental Monitoring Centre of Guangxi, Beihai, Guangxi, China. Electronic address: dr.lan@139.com.
  • Xinyi Wang
    School of Biological Sciences & Medical Engineering, Southeast University, Nanjing, China.
  • Junqi Wei
    School of Resources, Environment and Materials, Guangxi University, Nanning, China.
  • Mingen Li
    School of Resources, Environment and Materials, Guangxi University, Nanning, China.
  • Mingzhi Li
    School of Resources, Environment and Materials, Guangxi University, Nanning, China.
  • Yu Duan
    Yunnan Characteristic Plant Extraction Laboratory Co., Ltd., Key Laboratory of Medicinal Chemistry for Natural Resource, Ministry of Education and Yunnan Province, School of Chemical Science and Technology, Yunnan University, Kunming, 650500, China.
  • Jiatong Lv
    School of Resources, Environment and Materials, Guangxi University, Nanning, China.
  • Zixuan Chen
    School of Aerospace Engineering and Applied Mechanics, Tongji University, Shanghai 200092, China.