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Physicochemical changes in microplastics and formation of DBPs under ozonation

Chemosphere 2023 14 citations ? Citation count from OpenAlex, updated daily. May differ slightly from the publisher's own count. Score: 50 ? 0–100 AI score estimating relevance to the microplastics field. Papers below 30 are filtered from public browse.
Manhong Miao, Manhong Miao, Manhong Miao, Bingqing Yu, Manhong Miao, Tianwei Hao, Tianwei Hao, Tianwei Hao, Bingqing Yu, Yao Li, Min Zhang Min Zhang Min Zhang Min Zhang Tong Wang, Manhong Miao, Manhong Miao, Bingqing Yu, Min Zhang Manhong Miao, Bingqing Yu, Yao Li, Min Zhang Manhong Miao, Min Zhang Min Zhang Bingqing Yu, Min Zhang Manhong Miao, Yao Li, Tong Wang, Bingqing Yu, Manhong Miao, Manhong Miao, Manhong Miao, Yao Li, Tong Wang, Yihang Xiao, Manhong Miao, Manhong Miao, Yao Li, Manhong Miao, Manhong Miao, Tianwei Hao, Min Zhang Min Zhang Min Zhang Min Zhang Tong Wang, Min Zhang Min Zhang Yao Li, Yao Li, Min Zhang Min Zhang Bingqing Yu, Tianwei Hao, Manhong Miao, Bingqing Yu, Yao Li, Min Zhang Yao Li, Yao Li, Yao Li, Min Zhang Min Zhang Min Zhang Min Zhang Min Zhang Yao Li, Yao Li, Yao Li, Yao Li, Xiaoyu Ning, Yao Li, Xiaoyu Ning, Yao Li, Xiaoyu Ning, Yao Li, Xiaoyu Ning, Xiaoyu Ning, Xiaoyu Ning, Min Zhang

Summary

Researchers examined physicochemical changes in thermoplastic polyurethane and polyethylene microplastics during ozonation water treatment, finding that the process can alter microplastic morphology and potentially generate disinfection byproducts.

Polymers
Study Type Environmental

Microplastics (MPs) are substances that pose a risk to both human life and the environment. Their types and production are increasing year on year, and their potential to cause environmental pollution is a worldwide concern. Conventional water treatment processes, particularly coagulation and sedimentation, are not effective at removing all MPs. It is therefore important to assess the morphological changes in the MPs, i.e., the thermoplastic polyurethane (TPU) and polyethylene (PE), during ozonation and the dissolved organic carbon leaching as well as chloroform formation in the subsequent chlorination. The results show that the appearance and surface chemistry of the MPs changed during the ozonation process, most notably for TPU. The trichloromethane (CHCl) generation during chlorination was 0.168 and 0.152 μmol/L for TPU and PE, respectively, and the ozone pretreatment significantly increased the CHCl yield of TPU, while it had a weak effect on PE. Additional disinfection byproducts (DBPs), including CHClBr, CHClBr, and CHBr, were produced in the presence of bromide ions in the water column, and the total amount of DBPs produced by PE, PE-O, TPU, and TPU-O was significantly increased to 0.787, 0.814, 0.931, and 1.391 μmol/L, respectively. The study provides useful information for the environmental risk assessment of two representative MPs, i.e., TPU and MPs, in disinfection procedures for drinking water.

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