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Photochemical Oxidation of Polyethylene Terephthalate Microplastics Adsorbed on Sand and Silica Surfaces
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This study examined the photochemical oxidation of PET microplastics adsorbed on sand and silica surfaces under UV irradiation, focusing on the products released into water. Surface-bound PET underwent oxidative fragmentation, releasing soluble organic compounds, with implications for understanding the environmental chemistry of microplastic-contaminated sediments.
The environmental contamination by plastics, microplastics, and related compounds is a major concern. While the detection and release of micro- and nanoparticles from these materials have been widely studied, the formation and release of molecules resulting from their degradation in the environment have been overlooked. This work presents a study of the products released from poly(ethylene terephthalate) (PET) irradiated as pure particles and adsorbed on silica and sand surfaces under different irradiation conditions. The role of oxygen was also evaluated. The products were identified by gas chromatography-mass spectrometry (GC-MS) and liquid chromatography-high resolution mass spectrometry (LC-HRMS). The main released molecules can be accounted for by considering the cleavage of α- and β-bonds next to the ester moiety of the polymer chain. Volatile products such as benzene as well as monomer units of the polymer and related products were identified. In the presence of oxygen, acetic acid and products resulting from hydroxylation at the benzenic ring or at the ethyl moiety were detected. Adsorption on silica and sand has little effect on the photoproduct distributions. The irradiation at 360 nm leads to distributions similar to the ones observed at 257 nm, but the reaction rate is lower. The identified product ethylene terephthalate is a marker of PET plastics and particles and can therefore be used to evaluate the environmental contamination by this polymer material.
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Researchers investigated the photodegradation of polyethylene terephthalate plastics and found that UV-driven breakdown produces persistent low-molecular-weight compounds that accumulate in sediments, raising concerns about the long-term chemical legacy of PET waste in aquatic environments.
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