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Characteristics and mechanisms of dissolved organic matter leached by photodegradation of polyethylene microplastics: role of adsorbed antibiotics
Summary
Researchers investigated how UV-driven photoaging of polyethylene microplastics and their interactions with the antibiotic ofloxacin affect the release of dissolved organic matter in water. They found that UV exposure significantly increased DOM release from pristine microplastics, while antibiotic-adsorbed microplastics initially released different molecular weight compounds before converging to similar patterns. The study reveals that aging microplastics and their co-contaminants create complex secondary pollution dynamics in aquatic environments.
The photoaging of polyethylene microplastics (PE MPs) and their interactions with co-contaminants such as ofloxacin (OFL) play a critical role in shaping the composition and characteristics of dissolved organic matter (DOM) in aquatic environments. This study systematically investigates the characteristics and leaching mechanisms of DOM from pristine PE and PE-adsorbed OFL (PE-OFL) under prolonged ultraviolet irradiation. Molecular weight (MW) fractionation revealed that UV exposure significantly enhanced DOM release from pristine PE, with low-MW fractions (<1k Da) dominating (75.6-98.3% of total DOM). In contrast, PE-OFL initially released high-MW compounds (44.9-51.8% > 1k Da), which transitioned to low-MW dominance. Two-dimensional correlation spectroscopy of FTIR spectra indicated that photolytic degradation of pristine PE primarily involved -CH2 groups, while C-O groups were dominant in PE-OFL, reflecting OFL-induced alterations in photolytic pathways. Energy-dispersive X-ray spectroscopy and X-ray photoelectron spectroscopy demonstrated that OFL adsorption substantially increased surface oxidation, with a 2.4-fold elevation in O/C ratios and enhanced carboxylation (77.5% CO content vs. 32.8% in PE). These findings elucidate that OFL acts as both a photosensitizer and an electron shuttle, accelerating PE backbone scission via reactive oxygen species generation while temporarily stabilizing high-MW intermediates. Overall, the findings highlights that contaminant-laden MPs exhibit distinct DOM profiles compared to pristine MPs, emphasizing the necessity of considering co-pollutant interactions in environmental risk assessments.