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Rapid Generation of Microplastics and Plastic-Derived Dissolved Organic Matter from Food Packaging Films under Simulated Aging Conditions
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    Rapid Generation of Microplastics and Plastic-Derived Dissolved Organic Matter from Food Packaging Films under Simulated Aging Conditions
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    Environmental Science & Technology

    Cite this: Environ. Sci. Technol. 2024, 58, 45, 20147–20159
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    https://doi.org/10.1021/acs.est.4c05504
    Published October 28, 2024
    Copyright © 2024 American Chemical Society

    Abstract

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    In this study, we show that low-density polyethylene films, a prevalent choice for food packaging in everyday life, generated high numbers of microplastics (MPs) and hundreds to thousands of plastic-derived dissolved organic matter (DOM) substances under simulated food preparation and storage conditions. Specifically, the plastic film generated 66–2034 MPs/cm2 (size range 10–5000 μm) under simulated aging conditions involving microwave irradiation, heating, steaming, UV irradiation, refrigeration, freezing, and freeze–thaw cycling alongside contact with water, which were 15–453 times that of the control (plastic film immersed in water without aging). We also noticed a substantial release of plastic-derived DOM. Using ultrahigh-resolution mass spectrometry, we identified 321–1414 analytes with molecular weights ranging from 200 to 800 Da, representing plastic-derived DOM containing C, H, and O. The DOM substances included both degradation products of polyethylene (including oxidized forms of oligomers) and toxic plastic additives. Interestingly, although no apparent oxidation was observed for the plastic film under aging conditions, plastic-derived DOM was more oxidized (average O/C increased by 27–46%) following aging with a higher state of carbon saturation and higher polarity. These findings highlight the future need to assess risks associated with MP and DOM release from plastic wraps.

    Copyright © 2024 American Chemical Society

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    Supporting Information

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    The Supporting Information is available free of charge at https://pubs.acs.org/doi/10.1021/acs.est.4c05504.

    • Text S1, conditional fragmentation modeling of the size distribution of MPs; Text S2, MP generation kinetics modeling; Text S3, literature search methodology; Text S4, 2D-COS analysis; Text S5, meanings of key parameters from GPC analysis; Text S6, detailed information on FT-ICR-MS data interpretation; Text S7, quality control measures and statistical analyses; Tables S1 and S2, conditional fragmentation modeling parameters and exponential modeling parameters for different aging treatments; Table S3, calculated fragmentation dimension values; Table S4, MP counting results in procedural blank samples; Table S5, analyte characteristics of shared 40 DOM substances for all groups; Tables S6–S13, analyte characteristics of the most abundant DOM substances following different aging processes; Table S14, summary of the DOM characteristics determined by FT-ICR-MS; Figure S1, conditional fragmentation modeling of the size distribution of MP generated following different aging processes; Figure S2, flow diagram reporting the number of retrieved studies; Figure S3, effect of air-drying on MP quantification; Figure S4, MP generation from large pieces of food wrap as compared with cut pieces; Figure S5, MP generation from food wrap in contact with different liquids; Figure S6, exponential fitting of MP generation characteristics; Figure S7, morphologies of the aged food wrap and the generated MP; Figure S8, FTIR spectra of the remaining plastic film following different aging treatments; Figure S9, 2D-COS maps showing the changes in surface functionality of the remaining plastic film; Figure S10, Raman spectra of the remaining plastic film following different aging treatments; Figure S11, XPS survey spectra of the remaining plastic film following different aging treatments; Figure S12, XPS C 1s spectra of the pristine and aged plastic film following microwave irradiation, heating, and steaming; Figure S13, XPS C 1s spectra of the aged plastic film following UV irradiation, refrigeration, freezing, and freeze–thaw cycling; Figure S14, correlation of DOC content with the number of FT-ICR-MS identified analytes; and Figure S15, Venn diagram showing the number of shared and unique analytes determined by FT-ICR-MS (PDF)

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    This article is cited by 5 publications.

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    Environmental Science & Technology

    Cite this: Environ. Sci. Technol. 2024, 58, 45, 20147–20159
    Click to copy citationCitation copied!
    https://doi.org/10.1021/acs.est.4c05504
    Published October 28, 2024
    Copyright © 2024 American Chemical Society

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