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Secondary plastic nanoparticle transport and retention in sand and soil

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When plastic breaks down in the environment, the resulting nanoparticles move through soil and sand differently depending on what type of plastic they came from and how weathered they are, meaning some tiny plastic bits could travel further and potentially reach groundwater more easily than others. This matters because most lab studies use simple plastic beads that don't behave like real-world weathered plastic, so this research suggests we may be underestimating how varied and unpredictable plastic contamination in our water and soil actually is.

Secondary plastic nanoparticles (Sec-PNPs), produced by plastic weathering, are contaminants of emerging concern with poorly understood behavior. Most current understanding of Sec-PNP transport is based mainly on studies of primary PNPs, particularly polystyrene (PS) nanobeads, which differ significantly from environmentally relevant Sec-PNPs. This study addresses this gap by conducting column experiments to benchmark the transport characteristics of various Sec-PNP types, including PS, low-density polyethylene (LDPE), high-density polyethylene (HDPE), polyethylene terephthalate (PET), and environmentally aged landfill-derived PNPs. Column experiments in sand and soil show plastic- and medium-dependent behaviors, as evidenced by breakthrough curves and particle-size data. Aliphatic Sec-PNPs exhibit higher retention than aromatic Sec-PNPs due to hydrophobic interactions, with larger particles enriched in eluted fractions, indicating aggregation or retention of smaller sizes. Despite chemical similarities, Sec-HDPE and Sec-LDPE display different elution patterns, while Sec-PET shows increased aggregation from π-conjugation. Landfill Sec-PNPs exhibit greater retention from inorganic impurities, promoting aggregation. Retention is consistent in all porous media for Sec-HDPE, except in fine sand, where pore constraints cause bimodal elution, and in soil, where matrix interactions delay breakthrough. These results demonstrate that Sec-PNP mobility is governed by the combined effects of polymer structure, particle aggregation, porous-medium characteristics, and contaminant interactions. The findings also highlight the limitations of using primary PS nanobeads as proxies for environmental PNPs and provide a framework for studying Sec-PNP transport under environmentally relevant conditions.

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