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Insights into How Degradable Microplastics Enhance Cu2+ Mobility in Soil Through Interfacial Interaction

Toxics 2025 1 citation ? Citation count from OpenAlex, updated daily. May differ slightly from the publisher's own count. Score: 43 ? 0–100 AI score estimating relevance to the microplastics field. Papers below 30 are filtered from public browse.
Hongjia Peng, Hongjia Peng, Hongjia Peng, Hongjia Peng, Hongjia Peng, Hongjia Peng, Bolun Yu, Haipu Li Haipu Li Bolun Yu, Zuhong Lin, Zuhong Lin, Zuhong Lin, Zuhong Lin, Zuhong Lin, Haipu Li Haipu Li Zuhong Lin, Haipu Li Bolun Yu, Bolun Yu, Haipu Li Zuhong Lin, Haipu Li Haipu Li Haipu Li Zuhong Lin, Haipu Li

Summary

Degradable microplastics were found to enhance the mobility of copper ions in soil through interfacial chemical interactions, potentially spreading heavy metal contamination beyond its original source. The study highlights an unexpected way that biodegradable plastics can worsen co-contaminant risks in polluted soils.

Polymers

The incomplete degradation of degradable plastics may pose potential ecological risks, as it can generate degradable microplastics (DMPs), especially when these DMPs coexist with heavy metals in soil. Taking petrochemical-based poly(butylene adipate-co-terephthalate) (PBAT) and bio-based polylactic acid (PLA) as representative DMPs, this study investigated how DMPs affect the adsorption-desorption behavior of Cu<sup>2+</sup> in soil and the underlying mechanisms via batch equilibrium experiments and characterization analyses. The experiments revealed that ion exchange (accounting for 33.6-34.3%), oxygen-containing functional group complexation, and electrostatic interactions were the primary adsorption driving forces, with chemical adsorption playing the main role. Compared to the soil, the PBAT and PLA had smaller specific surface areas and pore volumes, fewer oxygen-containing functional groups, and especially lacked O-metal functional groups. They can dilute soil, clog its pores, and cover its active sites. 1% DMPs significantly reduced the soil's equilibrium adsorption capacity (Q<sub>e</sub>) (3.7-4.7%) and increased equilibrium desorption capacity (Q<sub>De</sub>) (1.7-2.6%), thereby increasing the mobility and ecological risk of Cu<sup>2+</sup>. PBAT and PLA had no significant difference in effects on the adsorption, but their specific mechanisms were somewhat distinct. Faced with the prevalent, worsening coexistence of DMPs and heavy metals in soil, these findings contribute to the ecological risk assessment of DMPs.

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