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Article ? AI-assigned paper type based on the abstract. Classification may not be perfect — flag errors using the feedback button. Tier 2 ? Original research — experimental, observational, or case-control study. Direct primary evidence. Nanoplastics Sign in to save

Both nanoplastic and iron mineral types determine their heteroaggregation: Aggregation kinetics and interface process

Journal of Hazardous Materials 2024 22 citations ? Citation count from OpenAlex, updated daily. May differ slightly from the publisher's own count. Score: 55 ? 0–100 AI score estimating relevance to the microplastics field. Papers below 30 are filtered from public browse.
Zhenyu Wang Yu Kong, Yu Kong, Ning Liu, Xuesong Cao, Yu Kong, Yu Kong, Zhenyu Wang Xiaona Li, Xiaona Li, Xuesong Cao, Xuesong Cao, Xuesong Cao, Yu Kong, Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Xuesong Cao, Zhenyu Wang Xuesong Cao, Xuesong Cao, Zhenyu Wang Zhenyu Wang Zhenyu Wang Le Yue, Xuesong Cao, Le Yue, Le Yue, Ning Liu, Xuesong Cao, Xuesong Cao, Yu Kong, Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Le Yue, Ning Liu, Zhenyu Wang Xuesong Cao, Zhenyu Wang Le Yue, Xuesong Cao, Le Yue, Xiaona Li, Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Xiaona Li, Xiaona Li, Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Xuesong Cao, Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang Zhenyu Wang

Summary

Researchers measured how four types of nanoplastics aggregate with iron minerals and found that surface chemistry drives the outcome — with PMMA forming the strongest heteroaggregates and carboxyl-modified particles the weakest — and that electron transfer from nanoplastics to hematite partially reduces iron, with implications for aquatic iron cycling.

Nanoplastics (NPs) inevitably interact with iron minerals (IMs) after being released into aquatic environments, changing their transport and fate. In this study, batch heteroaggregation kinetics of four types of NPs, i.e., polymethyl methacrylate (PMMA), polystyrene (PS-Bare), amino-polystyrene (PS-NH), and carboxyl-polystyrene (PS-COOH), with two different IMs (hematite and magnetite) were conducted. We found that the heteroaggregation of NPs and IMs and the associated interfacial interaction mechanisms are both NPs-dependent and IMs-dependent. Specifically, the NPs had stronger heteroaggregation with hematite than magnetite; the heteroaggregation order of two IMs with NPs was PMMA > PS-NH > PS-Bare > PS-COOH. Moreover, hydrogen bond, complexation, hydrophobic, cation-π, and electrostatic interaction were involved in the interfacial reaction between NPs and hematite, and electrons were transferred from the NPs to the hematite, causing the reduction of Fe into Fe. Furthermore, we first revealed that both pre-homoaggregation of NPs and IMs could affect their subsequent heteroaggregation, and the homoaggregates of IMs could be interrupted by PMMA or PS-COOH NPs introduction. Therefore, the emerging NPs pollution is likely to generate an ecological effect in terms of elemental cycles such as iron cycle. This work provides new insights into assessing the environmental transfer and ecological effects of NPs in aquatic environments.

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