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Combined toxicity of organophosphate flame retardants and polyethylene microplastics on Eisenia fetida: Biochemical and molecular insights

Environmental Research 2025 1 citation ? Citation count from OpenAlex, updated daily. May differ slightly from the publisher's own count. Score: 53 ? 0–100 AI score estimating relevance to the microplastics field. Papers below 30 are filtered from public browse.
Qi Guo, Hua Shen, Yinchang Feng, Minghan Wang, Yuheng Li, Xinda Lin, Yuxuan Gao, Lili Ma, Xiansheng Liu

Summary

Researchers exposed earthworms to polyethylene microplastics, chlorinated flame retardants, and their combinations to assess combined toxicity effects. They found that the most toxic flame retardant (TDCPP) had its effects reduced when combined with microplastics, likely because the plastics absorbed the chemical and lowered its bioavailability. In contrast, microplastics enhanced the toxicity of another flame retardant (TCPP), demonstrating that microplastics can act as both carriers and modulators of co-contaminant toxicity in soil ecosystems.

Microplastics and organophosphate flame retardants (OPFRs), a subset of organophosphate esters (OPEs), are frequently co-detected in terrestrial ecosystems, raising concerns about their combined ecological risks. In this study, the epigeic earthworm Eisenia fetida was exposed to polyethylene microplastics (PEs) (0.5 g kg), three chlorinated OPFRs (TCEP (tris(2-chloroethyl) phosphate), TCPP (tris(1-chloro-2-propyl) phosphate), and TDCPP (tris(1,3-dichloro-2-propyl) phosphate), each at 0.002 g kg), and their binary mixtures for 7 and 28 days. A suite of physiological, biochemical, and molecular biomarkers, including enzyme activities (SOD, CAT, GST, AChE, ATPases), oxidative damage markers (MDA, 8-OHdG), and gene expressions (sod, hsp70, tctp), were evaluated to assess sublethal toxic responses. A time-dependent shift in the correlation between sod transcription and SOD enzyme activity was observed, indicating possible early-stage post-transcriptional regulation and later-stage transcriptional control. The results revealed compound-specific and time-dependent toxicities. TDCPP exhibited the highest individual toxicity, suppressing antioxidant enzymes and disrupting ion transport. Co-exposure with PEs attenuated TDCPP-induced effects, likely via reduced bioavailability. In contrast, PEs enhanced the toxicity of TCPP, especially in oxidative and genotoxic responses. TCEP induced moderate but delayed biochemical changes. This study underscores the dual role of PEs as both carriers and modulators of co-occurring pollutants, and highlights the need for mixture-based risk assessments in soil ecosystems.

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