Fate of Bisphenol AF (BPAF) in Soil-Earthworm System: Dual Role of Bioaccumulation and Biotransformation

Bisphenol AF (BPAF) contamination in soil from plastic and rubber use is widespread, yet its bioaccumulation and biotransformation in terrestrial invertebrates and its effects on the fate of BPAF in soil remain unknown. Here, we used <sup>14</sup>C-radiotracer to study the accumulation, distribution, metabolism, and excretion of BPAF in the geophagous earthworm <i>Metaphire guillelmi</i>. Earthworms significantly promoted the formation of nonextractable BPAF residues in soil, accelerating BPAF dissipation. After 21 days of exposure, bioaccumulation of total BPAF-derived residues was 6.3-fold higher than that of extractable parent BPAF in earthworms, primarily located in the gut (73.6%), followed by skin (14.7%), body fluid (7.0%), and organs (4.7%), with 47.4% overall existing as tissue-bound residues (TBRs). TBRs showed limited elimination from earthworms but might release BPAF and its transformation products (TPs), predominantly BPAF, into the soil upon earthworm death, increasing BPAF persistence. The dominant TP in earthworms was the monosulfate conjugate of BPAF, the first such conjugate reported in soil animals. Both the TBR formation and excretion of BPAF monosulfate could contribute to the detoxification of BPAF in <i>M. guillelmi</i>. The results underscore a dual role of earthworms in the fate of BPAF in soil (accelerating dissipation vs. increasing persistence) and highlight risks associated with BPAF conjugation and TBR formation.

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Journal
Environmental Science & Technology
Published
2025-12-02
DOI
https://doi.org/10.1021/acs.est.5c05982
Primary Topic
Effects and risks of endocrine disrupting chemicals
Type
article
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article

Fate of Bisphenol AF (BPAF) in Soil-Earthworm System: Dual Role of Bioaccumulation and Biotransformation

Yan He, Lianhong Wang, Xiaoran Guo, Rong Ji et al.
Environmental Science & Technology
Effects and risks of endocrine disrupting chemicals
article

Fate of Bisphenol AF (BPAF) in Soil-Earthworm System: Dual Role of Bioaccumulation and Biotransformation

Yan He, Lianhong Wang, Xiaoran Guo, Rong Ji, Bin Wang, Yongfeng Wang, Xuan Wu, Xiaoming Yun
article en

Abstract

Bisphenol AF (BPAF) contamination in soil from plastic and rubber use is widespread, yet its bioaccumulation and biotransformation in terrestrial invertebrates and its effects on the fate of BPAF in soil remain unknown. Here, we used <sup>14</sup>C-radiotracer to study the accumulation, distribution, metabolism, and excretion of BPAF in the geophagous earthworm <i>Metaphire guillelmi</i>. Earthworms significantly promoted the formation of nonextractable BPAF residues in soil, accelerating BPAF dissipation. After 21 days of exposure, bioaccumulation of total BPAF-derived residues was 6.3-fold higher than that of extractable parent BPAF in earthworms, primarily located in the gut (73.6%), followed by skin (14.7%), body fluid (7.0%), and organs (4.7%), with 47.4% overall existing as tissue-bound residues (TBRs). TBRs showed limited elimination from earthworms but might release BPAF and its transformation products (TPs), predominantly BPAF, into the soil upon earthworm death, increasing BPAF persistence. The dominant TP in earthworms was the monosulfate conjugate of BPAF, the first such conjugate reported in soil animals. Both the TBR formation and excretion of BPAF monosulfate could contribute to the detoxification of BPAF in <i>M. guillelmi</i>. The results underscore a dual role of earthworms in the fate of BPAF in soil (accelerating dissipation vs. increasing persistence) and highlight risks associated with BPAF conjugation and TBR formation.

Environmental Science & TechnologyVol. 59(49)
Quanzhou Normal University (CN), Chinese Academy of Sciences (CN), State Key Laboratory of Pollution Control and Resource Reuse (CN), Institute of Applied Ecology (CN), Institute of Environmental Protection (PL), Zhejiang University (CN), Nanjing University (CN)
Openalex Percentile: Top 53%
Effects and risks of endocrine disrupting chemicals
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