Microbial potential to mitigate neurotoxic methylmercury accumulation in farmlands and rice.

Zhou, Xin-Quan; Chen, Kang-Hua; Yu, Ri-Qing; Yang, Man; Liu, Qin; Hao, Yun-Yun; Li, Jibing; Liu, Hui-Wen et al. · Nat Commun · 2025

basic_science · Level V

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Abstract

Toxic methylmercury (CH<sub>3</sub>Hg<sup>+</sup>) is produced by microbial conversion of inorganic mercury in hypoxic environments such as rice paddy soils, and can accumulate in rice grains. Although microbial demethylation has been recognized as a crucial pathway for CH<sub>3</sub>Hg<sup>+</sup> degradation, the identities of microbes and pathways accountable for CH<sub>3</sub>Hg<sup>+</sup> degradation in soil remain elusive. Here, we combine <sup>13</sup>CH<sub>3</sub>Hg<sup>+</sup>-DNA stable-isotope probing experiments with shotgun metagenomics to explore microbial taxa and associated biochemical processes involved in CH<sub>3</sub>Hg<sup>+</sup> degradation in paddy and upland soils. We identify Pseudarthrobacter, Methylophilaceae (MM2), and Dechloromonas as the most significant taxa potentially engaged in the degradation of <sup>13</sup>CH<sub>3</sub>Hg<sup>+</sup> in paddy soil with high mercury contamination. We confirm that strains affiliated with two of those taxa (species Dechloromonas denitrificans and Methylovorus menthalis) can degrade CH<sub>3</sub>Hg<sup>+</sup> in pure culture assays. Metagenomic analysis further reveals that most of these candidate <sup>13</sup>CH<sub>3</sub>Hg<sup>+</sup> degraders carry genes associated with the Wood-Ljungdahl pathway, dicarboxylate-hydroxybutyrate cycle, methanogenesis, and denitrification, but apparently lack the merB and merA genes involved in CH<sub>3</sub>Hg<sup>+</sup> reductive demethylation. Finally, we estimate that microbial degradation of soil CH<sub>3</sub>Hg<sup>+</sup> contributes to 0.08-0.64 fold decreases in CH<sub>3</sub>Hg<sup>+</sup> accumulation in rice grains across China (hazard quotient (HQ) decrements of 0.62-13.75%). Thus, our results provide insights into microorganisms and pathways responsible for CH<sub>3</sub>Hg<sup>+</sup> degradation in soil, with potential implications for development of bioremediation strategies.

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