Metagenomic analyses of aerobic bacterial enrichment cultures that degraded Tris(2-chloroethyl) phosphate (TCEP) and its transformation products

• Published in: Environmental pollution (1987) Vol. 361; p. 124825
• Main Authors: Yang, Tianyue, Zhou, Xiangyu, Wu, Yiding, Liang, Yi, Zeng, Xiangying, Yu, Zhiqiang
• Format: Journal Article
• Language: English
• Published: England Elsevier Ltd 15.11.2024
• Subjects: Burkholderiales; Rhizobiales; Sphingomonadales; Tris(2-chloroethyl) phosphate; Sphingomonadales; Rhizobiales; Burkholderiales; Tris(2-chloroethyl) phosphate
• ISSN: 0269-7491; 1873-6424; 1873-6424
• DOI: 10.1016/j.envpol.2024.124825

Tris(2-chloroethyl) phosphate (TCEP) is of growing public concern worldwide because of its ubiquitous contamination, toxicity, and persistence. In this study, we investigated bacterial communities in aerobic enrichment cultures with TCEP and its two major transformation products bis(2-chloroethyl) phosphate (BCEP) and 2-chloroethanol (2-CE) as the sole carbon source. Burkholderiales and Rhizobiales were likely two main bacterial guilds involved in the hydrolysis of TCEP, while Rhizobiales and Sphingomonadales may play an important role in the hydrolysis of BCEP, given the increase of Rhizobiales and Sphingomonadales-related phosphoesterase genes when the carbon source was switched from TCEP to BCEP. All Burkholderiales, Rhizobiales, Sphingomonadales were probably efficient in 2-CE metabolism, because their dehydrogenase genes and dehalogenase genes increased after 2-CE enrichment. The different substrate preference of different bacterial guilds highlighted the importance to understand the diversity and collaboration among functional bacteria. Meanwhile, two TCEP-degrading strains affiliated with Xanthobacter and Ancylobacter were isolated. Xanthobacter sp. strain T2-1 was able to degrade both TCEP and BCEP following the pseudo-first-order kinetics with reaction rates of 1.66 h−1 for TCEP and 1.02 h−1 for BCEP, respectively. Ancylobacter sp. strain T3-4 could degrade TCEP following the pseudo-first-order kinetics with a reaction rate of 2.54 h−1, but is unable to degrade BCEP. Additionally, strains that were phylogenetically closely related were found to have different degradation capabilities toward TCEP and/or BCEP, indicating the importance to investigate functional genes such as phosphoesterase genes. [Display omitted] •Different bacteria played specific roles during different TCEP degradation steps.•Burkholderiales and Rhizobiales were two main degraders during TCEP hydrolysis.•Rhizobiales and Sphingomonadales were important during BCEP hydrolysis.•Phylogenetically similar Isolates showed strain-specific degradation capability.