Response of soil bacteria to PUREX chemicals suggests biomarker utility and bioremediation potential

Abstract

Chemicals involved in plutonium uranium reduction extraction (PUREX) have the potential to be released from nuclear reprocessing facilities and accumulate in the environment. In order to understand how soil microbial communities respond to contamination by PUREX chemicals, we carried out a series of microcosm experiments, exposing chemically diverse soils to a range of concentrations of key chemicals used in the PUREX process. We tested 4 PUREX chemicals, and 5 soil types using 16S rRNA amplicon sequencing, determining that responses of microbial communities are dependent on the soil type in which they reside, and that tributyl phosphate exposure appears to generate the most reproducible and detectable shifts in microbial communities. We identified a number of key taxa that are consistently enriched in soils exposed to tributyl phosphate. These key taxa are either in the family Rhizobiaceae or genus Pseudomonas. The relative abundance of these key taxa is concentration dependent, and their abundance remains elevated at least 100 days post initial exposure. Using whole-shotgun metagenomic sequencing, we reconstructed the genomes of these key taxa and find a number of putative phosphotriesterase genes found only in Rhizobiaceae. We find the abundance of phosphotriesterase genes is significantly higher in samples exposed to tributyl phosphate. These phosphotriesterase genes, which degrade tributyl phosphate into dibutyl phosphate and butanol, may serve as effective biomarkers for tributyl phosphate contaminated soil, as well as a method for future bioremediation.Importance: Nuclear materials reprocessing facilities have the capacity to release toxic chemicals during normal operations or accidents. This study examines the ways in which chemicals involved with nuclear materials reprocessing impact microorganisms in the soil. Our intention was to understand the consequences of the release of these chemicals on ecosystems that may surround these reprocessing facilities. We find soil microbial communities change in response to some chemicals but not others, and that tributyl phosphate appears to generate the most reproducible and detectable shifts in microbial communities. Microorganisms in the family Rhizobiaceae increase in abundance in response to the addition of tributyl phosphate, and an examination of the genomes of these microbes suggest they may be able to break down tributyl phosphate to access the phosphosphate present in this chemical. Overall, this work demonstrates that changes in soil microbial communities in response to contamination with chemicals from nuclear materials reprocessing facilities may be predictable, and these responses could be leveraged to remediate contamination.