16Bacterial genetic material can be horizontally transferred between microorganisms 17 via outer membrane vesicles (OMVs) released by bacteria. Up to now, the application of 18 vesicle-mediated horizontal transfer of "degrading genes" in environmental remediation 19 has not been reported. In this study, the nirS gene from an aerobic denitrification 20 bacterium, Pseudomonas stutzeri, was enclosed in a pET28a plasmid, transformed into 21 Escherichia coli (E. coli) DH5α and expressed in E. coli BL21. The E. coli DH5α 22 released OMVs containing the recombination plasmid pET28a-nirS. Moreover, the 23 amount of released OMVs-protein and DNA in OMVs increase as heavy metal 24 concentrations and temperature increased. When compared with the free pET28a-nirS 25 plasmid's inability to transform, nirS in OMVs could be transferred into E. coli BL21 26 with the transformation frequency of 2.76Ă10 6 CFU/g when the dosage of OMVs was 27 200 ”g under natural conditions, and nirS could express successfully in recipient bacteria. 28 Furthermore, the recipient bacteria that received OMVs could produce 18.16 U ml -1 29 activity of nitrite reductase. Vesicle-mediated HGT of aerobic denitrification genes 30 provides a novel bioaugmentation technology of nitrogen removal. 31 32 Importance 33Previous studies have reported that bacterial genetic material can be horizontally 34 transferred between microorganisms via outer membrane vesicles(OMVs) released by 35 bacteria. However, the application of vesicle-mediated horizontal transfer of "degrading 36 genes" in environmental remediation has not been reported. In this study, we found that 37 OMVs could mediate horizontal transfer of pET28a-nirS plasmid between E. coli under 38 3 natural condition. The transformation frequency reached to 2.76Ă10 6 , which was higher 39 than that of the free plasmid. Vesicle-mediated HGT of aerobic denitrification genes 40 provides a novel bioaugmentation technology of nitrogen removal. 41 42 44 45 4 Introduction 46High nitrogen concentrations in water result in water eutrophication and pollution.
47Traditional bio-treatment processes for nitrogen removal involve autotrophic and 48 heterotrophic denitrification under aerobic and anoxic conditions, respectively (1).
49Because of their different oxygen requirements, these two steps are separated spatially 50 and temporally. Recently, more researchers have focused on nitrogen removal using 51 aerobic denitrification bacteria. Unlike traditional anaerobic denitrification mechanisms, 52 aerobic denitrification occurs via co-respiration or co-metabolism of O 2 and NO 3 -.
53Additionally, nitrification and denitrification can occur in the same aerobic denitrification 54 system (2, 3). Nitrate reductase (napA), nitrite reductase (nirS), nitric oxide reductase 55 (norB) and nitrous oxide reductase (nosZ) are four key enzymes in the aerobic 56 denitrification process of aerobic denitrifying bacteria. The aerobic denitrification 57 bacteria or microbial consortium can be added into wastewater for promoting the remo...