Molecular comparison of organic matter removal from shale gas flowback wastewater: Ozonation versus Fenton process

Xinglong Chen; Guonan Zhao; Zhuowen Yang; Qibin Li

doi:10.1016/j.scitotenv.2023.167147

Molecular comparison of organic matter removal from shale gas flowback wastewater: Ozonation versus Fenton process

Sci Total Environ. 2023 Dec 20:905:167147. doi: 10.1016/j.scitotenv.2023.167147. Epub 2023 Sep 18.

Authors

Xinglong Chen¹, Guonan Zhao¹, Zhuowen Yang¹, Qibin Li²

Affiliations

¹ Faculty of Geosciences and Environmental Engineering, Southwest Jiaotong University, 611756, China.
² Faculty of Geosciences and Environmental Engineering, Southwest Jiaotong University, 611756, China. Electronic address: liqb@home.swjtu.edu.cn.

PMID: 37730067
DOI: 10.1016/j.scitotenv.2023.167147

Abstract

Shale gas extraction process generates a large amount of shale gas flowback wastewater (SGFW) containing refractory organic compounds, which can pose serious environmental threats if not properly treated. However, the extremely complex compositions of organics in SGFW are still unknown and their transformation pathways in O₃- and ^•OH-dominated systems are not well recognized, which restrain the selection of treatment technology and optimization of operational parameters. The removal characteristics and reaction mechanism of dissolved organic matter (DOM) in SGFW treated by ozonation and Fenton processes were comparatively investigated using electrospray ionization Fourier transform ion cyclotron resonance mass spectrometry. The results showed that both processes could degrade low-oxygen highly unsaturated and phenolic organics, polyphenolics and polycyclic aromatics, and transform them into aliphatic organics and high-oxygen highly unsaturated and phenolic organics. With increasing action of reactive oxygen species (O₃ for ozonation and ^•OH for Fenton process), the degradation products (mainly aliphatic organics) increased during ozonation. However, in Fenton process, a wider range of DOM was removed without aliphatic organics accumulation. The degradation mechanisms of DOM during ozonation and Fenton processes included oxygen addition reactions (+3O, +H₂O₂, and +2O) as dominant pathways. However, ozonation showed more violent oxygenation, hydroxylation, and carboxylation, while Fenton process presented more violent chain-breaking reactions. These results revealed the selective oxidation of ozone and nonselective oxidation of ^•OH during SGFW treatment, and provided theoretical support for selecting SGFW treatment approaches.

Keywords: Dissolved organic matter; Fenton; Ozone; Shale gas flowback wastewater.