Chen Xinglong, Zhao Guonan, Yang Zhuowen, Li Qibin
Faculty of Geosciences and Environmental Engineering, Southwest Jiaotong University, 611756, China.
Faculty of Geosciences and Environmental Engineering, Southwest Jiaotong University, 611756, China.
Sci Total Environ. 2023 Dec 20;905:167147. doi: 10.1016/j.scitotenv.2023.167147. Epub 2023 Sep 18.
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 O- 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 (O 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, +HO, 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.
页岩气开采过程中会产生大量含有难降解有机化合物的页岩气返排废水(SGFW),若处理不当,会对环境造成严重威胁。然而,SGFW中有机物的组成极其复杂,目前仍不清楚,其在以O和OH为主的体系中的转化途径也未得到充分认识,这限制了处理技术的选择和运行参数的优化。采用电喷雾电离傅里叶变换离子回旋共振质谱法,对比研究了臭氧氧化和芬顿工艺处理SGFW时溶解有机物(DOM)的去除特性及反应机理。结果表明,两种工艺均可降解低氧高不饱和及酚类有机物、多酚类和多环芳烃,并将其转化为脂肪族有机物以及高氧高不饱和及酚类有机物。随着活性氧(臭氧氧化中的O和芬顿工艺中的OH)作用的增强,臭氧氧化过程中降解产物(主要为脂肪族有机物)增加。然而,在芬顿工艺中,去除的DOM范围更广,且无脂肪族有机物积累。臭氧氧化和芬顿工艺中DOM的降解机制均以加氧反应(+3O、+HO和+2O)为主导途径。然而,臭氧氧化表现出更剧烈的氧化、羟基化和羧基化反应,而芬顿工艺则表现出更剧烈的断链反应。这些结果揭示了SGFW处理过程中臭氧的选择性氧化和OH的非选择性氧化,为选择SGFW处理方法提供了理论支持。