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Sulfur-containing iron carbon nanocomposites activate persulfate for combined chemical oxidation and microbial remediation of petroleum-polluted soil.
Ma, Mengyu; An, Ning; Wang, Yanqin; Zhao, Chao; Cui, Zhaojie; Zhou, Weizhi; Gu, Meixia; Li, Qian.
Affiliation
  • Ma M; Shandong Key Laboratory of Water Pollution Control and Resource Reuse, School of Environmental Science and Engineering, Shandong University, Qingdao 266200, PR China.
  • An N; Shandong Key Laboratory of Water Pollution Control and Resource Reuse, School of Environmental Science and Engineering, Shandong University, Qingdao 266200, PR China.
  • Wang Y; Shandong Academy of Agricultural Sciences, Jinan 250100, PR China.
  • Zhao C; Shandong Provincial Soil Pollution Prevention and Control Centre, Jinan 250012, PR China.
  • Cui Z; Shandong Key Laboratory of Water Pollution Control and Resource Reuse, School of Environmental Science and Engineering, Shandong University, Qingdao 266200, PR China.
  • Zhou W; School of Civil Engineering, Shandong University, Jinan 250100, PR China.
  • Gu M; Sinopec Petroleum Engineering & Design Co., Ltd., Dongying 257100, PR China.
  • Li Q; Shandong Key Laboratory of Water Pollution Control and Resource Reuse, School of Environmental Science and Engineering, Shandong University, Qingdao 266200, PR China. Electronic address: qianli@sdu.edu.cn.
J Hazard Mater ; 469: 133889, 2024 May 05.
Article in En | MEDLINE | ID: mdl-38422735
ABSTRACT
In this study, sulfur-containing iron carbon nanocomposites (S@Fe-CN) were synthesized by calcining iron-loaded biomass and utilized to activate persulfate (PS) for the combined chemical oxidation and microbial remediation of petroleum-polluted soil. The highest removal efficiency of total petroleum hydrocarbons (TPHs) was achieved at 0.2% of activator, 1% of PS and 11 soil-water ratio. The EPR and quenching experiments demonstrated that the degradation of TPHs was caused by the combination of 1O2,·OH, SO4·-, and O2·-. In the S@Fe-CN activated PS (S@Fe-CN/PS) system, the degradation of TPHs underwent two phases chemical oxidation (days 0 to 3) and microbial degradation (days 3 to 28), with kinetic constants consistent with the pseudo-first-order kinetics of chemical and microbial remediation, respectively. In the S@Fe-CN/PS system, soil enzyme activities decreased and then increased, indicating that microbial activities were restored after chemical oxidation under the protection of the activators. The microbial community analysis showed that the S@Fe-CN/PS group affected the abundance and structure of microorganisms, with the relative abundance of TPH-degrading bacteria increased after 28 days. Moreover, S@Fe-CN/PS enhanced the microbial interactions and mitigated microbial competition, thereby improving the ability of indigenous microorganisms to degrade TPHs.
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Full text: 1 Collection: 01-internacional Database: MEDLINE Main subject: Soil Pollutants / Petroleum Language: En Journal: J Hazard Mater Journal subject: SAUDE AMBIENTAL Year: 2024 Document type: Article

Full text: 1 Collection: 01-internacional Database: MEDLINE Main subject: Soil Pollutants / Petroleum Language: En Journal: J Hazard Mater Journal subject: SAUDE AMBIENTAL Year: 2024 Document type: Article