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含硫铁碳纳米复合材料激活过硫酸盐,用于石油污染土壤的联合化学氧化和微生物修复。

Sulfur-containing iron carbon nanocomposites activate persulfate for combined chemical oxidation and microbial remediation of petroleum-polluted soil.

机构信息

Shandong Key Laboratory of Water Pollution Control and Resource Reuse, School of Environmental Science and Engineering, Shandong University, Qingdao 266200, PR China.

Shandong Academy of Agricultural Sciences, Jinan 250100, PR China.

出版信息

J Hazard Mater. 2024 May 5;469:133889. doi: 10.1016/j.jhazmat.2024.133889. Epub 2024 Feb 24.

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 1:1 soil-water ratio. The EPR and quenching experiments demonstrated that the degradation of TPHs was caused by the combination of O·OH, SO·, and O·. 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.

摘要

在这项研究中,通过煅烧负载铁的生物质合成了含硫铁碳纳米复合材料(S@Fe-CN),并将其用于激活过硫酸盐(PS),以实现石油污染土壤的联合化学氧化和微生物修复。在活化剂用量为 0.2%、PS 用量为 1%、土壤-水比为 1:1 的条件下,总石油烃(TPHs)的去除效率最高。EPR 和猝灭实验表明,TPHs 的降解是由·OH、SO·和·O 共同作用引起的。在 S@Fe-CN 激活过硫酸盐(S@Fe-CN/PS)体系中,TPHs 的降解经历了两个阶段:化学氧化(第 0 天至第 3 天)和微生物降解(第 3 天至第 28 天),动力学常数分别与化学和微生物修复的拟一级动力学一致。在 S@Fe-CN/PS 体系中,土壤酶活性先降低后升高,表明在活化剂的保护下,化学氧化后微生物活性得到恢复。微生物群落分析表明,S@Fe-CN/PS 组影响了微生物的丰度和结构,经过 28 天后,TPH 降解菌的相对丰度增加。此外,S@Fe-CN/PS 增强了微生物间的相互作用,减轻了微生物的竞争,从而提高了土著微生物降解 TPHs 的能力。

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