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堆肥后通过类芬顿氧化和生物降解的顺序处理修复石油污染土壤。

Remediation of petroleum-contaminated soil after composting by sequential treatment with Fenton-like oxidation and biodegradation.

机构信息

State Key Laboratory of Heavy Oil Processing, China University of Petroleum, Beijing 102249, China.

出版信息

Bioresour Technol. 2010 Apr;101(7):2106-13. doi: 10.1016/j.biortech.2009.11.002. Epub 2009 Nov 25.

Abstract

A laboratory study was conducted to enhance removal of residual contaminants after composting in a highly petroleum-contaminated soil by combining Fenton-like pretreatment with biodegradation. The contaminants were characterized by Fourier transform ion cyclotron resonance mass spectrometry (FT-ICR MS) during soil treatment. The optimum molar ratio of H(2)O(2) and Fe(3+) was 300/1 determined in batch experiments. At the end of Fenton-like treatment, total dichloromethane-extractable organics (TEO) decreased from 32,400 to 21,800 mg kg(-1) soil, and the toxicity of soil was reduced greatly in the preoxidation process. A significant loss of the number of soil microorganisms was observed in the Fenton-like reaction. During the microbial treatment period, 50.6% of TEO was destroyed. Numerous varieties of polar compounds containing nitrogen and oxygen were identified by FT-ICR MS. The number of compounds containing two oxygen atoms dropped from 604 to 163 during Fenton-like oxidation, and increased again to 577 after biodegradation.

摘要

一项实验室研究旨在通过芬顿预处理与生物降解相结合,提高高度受石油污染土壤中堆肥后残留污染物的去除率。在土壤处理过程中,采用傅里叶变换离子回旋共振质谱(FT-ICR MS)对污染物进行了表征。通过批处理实验确定了最佳的 H(2)O(2)和 Fe(3+)摩尔比为 300/1。在芬顿预处理结束时,总二氯甲烷可萃取有机物(TEO)从 32,400 降至 21,800 mg kg(-1)土壤,土壤的毒性在预氧化过程中大大降低。在芬顿反应中,观察到土壤微生物数量显著减少。在微生物处理期间,50.6%的 TEO 被破坏。通过 FT-ICR MS 鉴定出了大量含有氮和氧的极性化合物。在芬顿氧化过程中,含两个氧原子的化合物数量从 604 降至 163,在生物降解后又增加到 577。

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