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超声/Fenton 法协同降解纺织印染污泥中多环芳烃的研究:系统参数影响与协同效应。

Degradation of polycyclic aromatic hydrocarbons (PAHs) in textile dyeing sludge with ultrasound and Fenton processes: Effect of system parameters and synergistic effect study.

机构信息

School of Environmental Science and Engineering, Institute of Environmental Health and Pollution Control, Guangdong University of Technology, Guangzhou 510006, China.

School of Environmental Science and Engineering, Institute of Environmental Health and Pollution Control, Guangdong University of Technology, Guangzhou 510006, China.

出版信息

J Hazard Mater. 2016 Apr 15;307:7-16. doi: 10.1016/j.jhazmat.2015.12.047. Epub 2015 Dec 29.

Abstract

To establish an efficient oxidation process for the degradation of polycyclic aromatic hydrocarbons (PAHs) in textile dyeing sludge, the effects of various operating parameters were optimized during the ultrasound process, Fenton process and the combined ultrasound-Fenton process. The results showed that the ultrasonic density of 1.80w/cm(3), both H2O2 and Fe(2+) dosages of 140mmol/L and pH 3 were favorable conditions for the degradation of PAHs. The degradation efficiency of high molecular weight PAHs was close to or even higher than that of light molecular weight PAHs. The highest degradation efficiencies of Σ16 PAHs were obtained within 30min in the order of: Fenton (83.5%) >ultrasound-Fenton (75.5%) >ultrasound (45.5%), then the efficiencies were decreased in the other of: ultrasound-Fenton (73.0%) >Fenton (70.3%) >ultrasound (41.4%) in 60min. The extra PAHs were released from the intracellular substances and the cavities of sludge due to the disruption of sludge during the oxidation process. Also, the degradation of PAHs could be inhibited by the other organic matter in the sludge. The combined ultrasound-Fenton process showed more efficient than both ultrasound process and Fenton process not only in the surface of sludge but also in the sludge interior.

摘要

为了建立一种高效的氧化工艺,用于降解纺织印染污泥中的多环芳烃(PAHs),在超声过程、芬顿过程和超声-芬顿联合过程中优化了各种操作参数。结果表明,超声密度为 1.80w/cm(3)、H2O2 和 Fe(2+)用量均为 140mmol/L、pH 值为 3 是 PAHs 降解的有利条件。高分子量 PAHs 的降解效率接近甚至高于低分子量 PAHs。在 30min 内,Σ16 PAHs 的最高降解效率顺序为:芬顿(83.5%)>超声-芬顿(75.5%)>超声(45.5%),然后在 60min 内,降解效率依次降低为:超声-芬顿(73.0%)>芬顿(70.3%)>超声(41.4%)。由于氧化过程中污泥的破坏,细胞内物质和污泥空腔中的额外 PAHs 被释放出来。此外,污泥中的其他有机物也会抑制 PAHs 的降解。与超声过程和芬顿过程相比,超声-芬顿联合过程不仅在污泥表面,而且在污泥内部都显示出更高的效率。

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