期刊文献+

Catalytic wet air oxidation of phenol, nitrobenzene and aniline over the multi-walled carbon nanotubes (MWCNTs) as catalysts

Catalytic wet air oxidation of phenol, nitrobenzene and aniline over the multi-walled carbon nanotubes (MWCNTs) as catalysts
原文传递
导出
摘要 Wet air oxidation (WAO) is one of effective technologies to eliminate hazardous, toxic and highly concentrated organic compounds in the wastewater. In the paper, multi-walled carbon nanotubes (MWCNTs), functionalized by 03, were used as catalysts in the absence of any metals to investigate the catalytic activity in the catalytic wet air oxidation (CWAO) of phenol, nitrobenzene (NB) and aniline at the mild operating conditions (reaction temperature of 155℃ and total pressure of 2.5 MPa) in a batch reactor. The MWCNTs were characterized with scanning electron microscopy (SEM), transmission electron microscopy (TEM), gas adsorption measurements (BET), fourier transform infrared spectroscopy (FT-IR), and X-ray photoelectron spectroscopy (XPS). The functionalized MWCNTs showed good catalytic performance. In the CWAO of phenol over the functionalized MWCNTs, total phenol removal was obtained after 90 rain run, and the reaction apparent activation energy was ca. 40kJ · mol^-1. The NB was not removed in the CWAO of single NB, while ca. 97% NB removal was obtained and 40% NB removal was attributed to the catalytic activity after 180 min run in the presence of phenol. Ca. 49% aniline conversion was achieved after 120 min run in the CWAO of aniline. Wet air oxidation (WAO) is one of effective technologies to eliminate hazardous, toxic and highly concentrated organic compounds in the wastewater. In the paper, multi-walled carbon nanotubes (MWCNTs), functionalized by 03, were used as catalysts in the absence of any metals to investigate the catalytic activity in the catalytic wet air oxidation (CWAO) of phenol, nitrobenzene (NB) and aniline at the mild operating conditions (reaction temperature of 155℃ and total pressure of 2.5 MPa) in a batch reactor. The MWCNTs were characterized with scanning electron microscopy (SEM), transmission electron microscopy (TEM), gas adsorption measurements (BET), fourier transform infrared spectroscopy (FT-IR), and X-ray photoelectron spectroscopy (XPS). The functionalized MWCNTs showed good catalytic performance. In the CWAO of phenol over the functionalized MWCNTs, total phenol removal was obtained after 90 rain run, and the reaction apparent activation energy was ca. 40kJ · mol^-1. The NB was not removed in the CWAO of single NB, while ca. 97% NB removal was obtained and 40% NB removal was attributed to the catalytic activity after 180 min run in the presence of phenol. Ca. 49% aniline conversion was achieved after 120 min run in the CWAO of aniline.
出处 《Frontiers of Environmental Science & Engineering》 SCIE EI CAS CSCD 2015年第3期436-443,共8页 环境科学与工程前沿(英文)
基金 This research is supported by the National Natural Science Foundation of China (Grant No. 51078143). Moreover, the authors are sincerely grateful to special fund of State Key Joint Laboratory of Environment Simulation and Pollution Control (12K10ESPCT), the Funda- mental Research Funds for the Central Universities (KJ2012071) and the Natural Science Foundation of Heilongjiang Province (B201104) for financial support. In addition, the authors also wish to acknowledge Beijing Cnano Technology Limited Company for kindly supplying the MWCNTs in our study.
关键词 catalytic wet nanotubes (CNTs) PHENOL air oxidation (CWAO) carbon nitrobenzene ANILINE catalytic wet nanotubes (CNTs), phenol, air oxidation (CWAO), carbon nitrobenzene, aniline
  • 相关文献

参考文献35

  • 1Wang Y T. Effect of chemical oxidation on anerobic biodegradation of model phenolic compounds. Water Environment Research, 1992, 64(3): 268-273.
  • 2Lee S H, Carberry J B. Biodegradation of PCP enhanced by chemical oxidation pretreatment. Water Environment Research, 1992, 64(5): 682-690.
  • 3Li H B, Cao H B, Li Y P, Zhang Y, Liu H R. Effect of organic compounds on nitrite accumulation during the nitrification process for coking wastewater. Water Science & Technology, 2010, 62(9): 2096-2105.
  • 4Niu J F, Lin H, Xu J L, Wu H, Li Y Y. Electrochemical mineralization of perfluorocarboxylic acids (PFCAs) by Ce-doped modified porous nanocrystalline PbO2 film electrode. Environmen- tal Science & Technology, 2012, 46(18): 10191-10198.
  • 5Mishra V S, Mahajani V V, Joshi J B. Wet air oxidation. Industrial & Engineering Chemistry Research, 1995, 34(1): 248.
  • 6Luck F. Wet air oxidation: past, present and future. Catalysis Today, 1999, 53(1): 8141.
  • 7Yang S X, Liu Z Q, Huang X H, Zhang B P. Wet air oxidation of epoxy acrylate monomer industrial wastewater. Journal of Hazar- dous Materials, 2010, 178(1-3): 786-791.
  • 8Oliviero L, Barbier J Jr, Duprez D. Wet air oxidation of nitrogen- containing organic compounds and ammonia in aqueous media. Applied Catalysis B: Environmental, 2003, 40(3): 163-184.
  • 9Benitez F J, Garcla J, Acero J L, Real F J, Roldan G. Non-catalytic and catalytic wet air oxidation of pharmaceuticals in ultra-pure and natural waters. Process Safety and Environmental Protection, 2011, 89(5): 334-341.
  • 10Chert I P, Lin S S, Wang C H, Chang L, Chang J S. Preparing and characterizing an optimal supported ceria catalyst for the catalytic wet air oxidation of phenol. Applied Catalysis B: Environmental, 2004, 50(1): 49-58.

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部