Abstract

ABSTRACTIn this study, effects of the initial nitrate, oxygen and carbon sources on the nitrification and denitrification rate were studied in a lab-scale biotrickling filter (l-BF) inoculated with Chelatococcus daeguensis TAD1, and the maximum nitrification and denitrification rate achieved to 30.08 mg-N/L/h and 100.8 mg-N/L/h, respectively. Thereafter, C. daeguensis TAD1 was initially inoculated into a pilot-scale biotrickling filter (p-BF) to remove NOx from the real flue gas of a coal-fired power plant, and a high removal efficiency of 86.7% at about 45–50°C was obtained. Analysis by PCR-DGGE showed that TAD1 was predominant in the biofilm of l-BF, whereas TAD1 in the biofilm of p-BF coexisted with other microbes to remove NOx together. Overall, the present study demonstrated that C. daeguensis TAD1 was firstly found to be one of the best candidates for the efficient treatment of NOx on a large scale under high flue gas temperature.

Highlights

  • Emissions of nitrogen oxides (NOx, mainly including NO and NO2) have a detrimental effect on ecosystems and human health (Lawrence and Crutzen, 1999)

  • Effects of the initial nitrate, oxygen and carbon sources on the nitrification and denitrification rate were studied in a lab-scale biotrickling filter (l-BF) inoculated with Chelatococcus daeguensis TAD1, and the maximum nitrification and denitrification rate achieved to 30.08 mg-N/L/h and 100.8 mg-N/L/h, respectively

  • The present study demonstrated that C. daeguensis TAD1 was firstly found to be one of the best candidates for the efficient treatment of NOx on a large scale under high flue gas temperature

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Summary

Introduction

Emissions of nitrogen oxides (NOx, mainly including NO and NO2) have a detrimental effect on ecosystems and human health (Lawrence and Crutzen, 1999). NOx, together with sulfur dioxide (SO2) are hazardous air pollutants that lead to the formation of acid rain, airborne particulates, and increased ground level ozone. NOx is growing in intensify, due to the burning of a large number of fossil fuels like in power plants and traffic vehicles. Technologies used to treat NOx usually refer to two methods: (1) conventional physico-chemical control systems with the major drawbacks of high operating cost and of possibility of the secondary pollution (Flanagan et al, 2002; Jin et al, 2005); (2) biological techniques with characteristics of high efficiency and low pollution.

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