Effect of the carbon source on N2O emissions during biological denitrification

During biological denitrification in Waste Water Treatment Plants (WWTPs), many parameters (chemical, physical and biological) are responsible for greenhouse gas emissions such as nitrous oxide (N2O) and nitric oxide (NO). The present study intends to investigate the impact of the carbon source more specifically on N2O emissions, but also on NO emissions. The experiments were done in a bioreactor performing batch denitrification at a laboratory scale. Three sources of carbon were tested: ethanol and acetate as short carbon chain compounds and a mixture composed of ethanol and acetate and two long carbon chain compounds: casein extract and meat extract. The nitrogen source was always nitrates (NO3−) and the ratio COD/N was set to three. Current nitrite and nitrate ions, nitric and nitrous oxide levels were monitored during experimentation. The results principally show that the acetate carbon source generates the highest N2O and NO emissions (74% and 19% of denitrified N-NO3−, respectively). The results of this work suggest that the type and length of the carbon source used are responsible for nitrogen emissions but not in the expected way. While the literature always focuses on the inhibitory effect of nitrites on N2O emissions, this work has singled out that NO may also exert inhibitory effects on the N2O reductase enzyme. These results may be explained by the diversity of denitrifying bacteria and their distinct metabolic pathways towards the added carbon substrates (influents).

[1]  F. Kargı,et al.  Simultaneous adsorption and biological treatment of pre-treated landfill leachate by fed-batch operation , 2003 .

[2]  D. Wareham,et al.  Utilization patterns of volatile fatty acids in the denitrification reaction , 2007 .

[3]  G. Tallec,et al.  Nitrous oxide emissions from secondary activated sludge in nitrifying conditions of urban wastewater treatment plants: effect of oxygenation level. , 2006, Water research.

[4]  B. Loubet,et al.  Characterisation of soil emissions of nitric oxide at field and laboratory scale using high resolution method , 2009 .

[5]  F. Kargı,et al.  Effect of carbon source on biological nutrient removal in a sequencing batch reactor. , 2003, Bioresource technology.

[6]  N. Ren,et al.  Synthesis of PHAs from waster under various C:N ratios. , 2007, Bioresource technology.

[7]  S. Mathieu,et al.  Estimation of wastewater biodegradable COD fractions by combining respirometric experiments in various So/Xo ratios , 2000 .

[8]  D. Chadwick,et al.  Factors affecting Nitrogen Transformations and Related Nitrous Oxide Emissions from Aerobically Treated Piggery Slurry , 1999 .

[9]  L. Horowitz,et al.  Photochemical oxidant formation over southern Switzerland: 2. Model results , 1997 .

[10]  A. Bouwman,et al.  Global air emission inventories for anthropogenic sources of NOx, NH3 and N2O in 1990 , 1998 .

[11]  K. Hanaki,et al.  Nitrous oxide production in high-loading biological nitrogen removal process under low COD/N ratio condition. , 2001, Water research.

[12]  A. Hiraishi,et al.  Application of polyhydroxyalkanoates for denitrification in water and wastewater treatment , 2003, Applied Microbiology and Biotechnology.

[13]  J. Salminen,et al.  Acetate and ethanol as potential enhancers of low temperature denitrification in soil contaminated by fur farms: a pilot-scale study. , 2009, Journal of hazardous materials.

[14]  J. Houghton,et al.  Climate change 2001 : the scientific basis , 2001 .

[15]  W. Payne Reduction of nitrogenous oxides by microorganisms. , 1973, Bacteriological reviews.