Nitrite build-up effect on nitrous oxide emissions in a laboratory-scale anaerobic/aerobic/anoxic/aerobic sequencing batch reactor

  • Larissa Coelho Auto Gomes Departamento de Saneamento e Saúde Ambiental (DSSA). Escola Nacional de Saúde Pública Sérgio Arouca (ENSP/Fiocruz), Rua Leopoldo Bulhões, n° 1480, CEP: 21041-210, Rio de Janeiro, RJ, Brazil.
  • Barbara Costa Pereira Departamento de Saneamento e Saúde Ambiental (DSSA). Escola Nacional de Saúde Pública Sérgio Arouca (ENSP/Fiocruz), Rua Leopoldo Bulhões, n° 1480, CEP: 21041-210, Rio de Janeiro, RJ, Brazil.
  • Renato Pereira Ribeiro Centro Experimental de Monitoramento e Mitigação Ambiental. Instituto Federal do Rio de Janeiro (IFRJ), Rua Lúcio Tavares, n° 1045, CEP: 26530-060, Nilópolis, RJ, Brazil.
  • Jaime Lopes da Mota Oliveira Departamento de Saneamento e Saúde Ambiental (DSSA). Escola Nacional de Saúde Pública Sérgio Arouca (ENSP/Fiocruz), Rua Leopoldo Bulhões, n° 1480, CEP: 21041-210, Rio de Janeiro, RJ, Brazil.
Keywords: nitrite accumulation, nitrous oxide production and emission, sequencing batch reactor

Abstract

Biological wastewater treatment processes with biological nitrogen removal are potential sources of nitrous oxide (N2O) emissions. It is important to expand knowledge on the controlling factors associated with N2O production, in order to propose emission mitigation strategies. This study therefore sought to identify the parameters that favor nitrite (NO2-) accumulation and its influence on N2O production and emission in an anaerobic/aerobic/anoxic/aerobic sequencing batch reactor with biological nitrogen removal. Even with controlled dissolved oxygen concentrations and oxidation reduction potential, the first aerobic phase promoted only partial nitrification, resulting in NO2- build-up (ranging from 29 to 57%) and consequent N2O generation. The NO2- was not fully consumed in the subsequent anoxic phase, leading to even greater N2O production through partial denitrification. A direct relationship was observed between NO2- accumulation in these phases and N2O production. In the first aerobic phase, the N2O/NO2- ratio varied between 0.5 to 8.5%, while in the anoxic one values ranged between 8.3 and 22.7%. Higher N2O production was therefore noted during the anoxic phase compared to the first aerobic phase. As a result, the highest N2O fluxes occurred in the second aerobic phase, ranging from 706 to 2416 mg N m-2 h-1, as soon as aeration was triggered. Complete nitrification and denitrification promotion in this system was proven to be the key factor to avoid NO2- build-up and, consequently, N2O emissions.

Published
23/03/2021
Section
Papers