Abstract

Nitrous oxide (N2O) is a powerful greenhouse gas emitted from wastewater treatment, as well as natural systems, as a result of biological nitrification and denitrification. While denitrifying bacteria can be a significant source of N2O, they can also reduce N2O to N2. More information on the kinetics of N2O formation and reduction by denitrifying bacteria is needed to predict and quantify their impact on N2O emissions. In this study, kinetic parameters were determined for Paracoccus pantotrophus, a common denitrifying bacterium. Parameters included the maximum specific reduction rates, hat{q}, growth rates, {hat{upmu }}, and yields, Y, for reduction of NO3− (nitrate) to nitrite (NO2−), NO2− to N2O, and N2O to N2, with acetate as the electron donor. The hat{q} values were 2.9 gN gCOD−1 d−1 for NO3− to NO2−, 1.4 gN gCOD−1 d−1 for NO2− to N2O, and 5.3 gN gCOD−1 d−1 for N2O to N2. The {hat{upmu }} values were 2.7, 0.93, and 1.5 d−1, respectively. When N2O and NO3− were added concurrently, the apparent (extant) kinetics, hat{q}_{text{app}}, assuming reduction to N2, were 6.3 gCOD gCOD−1 d−1, compared to 5.4 gCOD gCOD−1 d−1 for NO3− as the sole added acceptor. The {hat{upmu }}_{text{app}} was 1.6 d−1, compared to 2.5 d−1 for NO3− alone. These results suggest that NO3− and N2O were reduced concurrently. Based on this research, denitrifying bacteria like P. pantotrophus may serve as a significant sink for N2O. With careful design and operation, treatment plants can use denitrifying bacteria to minimize N2O emissions.Electronic supplementary materialThe online version of this article (doi:10.1186/s13568-016-0258-0) contains supplementary material, which is available to authorized users.

Highlights

  • Nitrous oxide (N2O) is a potent greenhouse gas with a global warming potential 300-fold greater than carbon dioxide (CO2) (IPCC 2006)

  • The biomass concentration was assessed with a spectrophotometer via the optical density at 600 nm (OD600) (UV10, Thermo, Rochester, NY) and converted to dry weight (DW) using a conversion factor

  • The lower qvalue for NO−2 indicates a bottleneck on the denitrification pathway, i.e., when NO−3 is present at non-rate-limiting concentrations, NO−2 necessarily accumulates, and the observed ited to the maximum rate rate of of N2O

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Summary

Introduction

Nitrous oxide (N2O) is a potent greenhouse gas with a global warming potential 300-fold greater than CO2 (IPCC 2006) It is a major concern for ozone depletion in the stratosphere (Ravishankara et al 2009). Wastewater treatment processes, especially those employing biological nutrient removal (BNR), have been found to be significant sources of N2O (Ni and Yuan 2015). The most common sources of N2O in BNR processes are ammonium-oxidizing bacteria (AOB) and heterotrophic denitrifying bacteria (DNB) (Law et al 2012). AOB can form significant amounts of N2O, especially when the dissolved oxygen (DO) concentrations are low, or during transitions from anoxic to aerobic conditions (Chandran et al 2011; Sabba et al 2015). N2O can form when insufficient electron donor is available, when the pH

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