Integrating food waste (FW) into
a wastewater treatment system
through FW disposers facilitates waste reduction and energy recovery;
however, it may pose challenges to the downstream biological nitrogen
removal (BNR) processes. Particularly, the response of nitrous oxide
(N<sub>2</sub>O, a potent greenhouse gas) emissions to FW discharge
is underexplored. In this study, it was revealed that FW contributed
to N<sub>2</sub>O mitigation by regulating denitrification. Chronic
FW addition enhanced N<sub>2</sub>O reduction capacity while weakening
the rates of other denitrification processes, thereby providing an
N<sub>2</sub>O sink for possible mitigation. Meanwhile, nitrite accumulation
during the predenitrification phase was completely avoided in the
presence of FW, reducing N<sub>2</sub>O production in the subsequent
nitrification. As a result, the overall N<sub>2</sub>O emission factor
of the mainstream BNR system decreased from 6.49% to 0.84% with FW
addition. In addition, N<sub>2</sub>O production during nitrification
increased by 19.8–118.2% because of the elevated ammonia-oxidizing
bacteria (AOB) denitrification pathway by chronic FW addition, while
the nitrification activities were reduced. The underlying mechanisms
for the altered N<sub>2</sub>O emission by FW addition were explored
from the point of view of sludge properties and microbial communities.
This study provided insights into the strategic management of FW while
focusing on the concern of N<sub>2</sub>O emissions in the context
of FW integration into wastewater systems.