In
deammonification systems, nitrite-oxidizing bacteria (NOB) suppression
and nitrous oxide (N2O) mitigation are two important operational
objectives. To carry out this multivariable analysis of response,
a comprehensive model for the N cycle was developed and evaluated
against experimental data from a laboratory-scale deammonification
granular sludge sequencing batch reactor. Different aeration strategies
were tested, and the manipulated variables comprised the dissolved
oxygen (DO) set point in the aerated phase, aeration on/off frequency
(F), and the ratio (R) between the non-aerated and aerated phase durations.
Experimental results showed that a high ammonium utilization rate
(AUR) in relation to the low nitrate production rate (NPR) (NPR/AUR
= 0.07–0.08) and limited N2O emissions (E
N2O < 2%) could be achieved at
the DO set point = 0.7 mg O2/L, R ratio = 2, and F frequency
= 6–7 h–1. Under specific operational conditions
(biomass concentration, NH4
+-N loading rate,
and temperature), simulation results confirmed the feasible aeration
strategies for the trade-offs between the NOB suppression and N2O emission. The intermittent aeration regimes led to frequent
shifts in the predominating N2O production pathways, that
is, hydroxylamine (NH2OH) oxidation (aerated phase) versus
autotrophic denitrification (non-aerated phase). The inclusion of
the extracellular polymeric substance mechanism in the model explained
the observed activity of heterotrophs, especially Anaerolineae, and granule formation.