In wastewater treatment plants, nitrifying systems are usually operated with elevated levels of aeration to avoid nitrification failures. This approach contributes significantly to operational costs and the carbon footprint of nitrifying wastewater treatment processes. In this study, we tested the effect of aeration rate on nitrification by correlating ammonia oxidation rates with the structure of the ammonia-oxidizing bacterial (AOB) community and AOB abundance in four parallel continuous-flow reactors operated for 43 days. Two of the reactors were supplied with a constant airflow rate of 0.1 liter/min, while in the other two units the airflow rate was fixed at 4 liters/min. Complete nitrification was achieved in all configurations, though the dissolved oxygen (DO) concentration was only 0.5 ؎ 0.3 mg/liter in the low-aeration units. The data suggest that efficient performance in the low-DO units resulted from elevated AOB levels in the reactors and/or putative development of a mixotrophic AOB community. Denaturing gel electrophoresis and cloning of AOB 16S rRNA gene fragments followed by sequencing revealed that the AOB community in the low-DO systems was a subset of the community in the high-DO systems. However, in both configurations the dominant species belonged to the Nitrosomonas oligotropha lineage. Overall, the results demonstrated that complete nitrification can be achieved at low aeration in lab-scale reactors. If these findings could be extended to full-scale plants, it would be possible to minimize the operational costs and greenhouse gas emissions without risk of nitrification failure.The water industry is energy intensive. In the United Kingdom, the water industry uses 9 TWh, releasing 5 million tonnes (carbon dioxide equivalent) of greenhouse gases (GHGs) to the atmosphere per year (61). Driven by increasing operational power costs and the need to abate anthropogenic GHG release, the water industry is being forced to develop new lowenergy and cost-effective technologies. In activated sludge systems, particular regard should be given to nitrification, the two-step biological oxidation of ammonia to nitrate via nitrite. This process prevents excessive hazardous discharges of nitrogen into receiving waters. Conventional nitrification is carried out by the ammonia-oxidizing bacteria (AOB) and the nitriteoxidizing bacteria (NOB). The AOB, responsible for the first and often limiting step of nitrification (39), are generally considered to have a strictly chemolithoautotrophic aerobic metabolism, to grow slowly, and to be poor competitors for oxygen (22, 60). Consequently, nitrifying systems are usually operated at a solid retention time (SRT) longer than 5 days and dissolved oxygen (DO) concentration above 2 mg/liter to satisfy both carbon and nitrogen removal requirements and to overcome diffusional resistance in the flocs (59).However, there is evidence that complete nitrification can also occur at low DO levels (Ͻ0.5 mg/liter) (35) or with intermittent aeration (30). Also, a recent theoretical study ...