Initial free ammonia is critical for robust acidic partial nitrification in sequencing batch reactor
Siqi Li1, Xiaofeng Kang1, Jiang Men2
1State Key Joint Laboratory of Environment Simulation and Pollution Control, School of Environment, Tsinghua University, Beijing, 100084, China.
Achieving stable partial nitrification (PN) in wastewater treatment is challenging with low ammonia. This study identified free ammonia and pH as critical factors for robust PN in sequencing batch reactors (SBRs).
Area of Science:
- Environmental Engineering
- Wastewater Treatment
- Microbial Ecology
Background:
- Partial nitrification (PN) implementation is hindered by low influent ammonium (NH4+-N) concentrations.
- Stability and inhibition boundary conditions for nitrite-oxidizing bacteria (NOB) in sequencing batch reactors (SBRs) treating low-strength wastewater are not well-defined.
- Dynamic environmental factors in SBRs complicate achieving stable PN.
Purpose of the Study:
- To identify critical factors for stable partial nitrification (PN) in SBRs.
- To extend the boundary conditions for stable PN under dynamic environmental conditions.
- To investigate the combined inhibition of free ammonia (FA) and free nitrous acid on NOB in SBRs.
Main Methods:
- Long-term operation (580 days) of a conventionally configured SBR.
- Investigation of combined inhibition by dynamic free ammonia (FA) and free nitrous acid on different NOB.
- Kinetic parameter measurement and model development for predicting PN conditions.
Main Results:
- Initial free ammonia (FA) concentration is critical for establishing PN under low-alkalinity conditions.
- Nitrospira NOB are highly sensitive to FA inhibition (KI_FA=0.35 mg NH3-N/L), reducing required FA levels.
- Lowering pH to 5.4 effectively inhibited acid-intolerant Ca. Nitrotoga NOB, crucial for maintaining PN.
Conclusions:
- Initial FA concentration is a critical factor for achieving stable and robust acidic partial nitrification (PN) in SBRs.
- Controlling FA and pH provides effective inhibition of NOB, enabling stable PN in low-strength wastewater.
- Study findings offer guidance for robust acidic PN implementation in conventional SBRs.
Related Concept Videos
Preparation of Amines: Alkylation of Ammonia and Amines
Each alkylation step makes the nitrogen center more nucleophilic, which triggers successive alkylations until a quaternary ammonium salt is formed. Considering...
Titration of a Weak Base with a Strong Acid
Using the ICE table and substituting the Kb value, we calculate the initial pH of 50 mL of 0.1 M ammonia to be 11.11. Addition of 25 mL of 0.1 M hydrochloric acid to this solution of ammonia results in a buffer with an equal concentration of ammonia and ammonium ions. The pH of this buffer can be calculated by substituting these...
2° Amines to N-Nitrosamines: Reaction with NaNO2
Overview of Nitrogen Metabolism
The largest pool of nitrogen available in the terrestrial ecosystem is gaseous nitrogen (N2) from the air, but this...
Basicity of Aliphatic Amines
To measure the basicity of amines, two conventions are generally used. The first defines Kb as the basicity constant for the deprotonation reaction of water by the amine, as presented in Figure 1. Conventionally, lower Kb indicates...
1° Amines to Diazonium or Aryldiazonium Salts: Diazotization with NaNO2 Overview
The nitrous acid is unstable. Hence, it is formed in situ from a solution of sodium nitrite and cold aqueous acids such as hydrochloric or sulfuric acid. In an acidic solution, the –OH group of nitrous acid undergoes protonation to give oxonium ion, followed by...


