Affiliation:
1. Department of Civil, Architectural, and Environmental Engineering North Carolina Agricultural & State University Greensboro North Carolina USA
2. Department of Civil & Environmental Engineering Rutgers University Piscataway New Jersey USA
3. Mott MacDonald Freehold New Jersey USA
4. Waste Management, Inc. Gaithersburg Maryland USA
Abstract
AbstractPartial nitritation (PN) is a novel treatment for nitrogen removal using aerobic ammonium oxidation with reduced oxygen requirements compared to conventional nitrification. This study evaluated the performance of the PN process and the factors influencing nitrogen removal from landfill leachate. During the reactivation of biomass, the results showed 70% ammonium removal, but only 20% total nitrogen removal. Further analysis showed that low nitrite accumulation and high nitrate production promoted the growth of nitrite‐oxidizing bacteria (NOB). The ammonium removal activity after soaking the cultivated biomass in synthetic water and leachate was measured to be 0.57, 0.1, 0.17, and 0.25 g N•g VSS−1•d−1 for synthetic wastewater and leachate soaking for synthetic wastewater, 12 h, 3 days, and 7 days, respectively. The study found abundant ammonium‐oxidizing bacteria (AOB) and NOBs in biomass soaked in synthetic wastewater. However, soaking in leachate promoted AOB growth and inhibited NOB growth making leachate suitable for PN.Practitioner Points
The study found that with a longer leachate‐soaking period for biomass, ammonium removal activity increases, which in turn increases ammonium conversions during the PN process.
Ammonium‐oxidizing bacteria (AOB) can acclimate to landfill leachate substrate and grow with a longer soaking period.
Nitrite‐oxidizing bacteria (NOB) were inhibited by landfill leachate substrate, which is beneficial for nitrite accumulation.
Anabolized DO can convert nitrite to nitrate rapidly, which results in higher nitrate accumulation compared to nitrite accumulation.
Hence, the DO level has to be sufficiently low to prevent nitrite oxidation and nitrate accumulation.
Funder
National Science Foundation