Abstract

A partial-denitrification coupling with anaerobic ammonium oxidation (anammox) process (PD/A) in a continuous-flow anoxic/oxic (A/O) biofilm reactor was developed to treat carbon-limited domestic wastewater (ammonia (NH4+-N) of 55 mg/L and chemical oxygen demand (COD) of 148 mg/L in average) for about 200 days operation. Satisfactory NH4+-N oxidation efficiency above 95% was achieved with rapid biofilm formation in the aerobic zone. Notably, nitrite (NO2−-N) accumulation was observed in the anoxic zone, mainly due to the insufficient electron donor for complete nitrate (NO3−-N) reduction. The nitrate-to-nitrite transformation ratio (NTR) achieved was as high as 64.4%. After the inoculation of anammox-enriched sludge to anoxic zones, total nitrogen (TN) removal was significantly improved from 37.3% to 78.0%. Anammox bacteria were effectively retained in anoxic biofilm utilizing NO2−-N produced via the PD approach and NH4+-N in domestic wastewater, with the relative abundance of 5.83% for stable operation. Anammox pathway contributed to TN removal by a high level of 38%. Overall, this study provided a promising method for mainstream nitrogen removal with low energy consumption and organic carbon demand.

Highlights

  • Nitrogen discharge to water bodies can cause eutrophication and brings serious threats to human health

  • Nitrogen removal is the major purpose in current wastewater treatment plants (WWTPs)

  • The continuous-flow A/O biofilm reactor was made of transparent plexiglas, which was divided into nine compartments (Figure 1)

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Summary

Introduction

Nitrogen discharge to water bodies can cause eutrophication and brings serious threats to human health. Nitrogen removal is the major purpose in current wastewater treatment plants (WWTPs). Nitrification/denitrification are commonly employed as traditional biological nitrogen removal technologies in WWTPs. In the first step, ammonia (NH4 + -N). Can be oxidized to nitrite (NO2 − -N) by ammonia-oxidizing bacteria (AOB), and to nitrate (NO3 − -N) by nitrite-oxidizing bacteria (NOB) in the second step [1,2]. NO3 − -N is converted to nitrogen gas (N2 ) by denitrification bacteria with organic carbon as the electron donor. This requires a carbon source and considerable consumption of oxygen, especially for meeting stricter standards [3]

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