Abstract

Nitrification activities and microbial populations of ammonium oxidizing bacteria (AOB) and nitrite oxidizing bacteria (NOB) were investigated in 10 full-scale biological nutrient removal wastewater treatment plants in Xi’an, China. Aerobic batch tests were used to determine the nitrifying activities while fluorescence in situ hybridization was used to quantify the fractions of AOB and NOB in the activated sludge. The results showed that nitrifying bacteria accounted for 1–10% of the total population. Nitrosomonas and Nitrospira were the dominant bacteria for AOB and NOB respectively. Moreover, the average percentage of AOB was 1.27% and that of NOB was 4.02%. The numerical ratios of NOB/AOB varied between 1.72 and 5.87. The average ammonium uptake rate and nitrite uptake rate were 3.25 ± 0.52 mg (NH4+–N)/g(VSS) h and 4.49 ± 0.49 mg (NO2−–N)/g(VSS) h, respectively. Correspondingly, the activity of NOB was 1.08–2.00 times higher than that of AOB. Thus, NOB was the dominating bacteria in nitrifying communities. The year-round data of Dianzicun (W6) also expressed a similar trend. Since NOB had higher activities than that of AOB, a large nitrite oxidation pool could be formed, which guaranteed that no nitrite would be accumulated. Therefore, stable nitrification could be achieved. A conceptual model was proposed to describe the population variation of AOB and NOB in a nitrifying community.

Highlights

  • Nitrification is of great importance for nitrogen removal from municipal wastewater in the biological nutrient removal process (BNR) employed in waste water treatment plants (WWTPs)

  • Ammonium is firstly oxidized to nitrite via ammonia-oxidizing bacteria (AOB), and to nitrate by nitrite-oxidizing bacteria (NOB)

  • Dominant bacteria responding to different treatment processes Nitrifying community structures in activated sludge of 10 WWTPs were analyzed by fluorescence in situ hybridization (FISH)

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Summary

Introduction

Nitrification is of great importance for nitrogen removal from municipal wastewater in the biological nutrient removal process (BNR) employed in waste water treatment plants (WWTPs). Ammonium is firstly oxidized to nitrite via ammonia-oxidizing bacteria (AOB), and to nitrate by nitrite-oxidizing bacteria (NOB). Nitrifying bacteria populations are generally within the range of 4–6% of biomass for adequate nitrification in nutrient. The numerical ratio of AOB to NOB in a balanced nitrifying system should be 2:1 according to thermodynamics and electron transfer (Arciero et al 1991; Hooper et al 1997; Mari et al 2012), which means that AOB should be the dominant bacteria in a nitrifying community. Li et al (2007) found that the AOB to NOB ratio in a sufficient nitrification process was 2.2–2.7. You et al (2003) reported the percentage

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