Elucidating nitrifying performance, nitrite accumulation and microbial community in a three-stage plug flow moving bed biofilm reactor (PF - MBBR)

硝基螺 蛋白质细菌 亚硝基单胞菌 流出物 亚硝酸盐 酸杆菌 拟杆菌 浮霉菌门 生物膜 微生物种群生物学 移动床生物膜反应器 环境化学 生物 硝化作用 单胞菌 废水 水力停留时间 化学 微生物学 食品科学 环境工程 细菌 生态学 16S核糖体RNA 硝酸盐 环境科学 氮气 假单胞菌 有机化学 遗传学
作者
Yajun Fan,Miao Zhang,Jilin Cheng,Daming Yong,Junjie Ji,Qichao Wu,Chengda He
出处
期刊:Chemosphere [Elsevier BV]
卷期号:297: 134087-134087 被引量:15
标识
DOI:10.1016/j.chemosphere.2022.134087
摘要

A three-stage plug flow moving bed biofilm reactor (PF - MBBR, consisting of three identical chambers of N1, N2 and N3) was proposed for nitrifier enrichment using synthetic wastewater. During the stable operation, the average NH4+-N effluent was 0.67 mg/L and NH4+-N removal was as high as 97.19% with the nitrite accumulation ratio (NAR) of 54.23%, although the biofilm thickness and biomass both presented downward trends from N1 (296 μm, 2280 mg/L), N2 (248 μm, 1850 mg/L) to N3 (198 μm, 1545 mg/L). Particularly, the comparative results of three stages revealed that N2 showed the optimum NH4+-N removal (77.27%) and NAR (75.21%) in the continuous-flow, while NAR of N3 unexpectedly maintained a high level of 65.83% in the batch test, suggesting that ammonia oxidizing bacteria (AOB) accounted for absolute advantage over nitrite oxidizing bacteria (NOB). High-throughput sequencing initially verified different distribution of bacterial community structure, where N2 was far away from N1 and N3 with the lowest community richness and community diversity (operational taxonomic units (OTUs): 454(N2)<527(N3)<621(N1)). Proteobacteria (77.60%-83.09%), Bacteroidetes (1.66%-3.66%), Acidobacteria (2.28%-4.67%), and Planctomycetes (1.19%-6.63%) were the major phyla. At the genus level, AOB (mainly Nitrosomonas) accounted for 5.08% (N1), 20.74% (N2) and 14.24% (N3) while NOB (mainly Nitrospira) increased from 0.14% (N1), 7.06% (N2) to 4.91% (N3) with the total percentages of 5.22%, 27.80% and 19.15%. Finally, the application feasibility of MBBR optimization linked with nitrite (NO2--N) accumulation for deep-level nutrient removal was discussed.

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