Zhu Lin, Cheng Cheng, Song Jia-Jun, Guo Kai-Cheng, Wang Qian, Liu Wen-Ru, Shen Yao-Liang
School of Environmental Science and Engineering, Suzhou University of Science and Technology, Suzhou 215009, China.
National and Local Joint Engineering Laboratory of Municipal Sewage Resource Utilization Technology, Suzhou 215009, China.
Huan Jing Ke Xue. 2020 Apr 8;41(4):1801-1807. doi: 10.13227/j.hjkx.201910164.
The realization process of nitritation was studied in a CSTR reactor seeding with nitrification granular sludge to treat low ammonia sewage. During the operation period, the physical and chemical properties, the spatial distribution of functional microbes, and the activity of the granular sludge were also investigated to elaborate the main factors for the stability of nitritation. The results showed that nitritation can be successfully achieved and maintained by the cooperative controlling of nitrogen loading rate (NLR) and dissolved oxygen (DO) levels, and the nitrite accumulation rate was over 80%. The obtained nitritation granular sludge was brownish yellow, showing a smooth, full ellipsoid or sphere, and the microorganisms on the surface of the particles were mainly cocci; the average particle size was 1.3 mm, and the average sedimentation rate was 71.3 m·h. Batch tests showed that there was a significant stratified distribution structure in granular sludge (particle size >0.8 mm), the ammonia-oxidizing bacteria (AOB) mainly occupied the surface space of the particles, and the nitrite-oxidizing bacteria (NOB) were mainly distributed inside the particles. Flocs or small-size sludge (particle size<0.8 mm) and granular sludge (particle size >0.8 mm) exhibit different spatial distribution characteristics of microorganisms. In the granular sludge reactor, well stratification of the nitrifier guilds, high level of residual ammonia concentrations in effluent (15-33 mg·L), or low ratio between DO and NH-N concentrations (0.08-0.15) should be key influencing factors in the process of achieving nitritation.
在一个接种了硝化颗粒污泥的连续搅拌釜式反应器(CSTR)中研究了亚硝化的实现过程,以处理低氨污水。在运行期间,还研究了颗粒污泥的物理化学性质、功能微生物的空间分布以及活性,以阐明亚硝化稳定性的主要因素。结果表明,通过协同控制氮负荷率(NLR)和溶解氧(DO)水平,可以成功实现并维持亚硝化,亚硝酸盐积累率超过80%。所获得的亚硝化颗粒污泥呈棕黄色,呈光滑、饱满的椭圆形或球形,颗粒表面的微生物主要为球菌;平均粒径为1.3mm,平均沉降速率为71.3m·h。批次试验表明,颗粒污泥(粒径>0.8mm)中存在明显的分层分布结构,氨氧化细菌(AOB)主要占据颗粒的表面空间,亚硝酸盐氧化细菌(NOB)主要分布在颗粒内部。絮体或小尺寸污泥(粒径<0.8mm)与颗粒污泥(粒径>0.8mm)表现出不同的微生物空间分布特征。在颗粒污泥反应器中,硝化菌群的良好分层、出水较高的残余氨浓度水平(15 - 33mg·L)或溶解氧与氨氮浓度之间的低比例(0.08 - 0.15)应是实现亚硝化过程中的关键影响因素。