Li Bo, Wu Guangxue
Key Laboratory of Microorganism Application and Risk Control (MARC) of Shenzhen, Graduate School at Shenzhen, Tsinghua University, Shenzhen 518055, Guangdong, China.
Int J Environ Res Public Health. 2014 Mar 27;11(4):3553-69. doi: 10.3390/ijerph110403553.
Sludge retention time (SRT) is an important factor affecting not only the performance of the nutrient removal and sludge characteristics, but also the production of secondary pollutants such as nitrous oxide (N2O) in biological nutrient removal (BNR) processes. Four laboratory-scale sequencing batch reactors (SBRs), namely, SBR5, SBR10, SBR20 and SBR40 with the SRT of 5 d, 10 d, 20 d and 40 d, respectively, were operated to examine effects of SRT on nutrient removal, activated sludge characteristics and N2O emissions. The removal of chemical oxygen demand or total phosphorus was similar under SRTs of 5-40 d, SRT mainly affected the nitrogen removal and the optimal SRT for BNR was 20 d. The molecular weight distribution of the effluent organic matters was in the range of 500-3,000 Da under SRTs of 5-40 d. The lowest concentration of the effluent soluble microbial products concentration was obtained at the SRT of 5 d. Nitrifier growth was limited at a short SRT and nitrite existed in the effluent of SBR5. With increasing SRTs, mixed liquor suspended solids concentration increased while the excess sludge production was reduced due to the high endogenous decay rate at high SRTs. Endogenous decay coefficients were 0.020 d⁻¹, 0.036 d⁻¹, 0.037 d⁻¹ and 0.039 d⁻¹ under SRTs of 5-40 d, respectively. In BNR, the N2O emission occurred mainly during the aerobic phase and its emission ratio decreased with increasing SRTs. The ratio between the N2O-N emission and the removed ammonium nitrogen in the aerobic phase was 5%, 3%, 1.8% and 0.8% at the SRT of 5 d, 10 d, 20 d and 40 d, respectively. With low concentrations of dissolved oxygen and high concentrations of oxidized nitrogen, the N2O emission was significantly accelerated due to heterotrophic denitrification activities.
污泥停留时间(SRT)是一个重要因素,不仅影响生物脱氮(BNR)过程中营养物去除性能和污泥特性,还影响一氧化二氮(N₂O)等二次污染物的产生。运行了四个实验室规模的序批式反应器(SBR),即SRT分别为5天、10天、20天和40天的SBR5、SBR10、SBR20和SBR40,以研究SRT对营养物去除、活性污泥特性和N₂O排放的影响。在5 - 40天的SRT下,化学需氧量或总磷的去除情况相似,SRT主要影响氮的去除,BNR的最佳SRT为20天。在5 - 40天的SRT下,出水有机物的分子量分布在500 - 3000 Da范围内。在SRT为5天时,出水可溶性微生物产物浓度最低。在短SRT下,硝化菌生长受限,SBR5的出水中存在亚硝酸盐。随着SRT增加,混合液悬浮固体浓度增加,而由于高SRT下较高的内源衰减率,剩余污泥产量降低。在5 - 40天的SRT下,内源衰减系数分别为0.020 d⁻¹、0.036 d⁻¹、0.037 d⁻¹和0.039 d⁻¹。在BNR中,N₂O排放主要发生在好氧阶段,其排放率随SRT增加而降低。在SRT为5天、10天、20天和40天时,好氧阶段N₂O - N排放与去除的铵态氮之比分别为5%、3%、1.8%和0.8%。在低溶解氧浓度和高氧化态氮浓度下,由于异养反硝化活动,N₂O排放显著加速。