Lee J W, Cha H-Y, Park K Y, Song K-G, Ahn K-H
Department of Civil and Environmental Engineering, University of Delaware, Newark, DE 19716, USA.
Water Res. 2005 Apr;39(7):1199-204. doi: 10.1016/j.watres.2004.10.004. Epub 2005 Mar 27.
A pilot-scale activated sludge system coupled with sludge ozonation process was operated for 112 days of a winter season without excess sludge wasting. The concept of this process is that the excess sludge produced is first disintegrated by ozone oxidation and then recirculated to a bioreactor in order to mineralize the particulate and soluble organic compounds. The basis of operation was to determine either the optimal amount of sludge in kg SS ozonated each day (SO) or the optimal ozonation frequency under the variable influent chemical oxygen demand (COD) loading and temperature conditions, since the ozone supply consumes costly energy. The optimal SO was obtained using the theoretically estimated sludge production rate (SP) and experimentally obtained ozonation frequency (n). While the SP was mainly subject to the COD loadings, sludge concentration was affected by the temperature changes in winter season. The optimal n was observed between 2.5 and 2.7 at around 15 degrees C, but it was doubled at 10 degrees C. Mixed liquor suspended solids (MLSS) concentration was leveled off at around 5000 mg/L in bioreactor at 15 degrees C, but the volatile fraction of MLSS was fixed around 0.7 indicating that there was no significant inorganic accumulation. Suspended solids (SS) and soluble COD in effluents kept always a satisfactory level of 10 and 15 mg/L with sufficient biodegradation. It was recommended to apply a dynamic SO under variable influent COD loadings and temperature conditions to the activated sludge system without excess sludge production for saving energy as well as system stabilization.
一个中试规模的活性污泥系统与污泥臭氧化工艺相结合,在冬季运行了112天,未进行剩余污泥排放。该工艺的概念是,产生的剩余污泥首先通过臭氧氧化进行分解,然后再循环至生物反应器,以使颗粒状和溶解性有机化合物矿化。运行的基础是确定每天臭氧氧化的污泥最佳量(以千克悬浮固体计,即SO),或者在进水化学需氧量(COD)负荷和温度条件变化的情况下确定最佳臭氧化频率,因为臭氧供应会消耗昂贵的能源。利用理论估算的污泥产率(SP)和实验获得的臭氧化频率(n)来获得最佳SO。虽然SP主要受COD负荷影响,但污泥浓度受冬季温度变化的影响。在15摄氏度左右观察到最佳n在2.5至2.7之间,但在10摄氏度时增加了一倍。在15摄氏度时,生物反应器中的混合液悬浮固体(MLSS)浓度稳定在5000毫克/升左右,但MLSS的挥发性部分固定在0.7左右,表明没有明显的无机积累。通过充分的生物降解,出水的悬浮固体(SS)和溶解性COD始终保持在令人满意的10毫克/升和15毫克/升水平。建议在进水COD负荷和温度条件变化的情况下,对无剩余污泥产生的活性污泥系统应用动态SO,以节省能源并实现系统稳定。