针对制革废水高COD、高总氮的问题,提出了基于上流式厌氧污泥床(UASB)、上流式反硝化污泥床(UDNSB)、生物接触氧化池的生物处理组合工艺,进行了为期321 d的现场中试研究。研究结果表明,对于COD、TN、NH_4^+-N平均浓度分别为2 740、278和...针对制革废水高COD、高总氮的问题,提出了基于上流式厌氧污泥床(UASB)、上流式反硝化污泥床(UDNSB)、生物接触氧化池的生物处理组合工艺,进行了为期321 d的现场中试研究。研究结果表明,对于COD、TN、NH_4^+-N平均浓度分别为2 740、278和193 mg·L^(-1)的制革废水,在硝化液回流比R为300%,UASB反应器、UDNSB反应器、生物接触氧化池的水力停留时间(HRT)分别为11、22和57 h,平均容积负荷分别为5.63 kg COD·(m^3·d)^(-1)、0.30 kg TN·(m^3·d)^(-1)和0.11 kg NH+4-N·(m^3·d)^(-1)的条件下,该组合工艺处理出水COD、TN和NH_4^+-N的平均浓度分别为190、69.8和4.6 mg·L^(-1),其平均去除率分别达到92%、73%和97%以上。展开更多
Kinetics of municipal sewage degradation in Expanded Granular Sludge Bed(EGSB)and Up-flow Anaerobic Sludge Blanket(UASB)reactors at 10℃ were investigated via continuous experimental equipments.The results indicated t...Kinetics of municipal sewage degradation in Expanded Granular Sludge Bed(EGSB)and Up-flow Anaerobic Sludge Blanket(UASB)reactors at 10℃ were investigated via continuous experimental equipments.The results indicated that the whole reaction process can be simulated by the first-order dynamic equation model.Dynamic parameters such as k,Vmax and Ks of UASB in hydrolysis acidification stage were 1.08 d-1,2.8 d-1 and 372 mg/L comparing to those of 1.18 d-1,3.5 d-1 and 112 mg/L in the methanogenesis stage respectively.The EGSB’s k,Vmax and Ks were 2.91 d-1,14.3 d-1 and 470 mg/L in the hydrolysis acidification stage comparing to those of 1.68 d-1,6.6 d-1 and 103 mg/L in the methanogenesis stage respectively.Comparison of k values of the two stages in UASB and EGSB indicates that hydrolysis acidification stage is the controlling step for the whole reaction process of UASB,while methanogenesis stage is the controlling step in EGSB.Compared with UASB,municipal sewage treatment by EGSB at 10 ℃ can reach the same effluent requirement with lower retention time due to its effluent recirculation.展开更多
文摘针对制革废水高COD、高总氮的问题,提出了基于上流式厌氧污泥床(UASB)、上流式反硝化污泥床(UDNSB)、生物接触氧化池的生物处理组合工艺,进行了为期321 d的现场中试研究。研究结果表明,对于COD、TN、NH_4^+-N平均浓度分别为2 740、278和193 mg·L^(-1)的制革废水,在硝化液回流比R为300%,UASB反应器、UDNSB反应器、生物接触氧化池的水力停留时间(HRT)分别为11、22和57 h,平均容积负荷分别为5.63 kg COD·(m^3·d)^(-1)、0.30 kg TN·(m^3·d)^(-1)和0.11 kg NH+4-N·(m^3·d)^(-1)的条件下,该组合工艺处理出水COD、TN和NH_4^+-N的平均浓度分别为190、69.8和4.6 mg·L^(-1),其平均去除率分别达到92%、73%和97%以上。
基金This work was supported by the Project of Science and Technology Commission of Shanghai Municipality(No.042312076,062R14089)the Key Technologies Research and Development Program(No.2003BA808A17)the High Tech Research and Development(863)Program(No.2004AA649310)
文摘Kinetics of municipal sewage degradation in Expanded Granular Sludge Bed(EGSB)and Up-flow Anaerobic Sludge Blanket(UASB)reactors at 10℃ were investigated via continuous experimental equipments.The results indicated that the whole reaction process can be simulated by the first-order dynamic equation model.Dynamic parameters such as k,Vmax and Ks of UASB in hydrolysis acidification stage were 1.08 d-1,2.8 d-1 and 372 mg/L comparing to those of 1.18 d-1,3.5 d-1 and 112 mg/L in the methanogenesis stage respectively.The EGSB’s k,Vmax and Ks were 2.91 d-1,14.3 d-1 and 470 mg/L in the hydrolysis acidification stage comparing to those of 1.68 d-1,6.6 d-1 and 103 mg/L in the methanogenesis stage respectively.Comparison of k values of the two stages in UASB and EGSB indicates that hydrolysis acidification stage is the controlling step for the whole reaction process of UASB,while methanogenesis stage is the controlling step in EGSB.Compared with UASB,municipal sewage treatment by EGSB at 10 ℃ can reach the same effluent requirement with lower retention time due to its effluent recirculation.
