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硫磺和黄铁矿为填料的生物滤池自养反硝化强化处理二沉尾水
引用本文:李芳芳,施春红,周北海,李海波.硫磺和黄铁矿为填料的生物滤池自养反硝化强化处理二沉尾水[J].环境科学研究,2016,29(11):1693-1700.
作者姓名:李芳芳  施春红  周北海  李海波
作者单位:1.北京科技大学土木与环境工程学院环境工程系, 北京 100083 ;工业典型污染物废物资源化处理北京市重点实验室, 北京 100083
基金项目:国家海洋公益性行业科研专项(201405035)
摘    要:采用硫自养反硝化工艺处理模拟污水厂二沉尾水,分别以硫磺/白云石、黄铁矿/白云石为填料,考察不同填料下生物滤池的脱氮除磷效果.结果表明,在HRT(水力停留时间)为1 h的条件下,硫磺/白云石反应器在10 d内能迅速启动,出水ρ(NO3--N)小于1.00 mg/L,去除率高达99%,反应器的最佳实际HRT为45 min.进水中的DO对硫磺/白云石反应器反硝化效果没有明显影响,但会对黄铁矿/白云石反应器的反硝化效果产生影响.去除进水中的DO后,在HRT为4 d下,黄铁矿/白云石反应器出水NO3--N和TP的质量浓度分别为10.31和0.10 mg/L,其去除率分别为67.2%和90.7%.采用高速水流反冲洗后,两个反应器的脱氮效果均能在2 d内迅速恢复.在12 ℃的低温条件下,硫磺/白云石和黄铁矿/白云石反应器的处理效果均变化不大.去除一定量的NO3--N时,硫磺/白云石反应器的SO42-生成量与理论值相符合,黄铁矿/白云石反应器的略高于理论值.研究显示,硫磺/白云石体系可有效去除二沉尾水中的NO3--N,而黄铁矿/白云石体系具有同时脱氮除磷的功能. 

关 键 词:硫自养反硝化    硫磺/白云石    黄铁矿/白云石    二沉尾水    脱氮除磷    反冲洗
收稿时间:2016/6/2 0:00:00
修稿时间:2016/7/4 0:00:00

Enhanced Treatment of Secondary Effluent via Autotrophic Denitrification Biofilter Process Using Sulfur and Pyrite as Fillings
LI Fangfang,SHI Chunhong,ZHOU Beihai and LI Haibo.Enhanced Treatment of Secondary Effluent via Autotrophic Denitrification Biofilter Process Using Sulfur and Pyrite as Fillings[J].Research of Environmental Sciences,2016,29(11):1693-1700.
Authors:LI Fangfang  SHI Chunhong  ZHOU Beihai and LI Haibo
Affiliation:1.College of Civil and Environmental Engineering, Beijing University of Science and Technology, Beijing 100083, China ;Beijing Key Laboratory of Resource-Oriented Treatment of Industrial Pollutants, Beijing 100083, China2.College of Civil and Environmental Engineering, Beijing University of Science and Technology, Beijing 100083, China
Abstract:A sulfur-based autotrophic denitrification process was applied to treat the synthetic secondary effluent of a wastewater treatment plant. Sulfur/dolomite and pyrite/dolomitewere respectively usedas fillings to investigate the nutrientsremoval performance.Under the hydraulic retention time(HRT) of 1 h, the sulfur/dolomite reactor started up quickly within ten days, which resulted in the effluent concentrations of NO3--N being less than 1.00 mg/L, representing above 99% nitrate removal. Meanwhile, the optimal HRT of the sulfur/dolomite system was 45 min. The dissolved oxygen(DO) in the influent could not affect the denitrification performance of the sulfur/dolomite reactor, but it could affect the performance of the pyrite/dolomite reactor. After removing the DO in the influent, the NO3--N and TP effluent concentrations in the pyrite/dolomite reactor were 10.31 and 0.10 mg/L under the HRT of 4 d, with the corresponding removal rates of 67.2% and 90.7%, respectively. Using high speed water flow backwashing, nitrogen removal efficiency in the two reactors could be restored quickly in two days. At the low temperature of 12 ℃, the removal performances of the two reactionsystems were not sensitive to temperature. The production of sulfate in the sulfur/dolomite reactor wasin accordance with the theoretical value, but it was slightly higher than the theoretical value in the pyrite/dolomite reactor. The results showed that the sulfur/dolomite system could effectively remove nitrate in the secondary effluent, and the pyrite/dolomite system could simultaneously remove nitrate and phosphorus. 
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