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中试SAD-ASBR系统处理含盐废水的启动与工艺特性

本站小编 Free考研考试/2021-12-31

中文关键词含盐废水厌氧序批式反应器(ASBR)厌氧氨氧化(ANAMMOX)反硝化厌氧氨氧化耦合反硝化(SAD) 英文关键词saline wastewateranaerobic sequencing batch reactor (ASBR)anaerobic ammonia oxidation (ANAMMOX)denitrificationsimultaneous ANAMMOX and denitrification (SAD)
作者单位E-mail
于德爽青岛大学环境科学与工程学院, 青岛 266071qdydsh@163.com
唐佳佳青岛大学环境科学与工程学院, 青岛 266071
张军青岛大学环境科学与工程学院, 青岛 266071
王晓霞青岛大学环境科学与工程学院, 青岛 266071elainewangxx@163.com
赵红武汉凯迪电力环保有限公司, 武汉 430023
韩长民武汉凯迪电力环保有限公司, 武汉 430023
孙捷武汉凯迪电力环保有限公司, 武汉 430023
中文摘要 采用ASBR(530 L)接种A2/O厌氧污泥,考察了厌氧氨氧化(ANAMMOX)的启动及其与反硝化耦合处理含盐废水的脱氮特性,并对菌群结构进行了分析.结果表明,温度35℃±1℃、反应时间为14 h,160 d可实现ANAMMOX的成功启动.稳定运行阶段,ANAMMOX与反硝化耦合(SAD)使得总氮(TN)去除率和去除负荷分别达91.1%和0.45 kg·(m3·d)-1;污泥呈浅红色颗粒状,厌氧氨氧化菌为优势菌,且主要菌属为Candidatus Brocadia(10.6%).此外,采用按梯度逐步提高盐度的驯化方式,可实现SAD对高盐(Cl-浓度8000 mg·L-1)模拟火电厂废水的高效脱氮除碳,COD和TN去除率分别达93.2%和90.0%.推测SAD中反硝化主要为NO3--N→N2,部分反硝化(NO3--N→NO2--N)仅占30.3%. 英文摘要 A pilot scale anaerobic sequencing batch reactor (ASBR, working volume 530 L), inoculated by anaerobic sludge from an A2O process, was developed to investigate the start-up of anaerobic ammonia oxidation (ANAMMOX) and its combination with denitrification for deep-level nitrogen removal from saline wastewater. Simultaneously, the flora structure was analyzed. Results showed that under the conditions of temperature 35℃±1℃ and reaction time 14 h, ANAMMOX was successfully started-up after 160 days of operation. During the stabilized operation stage, ANAMMOX coupled with denitrification (SAD) led to a total nitrogen (TN) removal efficiency and removal rate of 91.1% and 0.45 kg·(m3·d)-1, respectively. The successful cultivated sludge formed granules and presented as a light red color, with the main bacteria genus being Candidatus Brocadia (10.6%). Additionally, high efficiency nitrogen and organic carbon removal (COD and TN removal efficiency of 93.2% and 90.0%, respectively) from wastewater simulating desulfurization and denitrification tailings with high salinity (Cl- concentration of 8000 mg·L-1) was achieved in the SAD system by gradually increasing the salinity gradient. Moreover, the denitrification in SAD was mostly NO3--N→N2, with partial denitrification (NO3--N→NO2--N) accounting for only 30.3%.

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