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The aerobe of aerobic sewage liquid in summer were significant more than that in spring.②The anaerobe and anaerobe facultative of anaerobic sewage liquid in autumn were notablely significant more than that in winter.

2冬季厌氧沼液的厌氧培养和需氧培养的细菌数量,均极显著低于秋季;冬季好氧沼液中的需氧培养出的细菌数,显著低于秋季。

The results showed that:①The anaerobe and anaerobe facultative of anaerobic sewage liquid in summer were notablely significant more than that in spring.

结果表明:(1)夏季厌氧沼液中厌氧菌及兼性细菌数量均极显著高于春季;夏季好氧沼液中好氧菌数量显著高于春季。

Magnetic Upper-flowing Anaerobic Fluidized Bed Reactor of sulphate reducing phase and Magnetic Aerobic Fluidized Bed Reactor of biological desulfurizing phase in this technological process filled with Magnetic Hollow porous Polystyrenemicrophere were economical and actable.

3工艺中硫酸盐还原相为以N_2吹脱、磁性多孔聚苯乙烯微球为填料的磁性上流式厌氧生物膜流化床——厌氧反应器,生物脱硫相为以磁性多孔聚苯乙烯微球为填料的磁性上流式好氧生物膜流化床—好氧反应器是经济可行的。

In biodegradation study, debromination of 4-monobrominated diphenyl ether (4-BDE) is investigated with aerobic and anaerobic sludges. This also is the first report demonstrating microbaially mediated biodegradation of 4-BDE under aerobic conditions. 4-BDE biodegraded within 11 days by 68 % and 83 % with toluene and diphenyl ether, respectively, as second carbon sources to stimulate biodegradation.

本研究之生物降解部分,以酒厂之好氧及厌氧活性污泥及经PCE驯化之厌氧活性污泥能有效降解一溴联苯醚(4-mono-BDE, 4-BDE),结果证实了在好氧情况下微生物降解PBDEs的可行性,而补助碳源的添加有助於提高降解速率,在甲苯或联苯醚存在的情况下,11天内4-BDE分别降解了68 %及83 %。

An anaerobic-aerobic intermittent CSTR process was used to decolorize mixed dye with E. coli NO3 strain at a hydraulic retention time of 32, 18, and 10 h. The color-removal efficiency was around 70 ~ 80%. Under steady operation for over 117 h, the total decolorization was 10900, 18200, and 7590 for HRT=32, 18, and 10 h, respectively. After repeated operation cycles, the decolorization rate of E. coli NO3 was always higher than the original cycle. This may be attributed to the acclimation effect since the E. coli NO3 cells were repeatedly exposed to the azo dye.

NO3於HRT = 10、18、32小时之条件下进行厌氧-好氧间歇式CSTR生物反应器褪色操作,褪色率可以达到7080﹪左右;在约117小时的稳定褪色操作下,总褪色量分别为10900、18200及7590,这显示NO3在长时间之间歇式CSTR褪色操作下,不但稳定且具有优异之褪色能力;若将一组好氧、厌氧步骤视为一个循环去探讨褪色率之变化,则可观察到随著循环次数增加其褪色率逐次上升,之后则明显下降,这与摇瓶重复批次实验相似之结果,也可以解释为驯养效应所导致。

Results: Pericoronitis was a complex odontogenic infection with aerobic bacteria and anaerobic bacteria.

结果:冠周炎为需氧菌和厌氧菌的混合感染,药物敏感试验显示氯林可霉素对需氧菌和厌氧菌均有显著的抑制作用。

A system for the treatment of organic containing waster water is provided, comprising an anaerobic bioreactor, an aerobic bioreactor disposed rearwardly of the anaerobic bioreactor, and a membrane separation reactor disposed rearwardly of the aerobic bioreactor.

一种含有机污染物之废水处理系统,包含一厌氧反应槽,一好氧反应槽,及一薄膜分离槽;其中前述好氧反应槽系设置於厌氧反应槽之后,前述薄膜分离槽系设置於前述好氧反应槽之后,该系统系利用生物处理法去除废水中的有机污染物,并以薄膜分离固液两相。

The special composition and structure of the AGS cause the sludge has some oxygen tolerance, which is affected by various factors. The AGS would tolerance 0.5h aerates without obvious activity loses.

厌氧颗粒污泥的组成和结构使得它具有一定耐氧活性,对厌氧颗粒污泥的耐氧活性而言,最佳曝氧时间为0.5h。

The fifty-year history of anaerobic biotechnology for industry wastewater treatment has proved that the development of high-rate anaerobic reactors is extremely important.

厌氧生物技术成功应用于工业废水处理的五十多年历史证明:高负荷厌氧反应器技术是厌氧生物处理技术发展的核心。

Organization: College of Environmental Science and Engineering, Guilin University of Technology;State Key Laboratory of Environmental Engineering and Protected Assessment in GuangxiAbstract: Anaerobic granular sludge was rapidly cultivated in a sequencing batch reactor using glucose and steaming process waste water as carbon source, and anaerobic granular sludge in well-operated upflow anaerobic sludge blanket reactor and aerobic activated sludge as inoculation sludge.

摘 要:在序列间歇式活性污泥法(sequencing batch reactor, SBR)反应器中,先后以葡萄糖和竹品蒸煮废水为碳源,用运行良好的上流式厌氧污泥床(upflow anaerobic sludge blanket, UASB)反应器中厌氧颗粒污泥和城市污水处理厂好氧活性污泥为接种泥,在充氧条件下快速培养好氧颗粒污泥。

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