好氧生物

所有光合细菌加上各种兼性的好氧生物和绝对的厌氧生物具有这种能力。

All the photosynthetic bacteria possess the capability in addition to various facultative aerobes and obligate anaerobes .

该方案采用了新的好氧生物厌氧生物改进后活性污泥处理方法，具有效率高；能耗低；良好的环境效益、社会效益和经济效。

The treatment adopts aerobe anaerobe actived sludge system , which has high effect , low consume of energy , good environmental benefit , society benefit and economic benefit .

缺氧&好氧生物脱氮过程中N2O的逸出规律研究

Study on the Emission of N_2O in Anoxic-aerobic Biological Nitrogen Removal Process

Cu对猪场废水厌氧&好氧生物处理的影响

Effects of Copper on Anaerobic-Aerobic Biotreatment of Swine Wastewater

工程设计中，在水解酸化反应器后应加设沉淀单元。在SBR好氧生物处理系统中，曝气反应时间宜大于6.5小时。

In the system of SBR following biological hydrolysis reactor , the aeration period should exceed 6.5 hours .

MSW好氧生物反应器与单纯好氧填埋的对比实验

Contrasting experiment between the means of MSW aerobic bioreactor landfill and that of barely aerobic landfill

好氧生物膜滤床去除COD及NH3-N的研究

Study on Removing Organic Matter and Ammonia Nitrogen with the Aerobic Biofilm Filter Bed

海河水体和表层沉积物中DDT污染物均以好氧生物降解为主。

DDTs were mainly aerobic biodegraded in water and surface sediment in Haihe River .

采用PVC弹性立体填料进行了好氧生物法脱硫的研究。

This paper describes the removal process of odious gas H 2S with the biological membrane method , which adopts PVC elastic solid filler .

采用了[BOD5]/[COD（Cr）]和呼吸速率曲线两种方法对6大类14种分散染料的好氧生物降解性能进行测试。

The aerobic degradation of the 14 disperse dyes in 6 types was tested by the way of BOD5 / COD and microbiological respiratory rate test .

在分析影响该工艺生物脱氮因素时发现：SBR反应器的DO时间分布是影响好氧生物脱氮和缺氧内碳源反硝化的重要因素；

The experiments show that dissolved oxygen is the important influencing factor of aerobic biological nitrogen removal and anoxic denitrification using endogenesis carbon .

研究了序批式水解酸化厌氧好氧生物处理工艺对NF合成制药废水的处理。

A hydrolyze acidification anaerobic aerobic process was investigated for the treatment of pharmacy wastewater from NF synthetic process by the sequencing batch reactors .

以LSAR（球形木素磺酸阳离子树脂）为载体，在升流式好氧生物流化床中，测定不同溶解氧条件下基质的COD去除率。

The matrix COD removal rate is evaluated in the aerobic fluidized bed by the carrier LSAR .

CO2是淀粉聚乙烯膜好氧生物降解的终产物，可以作为评估膜生物降解性的一个可靠指标。

CO 2 is an end product for aerobic biodegradation of starch containing polyethylene films , and it may be taken as a reliable index for assessing the biodegradability of the films .

给出了测试程序，采用峰值时间、峰高指数、IA指数作为定量评价指标，从而建立了ATP评价方法，并对46种有机物和7种废水的好氧生物降解性进行了评价。

The evaluating system ( peak time , peak height index and IA index ) is proposed to assess the biodegradability of 40 organic subStances and 7 wastewater .

好氧生物降解性试验表明，PASP属易生物降解性有机物。

By tests of aerobic biodegradation , it is concluded that PASP is a readily biodegradable polymer .

BOD5／COD（Cr）由进水的0.28左右提高到0.42左右，表明水解酸化后废水可生化性明显提高，更加有利于进行好氧生物处理。

BOD_5 / COD_ ( Cr ) changed from 0.28 to 0.42 . It is indicated that the biochemical treatability is obviously improved , which accelerates the process of subsequent aerobic treatment .

其中MSW好氧生物反应器是强制通风好氧填埋和渗滤液循环两种填埋方式有机结合体。

Through the contrasting experiment , the methods of degrading landfilled MSW and leachate are researched , and thus obtaining quite better effects from the means of MSW aerobic bio-reactor landfilling .

采用厌氧生物滤池（AF）&好氧生物接触氧化（BCO）联合工艺对合成洗涤剂（LAS）废水进行处理试验。

The anaerobic biofilter ( AF ) and aerobic biological contact oxidation ( BCO ) process have been used for treating synthetic detergent ( LAS ) wastewater .

运行结果表明：采用厌氧-好氧生物处理的CSTR工艺中的反应池和二沉池，可以实现实时运行控制和实时仿真，并具有良好的扩充性和移植性；

The result indicates that real time control and simulation of the reaction pond and the second sedimentation pond in anaerobic-aerobiotic biological treatment CSTR processing were realized .

采用测定生化呼吸线、BOD5、COD和BOD5/COD等方法，研究了几种制革常用染料在制革厂活性污泥作用下的好氧生物降解特性。

The biodegradability of the dyes under tannery activated sludge was evaluated based on the determinations of respiration curve of the activated sludge , BOD5 , COD and BOD5 / COD .

应用有机物结构－活性定量关系方法（QSAR）对杂环化合物的好氧生物降解性能与其化学结构间的关系进行定性、定量分析。

The quantitative and qualitative analysis were conducted on relativity between aerobic biodegradability and chemical structure of heterocyclic compounds by applying organics quantitative structure activity relativity ( QSAR ) .

采用Fenton反应好氧生物接触氧化工艺处理第一菊酸乙酯生产废水，确定了处理单元的设计参数；

The waste water from production of primary ethyl chrysanthemate was treated using a process of Fenton reaction & aerobic biological contact oxidation . The design parameters of treating units were determined .

建立了实验室小型水解酸化-好氧生物处理系统，研究了不同工艺条件下系统对染料和COD（Cr）的去除效果，并对处理系统内微生物群落结构进行解析；

Laboratory tests of hydrolysis ( acidiflcation ) - aerobic biological treatment process were conducted and removal efficiencies of dyes and COD_ ( Cr ) under different technical conditions were investigated . In addition , microbial community structures of systems were analyzed .

在与间歇流CASS工艺的实际平行运行中，复合好氧生物工艺体现了全面的优越性，对于高浓度难降解废水的处理采用复合好氧生物技术更为合理。

In a contrast of parallel running to batch-flow CASS technology , hybrid aerobic bio-reactor showed its all-around advantages , which is more suitable for high-concentrated and difficultly biodegradable wastewater treatment .

在滤速为0·4&1·2m·h-1范围内，好氧生物炭滤池的TOC去除率高于厌氧生物滤池，TN去除率低于厌氧生物滤池。

In the range of 0.4 & 1.2 m · h ~ - 1 , the TOC removal in aerated filter was higher than in anaerobic filter , but the TN removal is reverse .

TA占碱减量印染废水COD的40～78%，平均为55%，TA的可好氧生物降解性决定了碱减量印染废水处理工艺有必要以好氧生物法为核心。

TA made up 40-78 % of the total COD of alkali-minimization dyeing printing wastewater , the mean is 55 % . The biodegradation characteristic of TA illustrated that aerobic biological system should be in charge of this kind of wastewater treatment .

缺氧-好氧生物滤池中高效菌对活性红KN-3B的降解特性

Biodegradation behavior of reactive red KN-3B by highly effective decolorizing strain in anaerobic-aerobic biofilter

采用城市污水处理厂的活性污泥做菌源，在实验室条件下研究了对苯二甲酸（TA）和乙二醇（EG）的好氧生物降解性能，着重考察了EG对TA好氧生物降解性能的影响。

The aerobic biodegradability of terephthalic acid ( TA ) and ethylene glycol ( EG ), especially the effect of the added EG on the biodegradability of TA , were studied in the lab condition with mixed culture from activated sludge of WWTP .

研究了投加多孔软性填料后乳品废水好氧生物处理过程中COD的变化，试验结果表明，加入多孔软性填料，乳品废水中有机污染物的降解速率显著增加；

Studied the COD changes after addition of soft stuffing with pores in the processes of the aerobic treatment of dairy wastewater . The results of experiments show that after adding soft stuffing with pores , the speed of decomposition of organic pollutants is observably enhanced ;