好氧微生物

  • 网络Aerobe;aeromicrobe;Aerobic micro-organism
好氧微生物好氧微生物
  1. 在实验过程中,废水中的有机物,由生物膜中的好氧微生物与厌氧微生物菌群作为营养源而消耗;

    The organic materials in wastewater were consumed as nutritious source of biofilm , consisting of aerobes and anaerobes .

  2. 堆肥过程中,物料的pH值在堆体中好氧微生物生命活动适宜的范围内变化。堆肥过程中不需要调节pH值;

    PH of composting material range around what the microorganism are suitable to , and pH is not necessary to be adjusted ;

  3. 对照组由于较低的乳酸菌含量,较高的pH值,青贮酸度低,抑制好氧微生物的作用较弱,故黄曲霉毒素含量最高。

    Control barely inhibited aerobic microorganism due to a low lactic acid bacterial content , high pH value and low acidity which resulted the highest aflatoxin content .

  4. 在本试验条件下,影响罗布麻好氧微生物脱胶的因素主要有初始pH值、浴比、温度、脱胶时间、初始菌量、摇床转速、含氮添加剂。

    Initial pH value , bath ratio ( the material-to-liquor ratio ), temperature , degumming time , rotational speed of oscillator , initial quantity of bacteria and nitric additives are the main factors to Apocynum venetum degumming with aerobe . Through experiments their influences are researched by one by one .

  5. 环境激素邻苯二甲酸二丁基酯的好氧微生物降解

    Aerobic degradation of an endocrine-disrupting chemical , di-n-butyl phthalate by microorganism

  6. 好氧微生物净化污水的机理与实践

    The Mechanism and Practice of Aerobic Microorganism in Wastewater Purification

  7. 好氧微生物颗粒污泥脱氮机理

    The Mechanism of Nitrogen Removal by Aerobic Granular Sludge

  8. 基质上层好氧微生物数量显著大于中下层基质;

    The microbe in upper level of substrate was higher than lower one .

  9. 间苯二甲酸二甲酯的好氧微生物降解及其生化途径

    Aerobic biodegradation of an endocrine-disrupting chemical , dimethyl isophthalate , and its biochemical pathway

  10. 因为好氧微生物惟有在氧气足够的环境下才能发挥消化代谢污泥的效用。

    Aerobic bio-systems readily digest waste sludge but only when sufficient oxygen is present .

  11. 固定化好氧微生物细胞的供氧问题

    Oxygen Supply in Immobilized Aerobic Cells

  12. 中试秸秆沼气发酵好氧微生物生理群的时空动态

    Spatial and temporal dynamics of aerobic physiological microorganism during pilot biogas fermentation with crop straw feed

  13. 许多有机氯代物都能对抗好氧微生物的降解代谢,主要是由于氯位取代阻止了氧化酶的攻击。

    Many of these compounds were resistant to aerobic microbial metabolism often because the chlorine substitution blocked oxygenase attack .

  14. 在这个过程中,起主要作用的是附着在填料表面的好氧微生物的降解作用;

    In this process , decomposition is mostly under the act of aerobic microorganisms , inserted on the surfaces of stuffing ;

  15. 结果表明,上行流和下行流池0~10cm的基质层中好氧微生物数量高出30~55cm的层面1~2个数量级;

    Aerobic microorganisms amount in 0 ~ 10cm substrate of up-flow and of down-flow ponds were higher with 1 ~ 2 magnitudes than that in 30 ~ 55cm substrate ;

  16. 厌氧好氧微生物菌群通过固定化在微环境中有效的结合在有限供氧条件下能完全彻底降解高氯代芳香化合物。

    These results suggested immobilization of anaerobic and aerobic microbial communities under oxygen-limited conditions might be employed as an optimal strategy to mineralize more highly chlorinated aromatic compound with low final TOC concentrations .

  17. 结果表明,采用空气辅助(液气比1:10)激活好氧微生物,经过36天的培养驱替,残余油采收率提高了4.7%;

    The results showed that the oil recovery from residual oil had been increased by 4.7 % after 36 days culture by adopting air-assistant technique ( liquid / air 1:10 v : v ) .

  18. 其中80%左右为厌氧微生物,如光合细菌、硫酸盐还原细菌、反硝化细菌、产甲烷菌等等。它们参与新陈代谢的酶系与海洋好氧微生物有显著差异。

    And about 80 % are anaerobic ones , such as photosynthetic bacteria , sulfate-reducing bacteria , denitrifying bacteria , methane-producing bacteria , etc. The enzymatic system of metabolism is big different between marine aerobic microorganisms and anaerobic ones .

  19. 生物能力学原理在红麻好氧性微生物脱胶中的应用

    Application of Bioenergetic Principle in the Microbial Retting of Kenaf Fibers

  20. 接下来对好氧性微生物脱胶的影响因素进行了研究。

    After defining bacteria , the factors affecting the bacterial degumming are studied .

  21. 通过对微生物脱胶的原理及各种胶质降解的途径的研究,得出好氧性微生物脱胶优于厌氧性微生物胶质。

    And then through studying the principle of bacterial degumming and the course of decomposition , draw the conclusion that aerobic degumming is better than anaerobic degumming .

  22. 土壤中施用了杀菌剂多菌灵以后,与对照土壤比较,土壤好氧性微生物及各生理类群的微生物数量发生显著变化。

    After bactericide carbendazim was applied to soil , the results are compared with control soil ( without carbendazim ): The number of soil aerobic microorganism and all kinds of physiological microorganisms were markedly changed .

  23. 碳源对SBR单级好氧工艺中微生物摄磷能力的影响及其机理研究

    Effect and mechanism of carbon sources on phosphorus uptake by microorganisms in sequencing batch reactor with single-stage oxic process

  24. 针对有效微生物群(EM)中含有好氧和厌氧微生物的特点,采用SBR反应器,进行了用EM处理食品废水的试验研究。

    Considering the characteristic of effective microorganism ( EM ) containing aerobic and anaerobic microorganisms , using sequences batch reactor ( SBR ) process technology , EM was adopted to treat food wastewater .

  25. 外源接种粪便好氧堆肥的微生物相变化研究

    Study of Variation of Microbes in Night Soil Aerobic Composting

  26. 污泥好氧堆肥主要微生物类群及其生态规律

    Research on Main Microorganism Groups and Their Ecological Law im Aeration Sludge Composting Process

  27. 好氧脱氮微生物的混合培养条件

    Mixed culture conditions of novel aerobic denitrifying bacteria

  28. 另外,对高温好氧堆肥中微生物的生长特征和动力学还进行了研究,发现微生物的生长受温度影响很大,随温度变化呈波动性变化。

    It was considered that the growth of microorganism was affected largely by temperature . It showed wave change of growth of microorganism alone with temperature change .

  29. 用实验数据与模型计算值进行验证比较,模型计算与实验结果拟合良好,模型正确地反映了高温好氧堆肥中微生物的生长过程及其动力学机制。

    The model was scientific according to its numerical simulation results being consistent with experiment results and rightly reflected the growth rule of microorganism in the aerobic thermophilic composting .

  30. 好氧颗粒污泥微生物量密集、粒径大、结构致密、耐冲击负荷,具有同步脱氮除磷功能。

    Aerobic granular sludge have a higher biomass concentration , with big particle size , tense structure compact , and ability to withstand shock loadings , ability to remove nitrogen and phosphates simultaneous .