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降解     
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  degradation
    Synthesis, Characterization of Nanosize TiO_2 Composite and Its Application for Photocatalytic Degradation of Biorefractory Organic Compounds
    纳米TiO_2复合物的合成、表征及其处理难降解有机污染物的研究
短句来源
    Study on the Character and Mechanism of Degradation of Lignin in Paper Industry Black Liquor with Efficient Bacteria
    高效菌降解造纸黑液木质素的特性与机理研究
短句来源
    Study on the Degradation of Four Pesticides in Environmental Water
    四种农药在环境水体中降解研究
短句来源
    Degradation and Metabolism of Pesticide Abamectin in Environment
    农药阿维菌素在环境中降解和代谢研究
短句来源
    Preparation of Nanometer ZnO/SnO_2 Coupled Photocatalysts and Their Applications in Heterogeneous Photocatalytic Degradation of Organic Pollutants
    纳米ZnO/SnO_2等复合光催化剂的制备及其降解有机污染物研究
短句来源
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  degradation of
    Synthesis, Characterization of Nanosize TiO_2 Composite and Its Application for Photocatalytic Degradation of Biorefractory Organic Compounds
    纳米TiO_2复合物的合成、表征及其处理难降解有机污染物的研究
短句来源
    Study on the Character and Mechanism of Degradation of Lignin in Paper Industry Black Liquor with Efficient Bacteria
    高效菌降解造纸黑液木质素的特性与机理研究
短句来源
    Study on the Degradation of Four Pesticides in Environmental Water
    四种农药在环境水体中降解研究
短句来源
    Preparation of Nanometer ZnO/SnO_2 Coupled Photocatalysts and Their Applications in Heterogeneous Photocatalytic Degradation of Organic Pollutants
    纳米ZnO/SnO_2等复合光催化剂的制备及其降解有机污染物研究
短句来源
    Study on Catalyzing Dioxygen Degradation of Organic Pollutants in Aqueous Solutions
    催化分子氧降解水中有机污染物的研究
短句来源
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  degrading
    Non-cellulose Degrading Property of Erwinia Carotovora CXJZ95-198 and Cloning of It's manA Gene
    欧文氏杆菌CXJZ95-198非纤维素降解特性及manA基因的克隆研究
短句来源
    The degrading reaction of LZP08X accorded with Monod first-order equation. When the strain was cultured in the medium containing 400mg/L phenol,the degradation rate reached 99% in 12 hours,and the biodegradation rate constant and half lifes were 0.39 and 1.78h,respectively.
    其降解苯酚过程符合一级反应动力学方程,在苯酚初始浓度为400mg/L时,于12h内,降解率达99%,降解速率常数K值为0.39,半衰期为1.78h。
短句来源
    Using the quadratic regression model,the optimum concentrations were determined: temperature 28℃,pH value 7.0,concentration 1 500 mg/L,medium volume 100 mL and inoculum amount 10%,respectively,the predicted yield of the methamidophos degrading rate was 73.65%.
    通过对二次多项回归方程求解得知,在上述自变量取值分别为:温度28℃,pH值7.0,甲胺磷浓度1 500 mg/L,装液量100 mL,接种量10%时,甲胺磷降解率为最大,预测值为73.65%。
短句来源
    Yeast and lactobacillus had no degrading ability to PO43-and NH3-N in the wastewater.
    酵母菌、乳酸菌对黑臭河水中的PO43-和NH3-N都没有降解能力。
短句来源
    coli JM109 (containing plasmid pT7) degrading 1,2,4-TCB, the partial intermediate products were inspected and surveyed as 2,3,5-trichloromuconate, 2,5-dichloro- carboxymethylenebut-2-en-4-olide, and 2,5-dichloro-4-oxohex-2-enedioate respectively, adopting gas chromatography-mass spectrometry (GC-MS) technique.
    采用色谱/质谱联用(GC/MS)技术检测到转化子E. coli JM109(含质粒pT7)降解1,2,4-三氯苯过程中的部分中间产物分别为2,3,5-三氯-2,4-己二烯二酸、2,5-二氯-2,4-二烯-1,4-内酯-己酸、2,5-二氯-4-氧代-2-烯己二酸;
短句来源
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  degrade
    CHARACTERISTICS OF F8633 STRAINS DEGRADE POLYVINYL ALCOHOL
    F8633菌降解聚乙烯醇特性的研究
短句来源
    Synthesis and Function Proof of Graft Copolymerization Degrade Membrane of AM-AA and ST
    AM—AA与ST接技共聚降解膜材科的合成及性能表征
短句来源
    The nano-TiO_2 catalysts was used to degrade acid light yellow .
    采用纳米TiO_2光催化降解酸性嫩黄。
短句来源
    Ti400 catalyst was employed to degrade RhB, and its photocatalytic activity was kept almost the same after recycling 7 times.
    用Ti400做催化剂降解RhB,连续循环使用7次,其催化活性基本不变.
短句来源
    coli JM109, thus obtaing the ability to degrade 1,2,4-TCB. In the process of E.
    coli JM109中,转化子获得了降解1,2,4-三氯苯的能力.
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  degradation
The photocatalytic degradation of aniline on the composite films was carried out in a TiO2/UV system.
      
The photocatalytic degradation of methyl orange (MO) in aqueous solution under 365 nm irradiation on TiO2 and Ag/TiO2 thin films was investigated.
      
The thermo-oxidative degradation of the films is studied by thermogravimetric analysis (TGA).
      
For three tested samples, under UV illumination CCT01 has the highest activity for MB photocatalytic degradation, while in the case of RB, CCT02 is the most active photocatalyst.
      
Under visible light illumination, CCT005 has the highest activity for both MB and RB photocatalytic degradation.
      
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  degradation of
The photocatalytic degradation of aniline on the composite films was carried out in a TiO2/UV system.
      
The photocatalytic degradation of methyl orange (MO) in aqueous solution under 365 nm irradiation on TiO2 and Ag/TiO2 thin films was investigated.
      
The thermo-oxidative degradation of the films is studied by thermogravimetric analysis (TGA).
      
It was found that the degradation of sodium sulfite, sodium bisulfite or sodium pyrosulfite obeyed pseudo zero-order kinetics in the buffer solutions.
      
The photocatalytic degradation of phenol showed that under visible light (λ >amp;gt; 400 nm) irradiation, the chlorine-doped TiO2 calcined at 300°C displayed the best performance, the degradation ratio of phenol was 42.5% after 120 min.
      
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  degrading
After degrading the PCL cores of the two kinds of nanospheres by lipase, the corresponding crosslinked poly(methyl acrylic acid) hollow spheres and crosslinked poly(vinyl alcohol) hollow spheres were obtained.
      
The fast algorithm presented in this paper improves the speed of the image reconstructing by approximately 32 times without degrading the reconstructed image quality.
      
It has been proven that they are both highly-efficient pyrene degrading bacteria and both Bacillus sp..
      
The effecting factors during degradation and the degrading mechanism were studied.
      
The aim of the present work was to know the location of the genes for degrading 1,2,4-trichlorobenzen.
      
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  degrade
Methanosarcina barkeri, had some acid resistance and could still degrade methanol at pH 5.0.
      
Granular sludge of the system could protect the methanogenic bacteria within its body against the impact of the acidic environment and make them degrade methanol at pH 4.5.
      
The results showed that to degrade 50 mL of 4-aminophenol whose concentration was 500 mg/L, the optimal conditions were: volume of H2O2 = 3 mL, temperature = 40-60°C and pH = 9-10.
      
The microorganisms inoculated can probably degrade the phytotoxins present in soils, thereby favoring plant development.
      
As follows from the comparison of the degrading and antioxidative effects, measurement of the antioxidant activity can be used in screening of fungi for the ability to degrade lignocellulose substrates.
      
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