以亚甲基蓝为目标降解物，考察了硫化温度、催化剂加入量和制备方法对亚甲基蓝降解率的影响。
Using methylene blue as the degradation object, the effects of sulfurization temperature, photocatalyst dosage and preparation method on the degradation rate of methylene blue were studied.
同时以酸性红g、直接枣红和直接大红(直接染料)及亚甲基蓝为对象模拟染料废水进行催化降解实验。
Furthermore, samples, as catalysis, were used to degrade simulation dye effluents, such as solutions of Acid Red g, Direct Bordeaux, Direct Red and Methylene Blue.
并通过亚甲基蓝溶液在可见光照射下的催化降解脱色率来表征薄膜的催化活性。
And the visible photoelectric activities of the films were characterized by degradation rate of the methylene blue under visible light.
以棉籽壳基质的三种实验室制备菌糠过滤亚甲基蓝溶液的处理效果以菌株BP 降解的菌糠效果最佳。
Of three kinds of fungi culture matter of cottonseed shell, fungi culture matter of strain BP produced the best effect in filtering the solution of methyl blue.
以降解亚甲基蓝以及降解废水中有机物来对其催化性能进行评价。
The photocatalytic activity was evaluated by photocatalytic degradation of methylene blue and photocatalytic degradation of organism in waste water.
研究了镧盐掺杂对样品相结构、晶粒尺寸和光催化降解亚甲基蓝活性的影响。
The effects of lanthanum salt-doping on the photocatalytic degradation of methylene blue in solution, phase structure and crystallite size of the TiO2 films were investigated.
该复合材料通过磁分离可反复使用，重复使用7次后，对亚甲基蓝的降解率仍大于90%。
The removal rate of methylene blue still maintains more than 90% even after repeated use for 7 times.
复合体对亚甲基蓝的降解过程适合采用一级动力学方程进行描述。
The photocatalytic degradation process of methylene blue conformd to the first-order kinetic equation.
图8为太阳光下样品对亚甲基蓝的光催化降解效果图。
Fig. 8 indicates the effect drawing of photocatalytic degradation rate of methylene blue under sunlight.
图8为太阳光下样品对亚甲基蓝的光催化降解效果图。
Fig. 8 indicates the effect drawing of photocatalytic degradation rate of methylene blue under sunlight.
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