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ammonia相关的网络例句

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The results showed that the percentage of ammonia oxidizing bacteria and nitrite oxidizing bacteria in the activated sludge was 15.7%±3.7% and 12.9%±3.2%, Nitrosomonas europaea-Nitrosococcus mobilis lineage were the dominant AOB, Nitrobacter spp.

结果表明,污泥中氨氧化菌的含量为15.7%±3.7%,优势菌属为Nitrosomonas europaea-Nitrosococcus mobilis;亚硝酸氧化菌的含量为12.9%±3.2%,优势菌属为Nitrobacter spp。。

In the depth surpasses in 10 meter deep well nitrogenation oven technique of manufacture, applied the multi-link graduation to enter the ammonia active nitrogen atom weaken compensation method, caused the nitrided uniformity distinct enhancement.

在深度超过10米的深井氮化炉制造技术中,应用了多环分级进氨气活性氮原子衰减补偿法,使氮化均匀性明显提高。

The well type gas nitrogenation oven uses the multi-layered multistage multi-link multi-spot assignment type ammonia input mode, enables the active nitrogen member fast evenly with the work piece surface union, forms the even fast nitrided level, the coordinate high speed spiral air flue, the effective addressing work piece blind hole and the deep hole nitriding craft, nitrides strongly by the microcomputer programmed control infiltrates, the diffusion technology heating curve.

井式气体氮化炉采用多层多段多环多点分配式氨气输入方式,使活性氮气分子能快速均匀地与工件表面结合,形成均匀快速氮化层,配合高速螺旋风道,有效解决工件盲孔和深孔地氮化工艺,由微电脑程序控制氮化强渗、扩散工艺加热曲线。

In this paper, a research was made on the treatment of nitrophenol removal ammonia wastewater from a coke-plant by sequencing batch reactors.

试验表明SBR法处理焦化废水可以取得良好的脱氮效果。在低溶解氧下,氨氮及总氮的去除效率均较高。对氮平衡的分析证实了好氧条件下也可发生反硝化作用,初步探讨了好氧反硝化的机理。

The results suggest it be possible to establish the recombination bacteria of Nitrosomonas to oxidize the ammonia in wastewater.

第二步 ,由亚硝酸盐氧化成硝酸盐;其中第一步较慢,是限制性步骤,通过亚硝酸细菌完成,而在此过程中直接起作用的酶是氨单加氧酶(ammoniummonooxygenase,AMO)。

An ammonia-oxidizing bacterial strain A5 was isolated from the activated sludge of A/O process,and identified as Nitrosomonas sp.

从厌氧好氧工艺的废水处理系统活性污泥中分离出亚硝化细菌A5 ,鉴定为亚硝化单胞菌 Nitrosomonassp。

Experimental results showed that, in this process, the optimal pH of the shortcut nitrification was 8.0~8.5; when the pH was less than 6,the nitrification is completely inhibited; when the pH was 6~7, at the end of aeration, the Nitrobacteria become the dominant bacteria because of the dropping of the free ammonia concentration. It is known to all, the activity of the Nitrobacteria and Nitrosomonas was affected by FA concentration, so nitrification was affected by FA concentration. According to the author's research results, the FA concentration which inhibit the Nitrobacteria was below 1.0mg/L,which inhibit the Nitrosomonas was above 10mg/L.

实验研究结果表明:本工艺中,短程硝化反应的最佳pH值在8.0~8.5之间,当pH小于6时,整个硝化反应都会受到抑制,当pH在6~7之间时,随着游离氨浓度的降低,在曝气后期,硝化菌将会占据优势;FA浓度对短程硝化反应的影响是通过对亚硝酸菌和硝酸菌的抑制来实现的,在本研究条件下,游离氨对亚硝酸菌的抑制浓度在10mg/L以上,对硝酸菌的抑制浓度在1.0mg/L以下;温度对短程硝化反应的影响是双重的,既影响微生物的生理活性,又影响FA浓度。

The results showed that when ammonia nitrogen was concerned, the natural start-up finished accomplished within 9 days after the initially difficult period (20d). The MBR exhibited the stable removal of NH3-N with an average efficiency of 89.4% after the maturity of nitrosomonas group in the bioreactor.

结果表明,对于NH3-N在初始困难阶段(20d)之后,系统的自然启动可以在9d内完成;之后MBR一直保持着稳定的NH3-N去除效率(89.4%)。

Being the core of signal sample module, the bioelectrode converts nonelectric signal to electric signal by PAL and ammonia electrode.

以苯丙氨酸解氨酶电极为核心的信号采集模块,通过固定化生物活性酶和氨气敏电极完成由非电量导电量的转换过程。

The water quality was more stability when the dominant species was mainly Oocystis borgei in it. Ammonia nitrogen and nitrite nitrogen in the experiment pond was lower than that of the control pond.

波吉卵囊藻为主的微藻群落控制的水质较稳定,实验池氨氮和亚硝酸盐氮浓度较对照池低。

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