ammonify vt.使生氨；給…加氨。vi.進行氨處理，成氨。
vt. 使生氨；給…加氨。 vi. 進行氨處理，成氨。 “ammonifying“ 中文翻譯： 氨化; 加氨的“ammonifiers“ 中文翻譯： 氨化菌; 氨化細菌“ammonifying bacteria“ 中文翻譯： 氨化菌; 氨化細菌; 成氨菌; 生氨菌“ammonifier“ 中文翻譯： 氨化菌; 氨化細菌“ammonifying capacity“ 中文翻譯： 氨化強度“ammonificator“ 中文翻譯： 氨化菌; 氨化器; 氨化細菌“ammonifying proce“ 中文翻譯： 氨化過程“ammonification bacteria“ 中文翻譯： 氨化細菌“ammonifying process“ 中文翻譯： 氨化過程“ammonification“ 中文翻譯： n. 1.加氨(作用)。 2.(分解)成氨(作用)。
ammonite |
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On the base of degrading effect of cm , the paper investigated the correlation between microorganisms and nutrient salt in the water body . it showed that the correlation between ammonifying bacteria and nh3 - n was 0 . 74 ; the correlations between nitrifying bacteria , denitrifying bacteria and no _ ( 3 ) - n were 0 . 65 , - 0 . 53 , respectively . the correlation between phosphorus bacteria and po _ ( 4 ) ~ ( 3 ) p was 0 . 76 根據復合微生物對水質的降解效果，選擇其使用量為2g時，對水體中微生物功能菌群與營養鹽含量的相關性進行了研究，其中氨化菌與氨氮，硝化菌與硝氮，磷細菌與磷酸鹽均成正相關關系，相關性r分別為0 . 74 ， 0 . 65 ， 0 . 76 。 |
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1 . ecological effects of long - term organophasphate pesticides contamination on soil microflora the long - term effects of organophosphate pesticides contamination on soil microflora were investigated in the present study . little difference in total counts of bacteria , actinomycetes and fungi was observed between the contaminated and the non - contaminated soil . compared with the control there were a slight decrease in total counts of free - living nitrogen - fixer and denitrifying bacteria and a significant increase in those of ammonifying and ammonia - oxidizing and nitrifying _ bacteria in the methylparathion contaminated soil 一、甲基對硫磷長期污染對土壤微生物的生態學效應研究了有機磷農藥甲基對硫磷長期污染對土壤微生物的影響，實驗表明：土壤細菌、放線菌、真菌總的數量影響不大；自生固氮菌和反硝化細菌數量減少；氨化細菌、亞硝化細菌、硝化細菌的數量在污染土壤中卻有所增加；與對照土壤相比，污染土壤呼吸作用下降了29 . 93 ；氨化作用和硝化作用強度得到增強。 |
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2 . the population of functional bacteria in water body varied with adding cm . when the use of cm was 4g , the amount of the total bacteria and phosphorus bacteria were maximum in the fourth day , the amount of denitrifying bacteria were maximum in the tenth day ; when the use of cm was 1g , the amount of ammonifying bacteria were maximum 復合微生物的加入引起水體中的微生物功能菌群數量變化，其中復合微生物添加量為4g時，實驗第4天，總菌和磷細菌達到最高峰，第10天，反硝化菌達到最高峰；當復合微生物添加量為1g時，實驗第4天氨化菌達到最高峰。 |
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The population distribution of physiological groups of bacteria ， including ammonifying bacteria , denitrifying bacteria , nitrobacteria and nitroso bacteria , organic phosphate dissolving bacteria and inorganic phosphate dissolving bacteria in water body and sediment of suzhou creek are studied with mpn and flat account method from jan . 2002 to mar . 2003 . the role of these physiological groups of bacteria in suzhou creek aquatic ecosystem is discussed 用最大可能數( mpn )法和平板計數法，于2002年1月2003年3月對蘇州河水體和底泥中的主要微生物功能菌群? ?包括有機磷分解菌、無機磷分解菌、氨化菌、亞硝化菌、硝化菌和反硝化菌等進行了生態調查，并分析探討了它們在蘇州河水生態系統中的作用。 |
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The factors which affect the growth and function of ammonifying bacteria in suzhou creek are studied with altering the environmental conditions 通過改變氨化菌生長的環境條件，對影響氨化菌生長和功能的影響因素做初步研究。 |
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In the surface layer , the dominant microbes are usually denitrifying bacteria , followed by anaerobic nitrogen fixing , ammonifying and nitrifying bacteria 土壤氮素代謝微生物高寒草甸土壤氮素代謝微生物的數量及活性在 |