| 1. | Microbial degradation critically affects the fate and behavior of pesticides in soil .
生物降解主要影响土壤中农药的行为和命运。 |
| 2. | The utilazation study on the microbial degradation of phenol waste
微生物降解法处理含酚废水 |
| 3. | Microbial degradation influences on heave oil characters
微生物降解作用对稠油理化性质的影响 |
| 4. | Microbial degradation of petroleum hydrocarbon
石油烃类的微生物降解 |
| 5. | Study on microbial degradation of synthetic pyrethroid insecticides
拟除虫菊酯类农药微生物降解研究进展 |
| 6. | Study on microbial degradation of bound residues of metsulfuron - methyl in soil
土壤中结合残留态甲磺隆的微生物降解研究 |
| 7. | Study on the effect of - cyclodextrin on the microbial degradation of p - nitrobenzophenol
环糊精对对硝基苯酚微生物降解的影响 |
| 8. | The results of microbial degradation of the herbicide showed that nyb1 and nyb4 had special ability to degrade the chemical from those bacteria tested in cultured media added a series volumes ( 5 - 20 % in total volume ) of bacteria suspension while the concentration of the herbicide at 50 mg / l in the media
在精喹禾灵添加浓度为50mg l的基础培养基中，分别加入液量为总体积5 20 nyb1和nyb4菌株的培养液，降解试验结果表明两种菌株均对精哇禾灵的降解作用明显。 |
| 9. | The results showed that with the increase of initial concentration of abamectin , the microbial decomposition rate increased , but higher concentration of abamectin inhibited the decomposition rate ; when the inoculation amount of dominant bacteria increased , the decomposition rate was accelerated ; two possible metabolite products were found by the analysis of tic and ms chromatogram , and possible mechanism of microbial degradation of abamectin was put forward
结果表明：在一定范围内，当底物浓度增加时，降解速率常数相应加快，但高浓度对降解速率有一定抑制作用；而随着接种量增加，降解速率逐渐加快；通过分析tic图和质谱图，可能主要有两种代谢产物，进而推测了其降解机理。 |
| 10. | It seems that micro - organism in soil played a very important role to decompose the herbicide with the results of microbial degradation , which the half - lifves of quizalofop - p - ethyl with a level of 50 mg / kg in clay and red soil were 9 . 9 and 15 . 7 days comparing with that in the two types of soil sterilized , 29 . 8 and 37 . 5 days , respectively
土壤微生物对精喹禾灵在土壤环境中的降解发挥了重要的作用。起始浓度为50mg kg的精喹禾灵在未灭菌、灭菌处理青紫泥中的降解半衰期( t1c2 )分别为9 . 9和29 . 8d ，在红壤中降解半衰期分别为15 . 7和37 . 5d 。 |
