通过选择性培养,从黄河水体中分离纯化出3株能够以苊(Chr)和苯并[a]芘(B[a]P)为唯一碳源和能源进行生长的细菌HKS-1,HKS-2和HKS-3,采用16SrDNA序列分析,初步断定HKS-1为杆菌属或无芽孢杆菌属的一个种,HKS-2和HKS-3为芽孢杆菌菌株.微生物降解实验表明,Chr和B[a]P在前25d的降解符合零级动力学规律,3株细菌的混合菌群对Chr和B[a]P有良好的降解效果,泥沙的加入能够促进微生物数量的增长,从而促进Chr和B[a]P的降解.当Chr和B[a]P的初始质量浓度风分别为15.85和12.10μg·L^-1时,培养35d后不含泥沙体系中Chr和B[a]P的降解率分别为45.79%和37.36%;含泥沙体系中Chr和B[a]P的降解率分别为58.76%和51.69%.进一步采用膜实验对比研究了多环芳烃在水相和颗粒相的降解速率.结果表明,当用零级动力学对Chr和B[a]P的质量浓度(ID)变化(最初4d)进行拟合时,Chr和B[a]P在颗粒相的降解速率分别约为其在水相降解速率的3和4倍.
Three indigenous PAHs-degrading bacterial strains HKS-1, HKS-2 and HKS-3 were obtained by selective culture from The Yellow River. Sequence analysis of 16 s rDNA showed that HSK-1 belongs to Bacterium sp., HSK-2 and HSK-3 belongs to Bacillus sp. Biodegradation experiments showed that PAHs degradation in water-sediment systems could be fitted with zero-order kineties (the first 25 days were fitted). These microbial strains degraded chrysene and benzo[a] pyrene well, the presence of particulates promoted degradation. With the initial concentrations of chrysene and benzo[a]pyrene in water/sediment systems at 15.85 and 12. 10μg. L^-1, 45.79% and 37.36% of chrysene and benzo[a]pyrene respectively were degraded after 35 d incubation without sediment; at the same time, 58.76% and 51.69% of chrysene and benzo[a]pyrene respectively in the system were degraded with sediment. Water and PAHs can cross PTFE membrane but bacteria and sediment cannot, a membrane experiment was carried out to compare the biodegradation rates of PAHs in water phase and in particulate phase. It was found that when zero-order biodegradation kinetics was fitted (the first 4 days), degradation rate for chrysene and benzo[a]pyrene at the particulate phase were three and four times of that in water phase, respectively.