Institute of Applied Ecology, Chinese Academy of Sciences, Shenyang 110016, PR China.
J Hazard Mater. 2009 Dec 30;172(2-3):601-5. doi: 10.1016/j.jhazmat.2009.07.044. Epub 2009 Jul 18.
The biodegradation of polycyclic aromatic hydrocarbons (PAHs) (8.15 mg PAHs kg(-1) soil) in aged contaminated soil by isolated microbial consortium (five fungi and three bacteria) during the incubation of 64d is reported. The applied treatments were: (1) biodegradation by adding microbial consortium in sterile soils (BM); (2) biodegradation by adding microbial consortium in non-sterile soils (BMN); and (3) biodegradation by in situ "natural" microbes in non-sterile soils (BNN). The fungi in BM and BMN soils grew rapidly 0-4d during the incubation and then reached a relative equilibrium. In contrast the fungi in BNN soil remained at a constant level for the entire time. Comparison with the fungi, the bacteria in BNN soils grew rapidly during the incubation 0-2d and then reached a relative equilibrium, and those in BM and BMN soils grew slowly during the incubation of 64 d. After 64 d of incubation, the PAH biodegradations were 35%, 40.7% and 41.3% in BNN, BMN and BM, respectively. The significant release of sequestrated PAHs in aged contaminated soil was observed in this experiment, especially in the BM soil. Therefore, although bioaugmentation of introduced microbial consortium increased significantly the biodegradation of PAHs in aged contaminated soil with low PAH concentration, the creation of optimum of the environmental situation might be the best way to use bioremediation successfully in the field.
本研究报道了在 64 天的培养期内,分离的微生物群落(5 种真菌和 3 种细菌)对老化污染土壤中多环芳烃(PAHs)(8.15mgPAHs/kg 土壤)的生物降解作用。应用的处理方法有:(1)在无菌土壤中添加微生物群落进行生物降解(BM);(2)在非无菌土壤中添加微生物群落进行生物降解(BMN);(3)在非无菌土壤中利用原位“自然”微生物进行生物降解(BNN)。在 BM 和 BMN 土壤中,真菌在培养的 0-4 天内迅速生长,然后达到相对平衡。相比之下,BNN 土壤中的真菌在整个培养期间保持恒定水平。与真菌相比,BNN 土壤中的细菌在培养的 0-2 天内迅速生长,然后达到相对平衡,而 BM 和 BMN 土壤中的细菌在 64 天的培养期间生长缓慢。培养 64 天后,BNN、BMN 和 BM 中的 PAH 生物降解率分别为 35%、40.7%和 41.3%。在本实验中观察到老化污染土壤中被固定的 PAHs 大量释放,尤其是在 BM 土壤中。因此,尽管引入的微生物群落的生物增强显著提高了低浓度 PAHs 老化污染土壤中 PAHs 的生物降解率,但创造最佳的环境状况可能是成功应用生物修复技术的最佳方法。