Ruffini Castiglione Monica, Giorgetti Lucia, Becarelli Simone, Siracusa Giovanna, Lorenzi Roberto, Di Gregorio Simona
Department of Biology, University of Pisa, via Ghini 13, 56126, Pisa, Italy.
National Research Council (CNR), Institute of Biology and Agricultural Biotechnology (IBBA), Research Unit of Pisa, Via Moruzzi 1, 56124, Pisa, Italy.
Environ Sci Pollut Res Int. 2016 Apr;23(8):7930-41. doi: 10.1007/s11356-016-6049-y. Epub 2016 Jan 15.
Two bacterial strains, Achromobacter sp. (ACH01) and Sphingomonas sp. (SPH01), were isolated from a heavily polycyclic aromatic hydrocarbon (PAH)-contaminated soil (5431.3 ± 102.3 ppm) for their capacity to use a mixture of anthracene, pyrene, phenanthrene and fluorene as sole carbon sources for growth and for the capacity to produce biosurfactants. The two strains were exploited for bioaugmentation in a biopile pilot plant to increase the bioavailability and the degradation of the residual PAH contamination (99.5 ± 7.1 ppm) reached after 9 months of treatment. The denaturing gel gradient electrophoresis (DGGE) profile of the microbial ecology of the soil during the experimentation showed that the bioaugmentation approach was successful in terms of permanence of the two strains in the soil in treatment. The bioaugmentation of the two bacterial isolates positively correlated with the PAH depletion that reached 7.9 ± 2 ppm value in 2 months of treatment. The PAH depletion was assessed by the loss of the phyto-genotoxicity of soil elutriates on the model plant Vicia faba L., toxicological assessment adopted also to determine the minimum length of the decontamination process for obtaining both the depletion of the PAH contamination and the detoxification of the soil at the end of the process. The intermediate phases of the bioremediation process were the most significant in terms of toxicity, inducing genotoxic effects and selective DNA fragmentation in the stem cell niche of the root tip. The selective DNA fragmentation can be related to the selective induction of cell death of mutant stem cells that can compromise offsprings.
从严重受多环芳烃(PAH)污染的土壤(5431.3±102.3 ppm)中分离出两株细菌,无色杆菌属(ACH01)和鞘氨醇单胞菌属(SPH01),因其能够利用蒽、芘、菲和芴的混合物作为唯一碳源进行生长以及具有产生生物表面活性剂的能力。在一个生物堆试点工厂中利用这两株菌进行生物强化,以提高生物可利用性,并降解处理9个月后残留的PAH污染(99.5±7.1 ppm)。实验期间土壤微生物生态学的变性梯度凝胶电泳(DGGE)图谱表明,就处理土壤中这两株菌的持久性而言,生物强化方法是成功的。这两种细菌分离物的生物强化与PAH的去除呈正相关,在处理2个月后PAH去除量达到7.9±2 ppm。通过土壤浸出液对模式植物蚕豆的植物遗传毒性损失来评估PAH的去除情况,该毒理学评估也用于确定去污过程的最短时间,以实现PAH污染的去除以及过程结束时土壤的解毒。生物修复过程的中间阶段在毒性方面最为显著,在根尖干细胞生态位中诱导遗传毒性效应和选择性DNA片段化。选择性DNA片段化可能与突变干细胞的细胞死亡选择性诱导有关,这可能会影响后代。