Frascari Dario, Pinelli Davide, Nocentini Massimo, Zannoni Arianna, Fedi Stefano, Baleani Emilia, Zannoni Davide, Farneti Angiolo, Battistelli Alfredo
Department of Chemical, Mining and Environmental Engineering, University of Bologna, Via Terracini 34, Bologna 40131, Italy.
J Hazard Mater. 2006 Nov 2;138(1):29-39. doi: 10.1016/j.jhazmat.2006.05.009. Epub 2006 May 9.
The aerobic cometabolic biodegradation of a mixture of chlorinated aliphatic hydrocarbons (CAHs) including vinyl chloride (VC), cis- and trans-1,2-dichloroethylene (cis-DCE, trans-DCE), trichloroethylene (TCE), 1,1,2-trichloroethane (1,1,2-TCA) and 1,1,2,2-tetrachloroethane (1,1,2,2-TeCA) was investigated at both 25 and 17 degrees C by means of bioaugmented and non-bioaugmented sediment-groundwater slurry microcosm tests. The goals of the study were (i) to study the long-term aerobic biodegradation of a CAH mixture including a high-chlorinated solvent (1,1,2,2-TeCA) generally considered non-biodegradable in aerobic conditions; (ii) to investigate the efficacy of bioaugmentation with two types of internal inocula obtained from the indigenous biomass of the studied site; (iii) to identify the CAH-degrading bacteria. VC, methane and propane were utilized as growth substrates. The non-bioaugmented microcosms were characterized, at 25 degrees C, by an average 18-day lag-time for the direct metabolism of VC (accompanied by the cometabolism of cis- and trans-DCE) and by long lag-times (36-264 days) for the onset of methane or propane utilization (associated with the cometabolism of the remaining CAHs). In the inoculated microcosms the lag-phases for the onset of growth substrate utilization and CAH cometabolism were significantly shorter (0-15 days at 25 degrees C). Biodegradation of the 6-CAH mixture was successfully continued for up to 410 days. The low-chlorinated solvents were characterized by higher depletion rates. The composition of the microbial consortium of a propane-utilizing microcosm was determined by 16s rDNA sequencing and phylotype analysis. To the best of our knowledge, this is the first study that documents the long-term aerobic biodegradation of 1,1,2,2-TeCA.
通过生物强化和非生物强化的沉积物 - 地下水浆液微观试验,在25℃和17℃下研究了包括氯乙烯(VC)、顺式和反式1,2 - 二氯乙烯(顺式 - DCE、反式 - DCE)、三氯乙烯(TCE)、1,1,2 - 三氯乙烷(1,1,2 - TCA)和1,1,2,2 - 四氯乙烷(1,1,2,2 - TeCA)在内的氯代脂肪烃(CAHs)混合物的好氧共代谢生物降解。该研究的目标是:(i)研究包含通常被认为在好氧条件下不可生物降解的高氯代溶剂(1,1,2,2 - TeCA)的CAH混合物的长期好氧生物降解;(ii)研究用从研究地点的本地生物质中获得的两种类型的内部接种物进行生物强化的效果;(iii)鉴定CAH降解细菌。VC、甲烷和丙烷用作生长底物。在25℃下,未进行生物强化的微观试验中,VC直接代谢的平均延迟期为18天(伴随着顺式和反式 - DCE的共代谢),甲烷或丙烷利用开始的延迟期较长(36 - 264天)(与其余CAHs的共代谢相关)。在接种的微观试验中,生长底物利用和CAH共代谢开始的延迟期明显更短(25℃下为0 - 15天)。6 - CAH混合物的生物降解成功持续了长达410天。低氯代溶剂的消耗速率更高。通过16s rDNA测序和系统发育型分析确定了利用丙烷的微观试验中微生物群落的组成。据我们所知,这是第一项记录1,1,2,2 - TeCA长期好氧生物降解的研究。