Cápiro Natalie L, Löffler Frank E, Pennell Kurt D
Department of Civil and Environmental Engineering, Tufts University, Medford, MA 02155, United States.
Department of Microbiology, University of Tennessee, Knoxville, TN 37996, United States; Department of Civil and Environmental Engineering, University of Tennessee, Knoxville, TN 37996, United States; Center for Environmental Biotechnology, University of Tennessee, Knoxville, TN 37996, United States; University of Tennessee and Oak Ridge National Laboratory (UT-ORNL) Joint Institute for Biological Sciences (JIBS) and Biosciences Division, Oak Ridge National Laboratory, Oak Ridge, TN 37831, United States.
J Contam Hydrol. 2015 Nov;182:78-90. doi: 10.1016/j.jconhyd.2015.08.007. Epub 2015 Aug 22.
Effective treatment of sites contaminated with dense non-aqueous phase liquids (DNAPLs) requires detailed understanding of the microbial community responses to changes in source zone strength and architecture. Changes in the spatial and temporal distributions of the organohalide-respiring Dehalococcoides mccartyi (Dhc) strains and Geobacter lovleyi strain SZ (GeoSZ) were examined in a heterogeneous tetrachloroethene- (PCE-) DNAPL source zone within a two-dimensional laboratory-scale aquifer flow cell. As part of a combined remedy approach, flushing with 2.3 pore volumes (PVs) of 4% (w/w) solution of the nonionic, biodegradable surfactant Tween® 80 removed 55% of the initial contaminant mass, and resulted in a PCE-DNAPL distribution that contained 51% discrete ganglia and 49% pools (ganglia-to-pool ratio of 1.06). Subsequent bioaugmentation with the PCE-to-ethene-dechlorinating consortium BDI-SZ resulted in cis-1,2-dichloroethene (cis-DCE) formation after 1 PV (ca. 7 days), while vinyl chloride (VC) and ethene were detected 10 PVs after bioaugmentation. Maximum ethene yields (ca. 90 μM) within DNAPL pool and ganglia regions coincided with the detection of the vcrA reductive dehalogenase (RDase) gene that exceeded the Dhc 16S rRNA genes by 2.0±1.3 and 4.0±1.7 fold in the pool and ganglia regions, respectively. Dhc and GeoSZ cell abundance increased by up to 4 orders-of-magnitude after 28 PVs of steady-state operation, with 1 to 2 orders-of-magnitude increases observed in close proximity to residual PCE-DNAPL. These observations suggest the involvement of these dechlorinators the in observed PCE dissolution enhancements of up to 2.3 and 6.0-fold within pool and ganglia regions, respectively. Analysis of the solid and aqueous samples at the conclusion of the experiment revealed that the highest VC (≥155 μM) and ethene (≥65 μM) concentrations were measured in zones where Dhc and GeoSZ were predominately attached to the solids. These findings demonstrate dynamic responses of organohalide-respiring bacteria in a heterogeneous DNAPL source zone, and emphasize the influence of source zone architecture on bioremediation performance.
有效处理受致密非水相液体(DNAPL)污染的场地需要详细了解微生物群落对源区强度和结构变化的响应。在二维实验室规模的含水层流动池中,研究了异质四氯乙烯(PCE)-DNAPL源区内有机卤呼吸型脱卤球菌属麦氏菌株(Dhc)和洛氏地杆菌SZ菌株(GeoSZ)的时空分布变化。作为联合修复方法的一部分,用2.3孔隙体积(PV)的4%(w/w)非离子、可生物降解表面活性剂吐温80溶液冲洗,去除了51%的初始污染物质量,并导致PCE-DNAPL分布中包含51%的离散节和49%的油藏(节与油藏的比例为1.06)。随后用PCE到乙烯的脱氯联合体BDI-SZ进行生物强化,在1 PV(约7天)后形成顺式1,2-二氯乙烯(cis-DCE),而在生物强化10 PV后检测到氯乙烯(VC)和乙烯。DNAPL油藏和节区域内的最大乙烯产量(约90μM)与vcrA还原脱卤酶(RDase)基因的检测结果一致,该基因在油藏和节区域分别比Dhc 16S rRNA基因高出2.0±1.3倍和4.0±1.7倍。在28 PV的稳态运行后,Dhc和GeoSZ细胞丰度增加了多达4个数量级,在残留PCE-DNAPL附近观察到增加了1至2个数量级。这些观察结果表明这些脱氯剂参与了在油藏和节区域分别观察到的高达2.3倍和6.0倍的PCE溶解增强过程。实验结束时对固体和水样的分析表明,在Dhc和GeoSZ主要附着在固体上的区域测量到最高的VC(≥155μM)和乙烯(≥65μM)浓度。这些发现证明了异质DNAPL源区内有机卤呼吸细菌的动态响应,并强调了源区结构对生物修复性能的影响。