Da Silva Marcio L B, Alvarez Pedro J J
Department of Civil and Environmental Engineering, Rice University, MS 317, Houston, TX 77251-1892, USA.
Appl Environ Microbiol. 2004 Aug;70(8):4720-6. doi: 10.1128/AEM.70.8.4720-4726.2004.
Methanogenic flowthrough aquifer columns were used to investigate the potential of bioaugmentation to enhance anaerobic benzene-toluene-ethylbenzene-xylene (BTEX) degradation in groundwater contaminated with ethanol-blended gasoline. Two different methanogenic consortia (enriched with benzene or toluene and o-xylene) were used as inocula. Toluene was the only hydrocarbon degraded within 3 years in columns that were not bioaugmented, although anaerobic toluene degradation was observed after only 2 years of acclimation. Significant benzene biodegradation (up to 88%) was observed only in a column bioaugmented with the benzene-enriched methanogenic consortium, and this removal efficiency was sustained for 1 year with no significant decrease in permeability due to bioaugmentation. Benzene removal was hindered by the presence of toluene, which is a more labile substrate under anaerobic conditions. Real-time quantitative PCR analysis showed that the highest numbers of bssA gene copies (coding for benzylsuccinate synthase) occurred in aquifer samples exhibiting the highest rate of toluene degradation, which suggests that this gene could be a useful biomarker for environmental forensic analysis of anaerobic toluene bioremediation potential. bssA continued to be detected in the columns 1 year after column feeding ceased, indicating the robustness of the added catabolic potential. Overall, these results suggest that anaerobic bioaugmentation might enhance the natural attenuation of BTEX in groundwater contaminated with ethanol-blended gasoline, although field trials would be needed to demonstrate its feasibility. This approach may be especially attractive for removing benzene, which is the most toxic and commonly the most persistent BTEX compound under anaerobic conditions.
采用产甲烷流通式含水层柱来研究生物强化对受乙醇混合汽油污染的地下水中厌氧苯-甲苯-乙苯-二甲苯(BTEX)降解的促进潜力。使用了两种不同的产甲烷菌群(分别富集了苯或甲苯和邻二甲苯)作为接种物。在未进行生物强化的柱中,3年内唯一降解的烃类是甲苯,不过仅经过2年的驯化就观察到了厌氧甲苯降解。仅在接种了富含苯的产甲烷菌群进行生物强化的柱中观察到了显著的苯生物降解(高达88%),并且这种去除效率持续了1年,生物强化未导致渗透率显著下降。甲苯的存在阻碍了苯的去除,甲苯在厌氧条件下是一种更易降解的底物。实时定量PCR分析表明,在甲苯降解速率最高的含水层样品中,bssA基因拷贝数(编码苄基琥珀酸合酶)最多,这表明该基因可能是用于厌氧甲苯生物修复潜力环境法医分析的有用生物标志物。在停止柱进料1年后,柱中仍能检测到bssA,这表明添加的分解代谢潜力具有稳健性。总体而言,这些结果表明,厌氧生物强化可能会增强受乙醇混合汽油污染的地下水中BTEX的自然衰减,不过还需要进行现场试验来证明其可行性。这种方法对于去除苯可能特别有吸引力,因为苯在厌氧条件下是毒性最大且通常最持久的BTEX化合物。