Institute of Marine and Environmental Technology, Department of Marine Biotechnology, University of Maryland Baltimore County, Baltimore, Maryland 21202, United States.
Environ Sci Technol. 2013 Apr 16;47(8):3807-15. doi: 10.1021/es304372t. Epub 2013 Mar 26.
Bioremediation of sediments contaminated with commercial polychlorinated biphenyls (PCBs) is potentially achievable by the sequential activity of anaerobic halorespiration to convert higher chlorinated congeners to less chlorinated congeners that are susceptible to aerobic respiratory degradation. The efficacy of bioaugmentation with anaerobic halorespiring Dehalobium chlorocoercia DF1 and aerobic Burkholderia xenovorans LB400 added concurrently with granulated activated carbon (GAC) as a delivery system was determined in 2 L laboratory mesocosms containing weathered Aroclor-contaminated sediment from Baltimore Harbor, MD, USA. The greatest effect was seen in the mesocosm bioaugmented with both DF1 and LB400 together, which resulted in an 80% decrease by mass of PCBs, from 8 to <2 mg/kg after 120 days. There was no significant increase in lesser-chlorinated congeners, indicating that both anaerobic dechlorination by DF1 and aerobic degradation by LB400 occurred. In contrast, nonbioaugmented controls containing filtered culture supernatant showed only a 25% decrease in total levels of PCBs after 365 days, which was likely due to biostimulation of the indigenous population by the medium. Direct colony counts and molecular analysis targeting a putative reductive dehalogenase gene of D. chlorocoercia or the bphA gene of LB400 showed the presence of viable DF1 and LB400 in bioaugmented mesocosms after 365 days, indicating that both nonindigenous strains were sustainable within the indigenous microbial community. These results suggest that an in situ treatment employing the simultaneous application of anaerobic and aerobic microorganisms could be an effective and environmentally sustainable strategy to reduce PCBs levels in contaminated sediment.
生物修复受商业多氯联苯 (PCBs) 污染的沉积物是可行的,通过厌氧卤呼吸的顺序活动将高氯化同系物转化为易受需氧呼吸降解的低氯化同系物。在含有来自美国马里兰州巴尔的摩港风化 Aroclor 污染沉积物的 2 L 实验室中,同时添加颗粒活性炭 (GAC) 作为输送系统,研究了添加厌氧卤呼吸脱氯菌 Dehalobium chlorocoercia DF1 和需氧伯克霍尔德菌 Burkholderia xenovorans LB400 的生物增强对 PCB 的有效性。在同时添加 DF1 和 LB400 的中试生物增强系统中效果最大,结果导致 PCB 质量减少了 80%,从 8 毫克/千克减少到 120 天后的<2 毫克/千克。低氯化同系物没有显著增加,表明同时发生了 DF1 的厌氧脱氯和 LB400 的需氧降解。相比之下,含有过滤培养上清液的非生物增强对照在 365 天后仅显示 PCB 总水平降低了 25%,这可能是由于培养基对土著种群的生物刺激。直接菌落计数和针对 D. chlorocoercia 的还原脱卤酶基因或 LB400 的 bphA 基因的分子分析表明,在生物增强的中试系统中存在存活的 DF1 和 LB400 365 天后,表明这两种非土著菌株在土著微生物群落中是可持续的。这些结果表明,采用同时应用厌氧和需氧微生物的原位处理可能是一种有效且环境可持续的策略,可以降低污染沉积物中的 PCB 水平。