Snyder RA, Millward JD, Steffensen WS
Center for Environmental Diagnostics and Bioremediation, Biology Department, University of West Florida, 11,000 University Parkway, Pensacola, FL 32514, USA
Microb Ecol. 2000 Aug;40(3):189-199. doi: 10.1007/s002480000037.
Bacterivorous protists have been recovered from pristine and contaminated aquifer environments, but the ecological role of these organisms in bioremediation strategies has not been well defined. Burkholderia cepacia G4 PR1 constitutively expresses a toluene ortho-monooxygenase (tom) due to a secondary transposition of a Tn5 transposable element in a trichloroethylene (TCE) degradative plasmid (TOM). Groundwater and sediment from a potential site for a TCE bioremediation field demonstration were used in laboratory microcosms to test the survival of this organism. In nonsterile aquifer sediment slurries, the bacterium was eliminated in a logrithmic decay concomitant with an increase in bacterivorous protists. A half-life for the organism calculated from extinction coefficients increased logarithmically with increasing inoculation density above 1 x 10(6) PR1 ml(-1). For inoculation densities below this level, the half-life of PR1 increased exponentially with decreasing inoculation density. The lowest half-lives corresponded to densities of bacteria that stimulate response of bacterivores. In a column system designed to incorporate aquifer flow, repeated addition of PR1 resulted in a buildup of bacterivore populations and reduced half-life of the bacterium. Addition of TCE and growth substrate in the eluent resulted in prolonged survival of PR1 and apparent mineralization of TCE. The results indicate significant but predictable losses due to native bacterivores would occur within and beyond a treatment zone where PR1 would be added to the aquifer, and mineralization of TCE in contaminated groundwater might be possible with repeated inoculation and addition of nutrients.
已从原始和受污染的含水层环境中分离出噬菌原生生物,但这些生物体在生物修复策略中的生态作用尚未明确界定。洋葱伯克霍尔德菌G4 PR1由于三氯乙烯(TCE)降解质粒(TOM)中Tn5转座元件的二次转座,组成型表达甲苯邻单加氧酶(tom)。来自TCE生物修复现场示范潜在地点的地下水和沉积物被用于实验室微观试验,以测试这种生物体的存活情况。在非无菌含水层沉积物浆液中,该细菌呈对数衰减被消除,同时噬菌原生生物数量增加。根据灭绝系数计算出的该生物体半衰期随着接种密度高于1×10⁶ PR1 ml⁻¹而呈对数增加。对于低于此水平的接种密度,PR1的半衰期随着接种密度降低呈指数增加。最低半衰期对应于刺激食细菌者反应的细菌密度。在一个旨在模拟含水层水流的柱系统中,重复添加PR1导致食细菌者种群增加,细菌半衰期缩短。在流出物中添加TCE和生长底物导致PR1存活时间延长以及TCE明显矿化。结果表明,在向含水层添加PR1的处理区内和区外,由于原生食细菌者会造成显著但可预测的损失,并且通过重复接种和添加营养物质,受污染地下水中的TCE可能实现矿化。