Dwyer D F, Hooper S W, Rojo F, Timmis K N
Schriftenr Ver Wasser Boden Lufthyg. 1988;78:267-76.
The conclusions that can be derived from this study regarding the fate of the GEMs and their ability to degrade added pollutants are as follows: 1. Both GEMs were able to survive in the microcoms. Because Pseudomonas sp. B13 has been cultured for a long time in the laboratory, it was not expected to survive well in the microcosm. Surprisingly, it and the derivative GEMs persisted at a high population level of approximately 10(5) bacteria/ml. Pure culture studies had demonstrated an ability of FR1(pFRC20P) to readily degrade simultaneous mixtures of 3CB and 4MB. In the microcosms, however, the GEM did not perform as well as expected, particularly when confronted with a shock load of a 3CB and 4MB mixture. Thus, the microcosm studies may be of potential help for making predictions concerning environmental applications of GEMs. 2. Pseudomonas sp. B13 derivative strains FR1 and FR1(pFRC20P) were able to degrade low concentrations of substituted benzoates within the complex ecosystem of the activated sludge microcosm. A good deal of information concerning the degradation pathway for aromatics by Pseudomonas sp. B13 was already known. This allowed for the construction of the stable, regulated pathways for the degradation of substituted aromatic compounds in both GEMs and indicates that the construction of similar GEMs for the degradation of environmental pollutants is a promising experimental strategy. 3. There was not any demonstrable, adverse effect of GEM addition to the microbial population level in the microcosm. The GEMs were even able to function in a protective manner for the indigenous populations by buffering them against the adverse effects of addition of substituted benzoates. In contrast, for microcosms lacking GEM addition, a wash-out of the bacterial population in the microcosm occurred (data not shown). 4. Lateral transfer of new genetic information (xylXYZLS) from the GEM chromosome to indigenous microorganisms was not detected, whereas transfer of the hybrid, mobilizable pFRC20P carrying the gene for lactone isomerase did apparently occur. In this particular case, transfer may have been beneficial for the community as a whole if it increased the ecosystem's ability to cope with the presence of toxic pollutants. As more GEMs are constructed for specific biotechnological applications the diversity and complexity of microcosms used to study their fate and function will increase. The ability of such studies to predict a priori the fate of these microorganisms will help to develop strategies both to decrease the risks associated with introducing GEMs into the environment and to increase and regulate the capacity of GEMs to degrade toxic pollutants.(ABSTRACT TRUNCATED AT 400 WORDS)
关于基因工程微生物(GEMs)的归宿及其降解添加污染物能力,本研究可得出以下结论:1. 两种GEMs都能在微型生态系统中存活。由于假单胞菌属B13已在实验室培养很长时间,预计它在微型生态系统中存活不佳。令人惊讶的是,它和衍生的GEMs在约10(5) 个细菌/毫升的高种群水平下持续存在。纯培养研究表明FR1(pFRC20P) 能够轻易降解3CB和4MB的同时混合物。然而,在微型生态系统中,该GEM的表现不如预期,特别是在面对3CB和4MB混合物的冲击负荷时。因此,微型生态系统研究可能有助于预测GEMs的环境应用。2. 假单胞菌属B13的衍生菌株FR1和FR1(pFRC20P) 能够在活性污泥微型生态系统的复杂生态环境中降解低浓度的取代苯甲酸酯。关于假单胞菌属B13降解芳烃途径的大量信息已经为人所知。这使得在两种GEMs中构建稳定、受调控的取代芳烃化合物降解途径成为可能,并表明构建类似的用于降解环境污染物的GEMs是一种有前景的实验策略。3. 向微型生态系统中添加GEMs对微生物种群水平没有任何明显的不利影响。GEMs甚至能够以保护方式作用于本地种群,缓冲它们免受添加取代苯甲酸酯的不利影响。相比之下,对于未添加GEMs的微型生态系统,微型生态系统中的细菌种群出现了流失(数据未显示)。4. 未检测到新的遗传信息(xylXYZLS)从GEM染色体横向转移到本地微生物,而携带内酯异构酶基因且可移动的杂交质粒pFRC20P的转移显然发生了。在这种特殊情况下,如果转移增加了生态系统应对有毒污染物存在的能力,那么这种转移可能对整个群落有益。随着为特定生物技术应用构建更多的GEMs,用于研究其归宿和功能的微型生态系统的多样性和复杂性将会增加。此类研究预测这些微生物归宿的能力将有助于制定策略,既降低将GEMs引入环境相关的风险,又提高和调控GEMs降解有毒污染物的能力。(摘要截选至400字)