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兼性厌氧沉积物中质粒介导的单卤代联苯生物降解命运

Plasmid-mediated biodegradative fate of monohalogenated biphenyls in facultatively anaerobic sediments.

作者信息

Sayler G S, Kong H L, Shields M S

出版信息

Basic Life Sci. 1984;28:117-35. doi: 10.1007/978-1-4684-4715-6_8.

Abstract

The results of these studies have demonstrated that model PCB substrates can be mineralized by indigenous microbial population in contaminated sediments. This catabolic function can be rate limited at the microenvironmental level by physical-chemical processes such as physical partitioning and accumulation. At the biochemical level, this catabolic function is determined by the existence of plasmid borne genes that, under laboratory conditions, can be maintained and expressed in pure or mixed culture. Numerous limitations are encountered in establishing the significance of these biodegradative bacteria and the catabolic plasmids at the environmental level. Relatively little information is available concerning frequencies and stability of the bacteria or the plasmid encoded genes within the community. There is no information on the incompatibility grouping of the isolated plasmid relative to other plasmids maintained within the populations. Such factors will influence the development of gene screening techniques to monitor gene frequency distributions in the sediment community. Although mineralization of 4CBP was observed under moderately reducing conditions, it remains suspect that transient or trace levels of dissolved oxygen may have permitted conventional aerobic metabolism of the substrate. If this is true, demonstrating anaerobic metabolism of environmental contaminants will require strict and tedious cultivation under highly reduced conditions (approximately-300 mV). Large deletions of cryptic DNA observed under laboratory conditions may affect bacterial survival and gene maintenance and transfer under environmental conditions. Little information exists on regulation of catabolic activity of selective pressures required to maintain the degradative genes under environmental conditions. Such limitation encountered in these studies are shared by virtually all attempts to utilize genetically manipulated bacteria or newly isolated strains and plasmids. Perhaps the fundamental question is whether the catabolic genes are maintained and expressed within the community rather than whether the host bacterium can survive in the environment.

摘要

这些研究结果表明,模型多氯联苯底物可被受污染沉积物中的本地微生物群落矿化。这种分解代谢功能在微环境水平上可能受到物理分配和积累等物理化学过程的速率限制。在生化水平上,这种分解代谢功能取决于质粒携带基因的存在,在实验室条件下,这些基因可在纯培养或混合培养中得以维持和表达。在确定这些生物降解细菌和分解代谢质粒在环境层面的重要性时,会遇到诸多限制。关于群落中细菌或质粒编码基因的频率和稳定性,可用信息相对较少。关于分离出的质粒相对于种群中维持的其他质粒的不相容分组,尚无信息。这些因素将影响用于监测沉积物群落中基因频率分布的基因筛选技术的发展。尽管在适度还原条件下观察到了4CBP的矿化,但仍有人怀疑,溶解氧的瞬态或痕量水平可能允许底物进行传统的有氧代谢。如果真是这样,证明环境污染物的厌氧代谢将需要在高度还原条件下(约-300 mV)进行严格且繁琐的培养。在实验室条件下观察到的隐蔽DNA的大量缺失可能会影响细菌在环境条件下的存活以及基因的维持和转移。关于在环境条件下维持降解基因所需的选择性压力对分解代谢活性的调节,几乎没有相关信息。这些研究中遇到的此类限制实际上是所有利用基因工程细菌或新分离菌株及质粒的尝试所共有的。也许根本问题在于分解代谢基因是否在群落中得以维持和表达,而非宿主细菌能否在环境中存活。

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