Singleton David R, Powell Sabrina N, Sangaiah Ramiah, Gold Avram, Ball Louise M, Aitken Michael D
Department of Environmental Sciences and Engineering, School of Public Health, CB 7431, University of North Carolina, Chapel Hill, NC 27599-7431, USA.
Appl Environ Microbiol. 2005 Mar;71(3):1202-9. doi: 10.1128/AEM.71.3.1202-1209.2005.
[13C6]salicylate, [U-13C]naphthalene, and [U-13C]phenanthrene were synthesized and separately added to slurry from a bench-scale, aerobic bioreactor used to treat soil contaminated with polycyclic aromatic hydrocarbons. Incubations were performed for either 2 days (salicylate, naphthalene) or 7 days (naphthalene, phenanthrene). Total DNA was extracted from the incubations, the "heavy" and "light" DNA were separated, and the bacterial populations associated with the heavy fractions were examined by denaturing gradient gel electrophoresis (DGGE) and 16S rRNA gene clone libraries. Unlabeled DNA from Escherichia coli K-12 was added to each sample as an internal indicator of separation efficiency. While E. coli was not detected in most analyses of heavy DNA, a low number of E. coli sequences was recovered in the clone libraries associated with the heavy DNA fraction of [13C]phenanthrene incubations. The number of E. coli clones recovered proved useful in determining the relative amount of light DNA contamination of the heavy fraction in that sample. Salicylate- and naphthalene-degrading communities displayed similar DGGE profiles and their clone libraries were composed primarily of sequences belonging to the Pseudomonas and Ralstonia genera. In contrast, heavy DNA from the phenanthrene incubations displayed a markedly different DGGE profile and was composed primarily of sequences related to the Acidovorax genus. There was little difference in the DGGE profiles and types of sequences recovered from 2- and 7-day incubations with naphthalene, so secondary utilization of the 13C during the incubation did not appear to be an issue in this experiment.
合成了[¹³C₆]水杨酸盐、[U-¹³C]萘和[U-¹³C]菲,并将它们分别添加到用于处理受多环芳烃污染土壤的实验室规模需氧生物反应器的泥浆中。培养分别进行2天(水杨酸盐、萘)或7天(萘、菲)。从培养物中提取总DNA,分离“重”DNA和“轻”DNA,并通过变性梯度凝胶电泳(DGGE)和16S rRNA基因克隆文库检查与重组分相关的细菌种群。将来自大肠杆菌K-12的未标记DNA添加到每个样品中作为分离效率的内部指标。虽然在大多数重DNA分析中未检测到大肠杆菌,但在与[¹³C]菲培养物的重DNA组分相关的克隆文库中回收了少量大肠杆菌序列。回收的大肠杆菌克隆数量被证明有助于确定该样品中重组分的轻DNA污染的相对量。水杨酸盐和萘降解群落显示出相似的DGGE图谱,它们的克隆文库主要由属于假单胞菌属和罗尔斯通氏菌属的序列组成。相比之下,菲培养物的重DNA显示出明显不同的DGGE图谱,并且主要由与嗜酸菌属相关的序列组成。从萘培养2天和7天回收的DGGE图谱和序列类型几乎没有差异,因此在该实验中培养期间¹³C的二次利用似乎不是一个问题。