Lawrence J R, Chenier M R, Roy R, Beaumier D, Fortin N, Swerhone G D W, Neu T R, Greer C W
National Water Research Institute, 11 Innovation Blvd., Saskatoon, Saskatchewan S7N 3H5, Canada.
Appl Environ Microbiol. 2004 Jul;70(7):4326-39. doi: 10.1128/AEM.70.7.4326-4339.2004.
Studies were carried out to assess the influence of nutrients, dissolved oxygen (DO) concentration, and nickel (Ni) on river biofilm development, structure, function, and community composition. Biofilms were cultivated in rotating annular reactors with river water at a DO concentration of 0.5 or 7.5 mg liter(-1), with or without a combination of carbon, nitrogen, and phosphorus (CNP) and with or without Ni at 0.5 mg liter(-1). The effects of Ni were apparent in the elimination of cyanobacterial populations and reduced photosynthetic biomass in the biofilm. Application of lectin-binding analyses indicated changes in exopolymer abundance and a shift in the glycoconjugate makeup of the biofilms, as well as in the response to all treatments. Application of the fluorescent live-dead staining (BacLight Live-Dead staining kit; Molecular Probes, Eugene, Oreg.) indicated an increase in the ratio of live to dead cells under low-oxygen conditions. Nickel treatments had 50 to 75% fewer 'live' cells than their corresponding controls. Nickel at 0.5 mg liter(-1) corresponding to the industrial release rate concentration for nickel resulted in reductions in carbon utilization spectra relative to control and CNP treatments without nickel. In these cases, the presence of nickel eliminated the positive influence of nutrients on the biofilm. Other culture-dependent analyses (plate counts and most probable number) revealed no significant treatment effect on the biofilm communities. In the presence of CNP and at both DO levels, Ni negatively affected denitrification but had no effect on hexadecane mineralization or sulfate reduction. Analysis of total community DNA indicated abundant eubacterial 16S ribosomal DNA (rDNA), whereas Archaea were not detected. Amplification of the alkB gene indicated a positive effect of CNP and a negative effect of Ni. The nirS gene was not detected in samples treated with Ni at 0.5 mg liter(-1), indicating a negative effect on specific populations of bacteria, such as denitrifiers, resulting in a reduction in diversity. Denaturing gradient gel electrophoresis revealed that CNP had a beneficial impact on biofilm bacterial diversity at high DO concentrations, but none at low DO concentrations, and that the negative effect of Ni on diversity was similar at both DO concentrations. Notably, Ni resulted in the appearance of unique bands in 16S rDNA from Ni, DO, and CNP treatments. Sequencing results confirmed that the bands belonged to bacteria originating from freshwater and marine environments or from agricultural soils and industrial effluents. The observations indicate that significant interactions occur between Ni, oxygen, and nutrients and that Ni at 0.5 mg liter(-1) may have significant impacts on river microbial community diversity and function.
开展了多项研究,以评估营养物质、溶解氧(DO)浓度和镍(Ni)对河流生物膜发育、结构、功能及群落组成的影响。生物膜在旋转环形反应器中培养,使用的河水DO浓度为0.5或7.5毫克/升,添加或不添加碳、氮和磷(CNP)的组合,添加或不添加0.5毫克/升的Ni。Ni的影响在蓝藻种群的消除以及生物膜中光合生物量的减少方面很明显。凝集素结合分析的应用表明,胞外聚合物丰度发生了变化,生物膜的糖缀合物组成发生了转变,以及对所有处理的反应也发生了变化。荧光活死染色(BacLight活死染色试剂盒;Molecular Probes,俄勒冈州尤金市)的应用表明,在低氧条件下活细胞与死细胞的比例增加。Ni处理组的“活”细胞比相应对照组少50%至75%。对应于镍的工业释放速率浓度的0.5毫克/升Ni导致相对于无镍的对照和CNP处理,碳利用光谱降低。在这些情况下,镍的存在消除了营养物质对生物膜的积极影响。其他基于培养的分析(平板计数和最大可能数)显示对生物膜群落没有显著的处理效果。在存在CNP且两种DO水平下,Ni对反硝化有负面影响,但对十六烷矿化或硫酸盐还原没有影响。对总群落DNA的分析表明存在丰富的真细菌16S核糖体DNA(rDNA),而未检测到古菌。alkB基因的扩增表明CNP有积极影响,而Ni有负面影响。在0.5毫克/升Ni处理的样品中未检测到nirS基因,表明对特定细菌种群(如反硝化细菌)有负面影响,导致多样性降低。变性梯度凝胶电泳显示,CNP在高DO浓度下对生物膜细菌多样性有有益影响,但在低DO浓度下没有,并且Ni对多样性的负面影响在两种DO浓度下相似。值得注意的是,Ni导致来自Ni、DO和CNP处理的16S rDNA中出现独特条带。测序结果证实这些条带属于源自淡水和海洋环境或农业土壤及工业废水的细菌。这些观察结果表明,Ni、氧气和营养物质之间发生了显著的相互作用,并且0.5毫克/升的Ni可能对河流微生物群落多样性和功能有重大影响。