铜绿假单胞菌铁摄取与生物被膜形成研究进展

生物被膜是单细胞微生物通过其分泌的胞外多聚基质粘附于介质表面并将其自身包绕其中而成的膜样微生物细胞聚集物。生物被膜的形成使细菌具有更强的适应外界环境的能力,也是导致微生物产生耐药性及慢性感染性疾病难以治疗的重要原因之一。铜绿假单胞菌在肺部的定殖是肺囊性纤维化病患者发病和死亡主要原因,其造成的感染通常与形成抗生素抗性极强的生物被膜有关。铜绿假单胞菌生物被膜的形成受控于多种复杂的细菌调控体系之下,包括群体感应系统及参与调节胞外多聚基质合成的双组分调控系统等。此外,为了利用低浓度的环境铁来维持生存并完成各种生理功能,铜绿假单胞菌进化出了一系列铁摄取系统,这些系统对其毒力因子的释放和生物被膜的形成又起着重要的调控作用。本文主要对铜绿假单胞菌生物被膜的形成与调控机制及其铁摄取系统进行了综述,为进一步了解及清除铜绿假单胞菌引发的问题提供途径与思路。     

生物被膜在病原细菌与植物识别中的作用

生物被膜是微生物附着在生物或非生物表面所形成的一种三维结构,细胞被其自身所产生的胞外聚合物所包围,生物被膜的形成被认为是微生物应对生物和非生物胁迫时所产生的一种自我防御机制。众多微生物能够在植物叶、维管束和根等组织中生长,并在植物不同组织表面附着形成生物被膜,病原细菌的生物被膜随植物内部环境动态变化是其有效发挥致病作用的关键,研究植物病原细菌生物被膜调控机制是认识植物-病原菌互作的重要方面。文中将系统地介绍植物病原细菌生物被膜特征、组成成分、分子调控机制及最新研究进展。     

葡萄球菌生物被膜的基因调控机制研究进展

摘要:细菌的耐药性问题是目前医学临床面临的严峻问题,其中细菌生物被膜的形成是引起细菌持续性感染的主要致病机制之一。细菌生物被膜的形成过程十分复杂,受多种因子和多基因的共同调控,且不同的因子和基因在生物被膜形成的不同阶段所起的作用不同。本文重点对引起院内感染的主要致病菌葡萄球菌的生物被膜形成的基因调控机制,以及药物抑制葡萄球菌生物被膜的研究现状进行综述,旨在为解决医学临床中存在的细菌感染,研制抗生物被膜药物和疫苗等提供参考。     

白念珠菌生物被膜形成的遗传调控机制

白念珠菌是人体重要的条件性致病真菌。形态的多样性和可塑性是白念珠菌典型的生物学特征,这与它的致病性、宿主适应能力以及有性生殖过程密切相关。白念珠菌生物被膜(Biofilm)是由不同形态细胞(包括酵母型、菌丝和假菌丝)以及胞外基质组成的致密结构,也是毒性和耐药性形成的重要因子。生物被膜对抗真菌药物、宿主免疫系统和环境胁迫因子等都表现出较强的抵抗力和耐受性,是临床上病原真菌感染防治的重大挑战。随着基因表达谱和遗传操作技术的发展,白念珠菌生物被膜的形成及其耐药性的获得所依赖的遗传调控通路和分子调控机制越来越清楚。主要包括MAPK和cAMP介导的信号途径以及Bcr1和Tec1等因子介导的转录调控。此外,白念珠菌生物被膜的形成与形态转换和有性生殖之间存在密切的联系。文中综述了白念珠菌生物被膜形成的遗传调控机制,重点介绍了细胞壁相关蛋白、转录因子和交配型对该过程的调控以及生物被膜的耐药机制。     

生物被膜的形成及其电化学阻抗检测

生物被膜是细菌及其自身分泌的胞外聚合物组成的微生物群落,其形成是受多种机制共同调控的多阶段动态过程,具有较强的耐药性且难以清除,给医疗、食品等行业带来了巨大的威胁。近年来,生物被膜的相关研究领域备受关注,尤其是针对生物被膜的有效检测技术。本文在简要介绍生物被膜的特点、形成过程及群感效应对生物被膜的调控作用基础之上,总结了生物被膜常用的检测方法,重点针对电化学阻抗技术在生物被膜检测中的应用进行调研和讨论,并对基于微流控芯片的生物被膜电化学阻抗原位检测进行了综述和展望。     

细菌生物被膜中群体感应调控机制及其控制研究展望

生物被膜(biofilm)是微生物聚集黏附在物体表面形成的多细胞结构,是引起微生物感染的主要原因,对食品工业和公共卫生安全造成巨大的威胁。群体感应(quorum sensing,QS)是调控生物被膜形成的重要因素,与生物被膜的抗生素耐药性、抗逆性密切相关。研究发现:针对QS系统的天然、合成化合物被称为群体感应抑制剂(quorum sensing inhibitors,QSI),可干扰QS信号,破坏生物被膜的形成,这种现象被称为群体淬灭(quorum quenching,QQ)。本文中,笔者就生物被膜组分、群体感应的调控机制及生物被膜的控制策略进行深入综述,旨在为食品加工程中细菌生物被膜的防控提供理论依据。     

霍乱弧菌生物被膜发育与环境调控

生物被膜状态的霍乱弧菌具有极强的环境适应性和超高的感染性,生物被膜的发育调控研究对霍乱弧菌的宿主感染和环境适应非常重要。本文综述了近年来霍乱弧菌生物被膜研究结果,包括霍乱弧菌生物被膜的组成、发育和环境调控,尤其着重阐述了各种环境因子对霍乱弧菌生物被膜发育的影响,包括细菌自体信号分子、自然环境因子和宿主信号分子。     

鸡白痢沙门氏菌生物被膜形成相关基因rpoE的鉴定

【目的】通过鸡白痢沙门氏菌基因表达和缺失株生物特性的测定,鉴定其生物被膜形成的相关σ因子。【方法】利用结晶紫染色定量法测定沙门氏菌生物被膜形成能力;通过触酶试验测定rpo S活性,确定rpo S基因依赖性和非依赖性生物被膜形成株;利用建立的荧光定量PCR方法比较rpo S基因非依赖株在指数期和生物被膜形成期6个σ因子的基因表达差异;运用Red同源重组系统构建所鉴定σ因子基因缺失株,并测定野生株和基因缺失株对于环境应激的抵抗力差异。【结果】鸡白痢沙门氏菌S6702能够形成生物被膜,触酶试验阴性,确定S6702为rpo S基因非依赖性生物被膜形成株;荧光定量PCR检测显示,培养4-24 h后S6702中rpo E基因表达量最高;与野生株相比,Δrpo S缺失株保留了生物被膜形成能力,而Δrpo E缺失株不能形成生物被膜。rpo S和rpo E基因缺失株对于环境应激的抵抗力均显著降低。【结论】在rpo S基因非依赖性生物被膜形成株中,rpo E基因为参与生物被膜形成调控的σ因子之一,这一发现可用于进一步研究沙门氏菌生物被膜形成的调控机制。     

c-di-AMP调控细菌生物被膜的形成

细菌生物被膜是细菌持续性致病的重要机制。研究细菌生物被膜的形成和发展可为顽固性细菌感染防治提供新的思路与策略。环二腺苷酸c-di-AMP(Cyclic diadenosine monophosphate)是继c-di-GMP之后在细菌中新发现的一种核苷酸第二信使分子。研究发现,c-di-AMP参与调节细菌多种生理功能,包括细菌生长代谢、生物被膜形成、细胞壁的合成以及细菌毒力因子等。本文综述了c-di-AMP参与调控细菌生物被膜形成的不同方式及其分子机制。鉴于c-di-AMP在调控细菌生物被膜中的重要性,其可作为抗细菌生物被膜感染新药研发的潜在靶点。     

药物外排泵与生物被膜在微生物耐药机制中的相关性研究进展

生物被膜是介导微生物耐药与多重耐药的一大热点机制,涉及微生物的生长代谢、耐药基因等基因表型改变、群体感应系统的调控及药物外排泵等多重因素。耐药基因、药物外排泵与生物被膜在微生物耐药机制中,具有复杂而密切的相互影响。分别从生物被膜对药物外排泵、耐药基因的影响,药物外排泵对生物被膜的影响,以及药物外排泵和微生物生物被膜共同的调节因素,对近年来的相关研究进展作一综述。     

Changes in physico-chemical characteristics and viable bacterial communities during fermentation of alfalfa silages inoculated with Lactobacillus plantarum

Sulfate-reducing bacteria (SRB) are culprits for microbiologically influenced corrosion, and biofilms are believed to play essential roles in the corrosion induced by SRB. However, little is known about the regulation of SRB biofilms. Quorum sensing signal molecules acyl-homoserine lactones (AHLs) and autoinducer-2 (AI-2) regulate biofilm formation of many bacteria. In this study, the production of AHLs and AI-2 by one SRB strain, Desulfovibrio sp. Huiquan2017, was detected, and the effect of exogenous AI-2 on bacterial biofilm formation was discussed. It was found that the cell-free supernatants of Desulfovibrio sp. Huiquan2017 induced luminescence in a ?luxS mutant strain Vibrio harveyi BB170, indicating the production of functional AI-2 by the bacterium. In the presence of exogenous AI-2, the growth of Desulfovibrio sp. Huiquan2017 and early biofilm formation were not affected, but the later stage of biofilm development was inhibited significantly. The biofilms became looser, smaller, and thinner, and contained less bacteria and extracellular polymeric substances (EPS). The inhibition effect of AI-2 on the biofilm development of Desulfovibrio sp. Huiquan2017 was mainly achieved through reducing the amount of EPS in biofilms. These findings shed light on the biofilm regulation of SRB.

     

The use of biocides to control sulphate‐reducing bacteria in biofilms on mild steel surfaces

Three different types of biocides, viz. formaldehyde (FM), glutaraldehyde (GA) and isothiozolone (ITZ) were used to control planktonic and sessile populations of two marine isolates of sulphate‐reducing bacteria (SRB). The influence of these biocides on the initial attachment of cells to mild steel surfaces, on subsequent biofilm formation and on the activity of hydrogenase enzymes within developed biofilms was evaluated. In the presence of biocides the rate and degree of colonization of mild steel by SRB depended on incubation time, bacterial isolate and the type of biocide used. Although SRB differed in their susceptibility to biocides, for all isolates the biofilm population was more resistant to the treatment than the planktonic population. GA showed highest efficiency in controlling planktonic and sessile SRB compared with the other two biocides. The activity of the enzyme hydrogenase measured in SRB biofilms varied between isolates and with the biocide treatment. No correlation was found between the number of sessile cells and hydrogenase activity.     

A synergistic d-tyrosine and tetrakis hydroxymethyl phosphonium sulfate biocide combination for the mitigation of an SRB biofilm

Microbiologically influenced corrosion (MIC) is a major problem in various industries such as oil and gas, and water utilities. Billions of dollars are lost to microbiologically influenced corrosion (MIC) each year in the US. The key to MIC control is biofilm mitigation. Sulfate-reducing bacteria (SRB) are often the culprits. They are also involved in souring and biofouling. SRB biofilms are notoriously difficult to eradicate. Due to environmental concerns and increasing costs, better biocide treatment strategies are desired. Recent studies suggested that D: -tyrosine and some other D: -amino acids may signal biofilm dispersal. Experimental results in this work indicated that D: -tyrosine is an effective biocide enhancer for tetrakis hydroxymethyl phosphonium sulfate (THPS) that is a green biocide. Desulfovibrio vulgaris (ATCC 7757) was used in biofilm prevention and biofilm removal tests. It was found that 100?ppm D: -tyrosine alone and 50?ppm THPS alone were both ineffective against the SRB biofilm. However, when 1?ppm D: -tyrosine was combined with 50?ppm THPS, the synergy between the two chemicals successfully prevented the establishment of the SRB biofilm on C1018 mild steel coupon surfaces in batch treatment tests. It also eradicated established SRB biofilms from coupon surfaces in both 1 and 3-h shock treatment tests.     

Action of antimicrobial substances produced by different oil reservoir Bacillus strains against biofilm formation

Microbial colonization of petroleum industry systems takes place through the formation of biofilms, and can result in biodeterioration of the metal surfaces. In a previous study, two oil reservoir Bacillus strains (Bacillus licheniformis T6-5 and Bacillus firmus H₂O-1) were shown to produce antimicrobial substances (AMS) active against different Bacillus strains and a consortium of sulfate-reducing bacteria (SRB) on solid medium. However, neither their ability to form biofilms nor the effect of the AMS on biofilm formation was adequately addressed. Therefore, here, we report that three Bacillus strains (Bacillus pumilus LF4—used as an indicator strain, B. licheniformis T6-5, and B. firmus H₂O-1), and an oil reservoir SRB consortium (T6lab) were grown as biofilms on glass surfaces. The AMS produced by strains T6-5 and H₂O-1 prevented the formation of B. pumilus LF4 biofilm and also eliminated pre-established LF4 biofilm. In addition, the presence of AMS produced by H₂O-1 reduced the viability and attachment of the SRB consortium biofilm by an order of magnitude. Our results suggest that the AMS produced by Bacillus strains T6-5 and H₂O-1 may have a potential for pipeline-cleaning technologies to inhibit biofilm formation and consequently reduce biocorrosion.     

Sulfate-reducing bacterial community structure and their contribution to carbon mineralization in a wastewater biofilm growing under microaerophilic conditions

The community structure of sulfate-reducing bacteria (SRB) and the contribution of SRB to carbon mineralization in a wastewater biofilm growing under microaerophilic conditions were investigated by combining molecular techniques, molybdate inhibition batch experiments, and microelectrode measurements. A 16S rDNA clone library of bacteria populations was constructed from the biofilm sample. The 102 clones analyzed were grouped into 53 operational taxonomic units (OTUs), where the clone distribution was as follows: Cytophaga-Flexibacter-Bacteroides (41%), Proteobacteria (41%), low-G+C Gram-positive bacteria (18%), and other phyla (3%). Three additional bacterial clone libraries were also constructed from SRB enrichment cultures with propionate, acetate, and H₂ as electron donors to further investigate the differences in SRB community structure due to amendments of different carbon sources. These libraries revealed that SRB clones were phylogenetically diverse and affiliated with six major SRB genera in the delta-subclass of the Proteobacteria. Fluorescent in situ hybridization (FISH) analysis revealed that Desulfobulbus and Desulfonema were the most abundant SRB species in this biofilm, and this higher abundance (ca. 2–4×10⁹ cells cm^–3 and 5×10⁷ filaments cm^–3, respectively) was detected in the surface of the biofilm. Microelectrode measurements showed that a high sulfate-reducing activity was localized in a narrow zone located just below the oxic/anoxic interface when the biofilm was cultured in a synthetic medium with acetate as the sole carbon source. In contrast, a broad sulfate-reducing zone was found in the entire anoxic strata when the biofilm was cultured in the supernatant of the primary settling tank effluent. This is probably because organic carbon sources diffused into the biofilm from the bulk water and an unknown amount of volatile fatty acids was produced in the biofilm. A combined approach of molecular techniques and batch experiments with a specific inhibitor (molybdate) clearly demonstrated that Desulfobulbus is a numerically important member of SRB populations and the main contributor to the oxidation of propionate to acetate in this biofilm. However, acetate was preferentially utilized by nitrate-reducing bacteria but not by acetate-utilizing SRB.     

Linked Redox Precipitation of Sulfur and Selenium under Anaerobic Conditions by Sulfate-Reducing Bacterial Biofilms

A biofilm-forming strain of sulfate-reducing bacteria (SRB), isolated from a naturally occurring mixed biofilm and identified by 16S rDNA analysis as a strain of Desulfomicrobium norvegicum, rapidly removed 200 μM selenite from solution during growth on lactate and sulfate. Elemental selenium and elemental sulfur were precipitated outside SRB cells. Precipitation occurred by an abiotic reaction with bacterially generated sulfide. This appears to be a generalized ability among SRB, arising from dissimilatory sulfide biogenesis, and can take place under low redox conditions and in the dark. The reaction represents a new means for the deposition of elemental sulfur by SRB under such conditions. A combination of transmission electron microscopy, environmental scanning electron microscopy, and cryostage field emission scanning electron microscopy were used to reveal the hydrated nature of SRB biofilms and to investigate the location of deposited sulfur-selenium in relation to biofilm elements. When pregrown SRB biofilms were exposed to a selenite-containing medium, nanometer-sized selenium-sulfur granules were precipitated within the biofilm matrix. Selenite was therefore shown to pass through the biofilm matrix before reacting with bacterially generated sulfide. This constitutes an efficient method for the removal of toxic concentrations of selenite from solution. Implications for environmental cycling and the fate of sulfur and selenium are discussed, and a general model for the potential action of SRB in selenium transformations is presented.     

Stratified Microbial Structure and Activity in Sulfide- and Methane-Producing Anaerobic Sewer Biofilms

Simultaneous production of sulfide and methane by anaerobic sewer biofilms has recently been observed, suggesting that sulfate-reducing bacteria (SRB) and methanogenic archaea (MA), microorganisms known to compete for the same substrates, can coexist in this environment. This study investigated the community structures and activities of SRB and MA in anaerobic sewer biofilms (average thickness of 800 μm) using a combination of microelectrode measurements, molecular techniques, and mathematical modeling. It was seen that sulfide was mainly produced in the outer layer of the biofilm, between the depths of 0 and 300 μm, which is in good agreement with the distribution of SRB population as revealed by cryosection-fluorescence in situ hybridization (FISH). SRB had a higher relative abundance of 20% on the surface layer, which decreased gradually to below 3% at a depth of 400 μm. In contrast, MA mainly inhabited the inner layer of the biofilm. Their relative abundances increased from 10% to 75% at depths of 200 μm and 700 μm, respectively, from the biofilm surface layer. High-throughput pyrosequencing of 16S rRNA amplicons showed that SRB in the biofilm were mainly affiliated with five genera, Desulfobulbus, Desulfomicrobium, Desulfovibrio, Desulfatiferula, and Desulforegula, while about 90% of the MA population belonged to the genus Methanosaeta. The spatial organizations of SRB and MA revealed by pyrosequencing were consistent with the FISH results. A biofilm model was constructed to simulate the SRB and MA distributions in the anaerobic sewer biofilm. The good fit between model predictions and the experimental data indicate that the coexistence and spatial structure of SRB and MA in the biofilm resulted from the microbial types and their metabolic transformations and interactions with substrates.     

Linked redox precipitation of sulfur and selenium under anaerobic conditions by sulfate-reducing bacterial biofilms

A biofilm-forming strain of sulfate-reducing bacteria (SRB), isolated from a naturally occurring mixed biofilm and identified by 16S rDNA analysis as a strain of Desulfomicrobium norvegicum, rapidly removed 200 micro M selenite from solution during growth on lactate and sulfate. Elemental selenium and elemental sulfur were precipitated outside SRB cells. Precipitation occurred by an abiotic reaction with bacterially generated sulfide. This appears to be a generalized ability among SRB, arising from dissimilatory sulfide biogenesis, and can take place under low redox conditions and in the dark. The reaction represents a new means for the deposition of elemental sulfur by SRB under such conditions. A combination of transmission electron microscopy, environmental scanning electron microscopy, and cryostage field emission scanning electron microscopy were used to reveal the hydrated nature of SRB biofilms and to investigate the location of deposited sulfur-selenium in relation to biofilm elements. When pregrown SRB biofilms were exposed to a selenite-containing medium, nanometer-sized selenium-sulfur granules were precipitated within the biofilm matrix. Selenite was therefore shown to pass through the biofilm matrix before reacting with bacterially generated sulfide. This constitutes an efficient method for the removal of toxic concentrations of selenite from solution. Implications for environmental cycling and the fate of sulfur and selenium are discussed, and a general model for the potential action of SRB in selenium transformations is presented.     

Distribution of sulfate-reducing bacteria, O2, and H2S in photosynthetic biofilms determined by oligonucleotide probes and microelectrodes.

The vertical distribution of sulfate-reducing bacteria (SRB) in photosynthetic biofilms from the trickling filter of a sewage treatment plant was investigated with oligonucleotide probes binding to 16S rRNA. To demonstrate the effect of daylight and photosynthesis and thereby of increased oxygen penetration, we incubated two 4-mm-thick biofilm samples in darkness or exposed to light at natural intensity. Gradients of O2, H2S, and pH were examined with microelectrodes during incubation. The samples were subsequently frozen with liquid nitrogen and sliced on a cryomicrotome in 20-microns vertical slices. Fluorescent-dye-conjugated oligonucleotides were used as "phylogenetic" probes to identify single cells in the slices. Oligonucleotide sequences were selected which were complementary to short sequence elements (16 to 20 nucleotides) within the 16S rRNA of sulfate-reducing bacteria. The probes were labeled with fluorescein or rhodamine derivatives for subsequent visualization by epifluorescence microscopy. Five probes were synthesized for eukaryotes, eubacteria, SRB (including most species of the delta group of purple bacteria), Desulfobacter spp., and a nonhybridizing control. The SRB were unevenly distributed in the biofilm, being present in all states from single scattered cells to dense clusters of several thousand cells. To quantify the vertical distribution of SRB, we counted cells along vertical transects through the biofilm. This was done in a blind experiment to ascertain the reliability of the staining. A negative correlation between the vertical distribution of positively stained SRB cells and the measured O2 profiles was found. The distribution differed in light- and dark-incubated samples presumably because of the different extensions of the oxic surface layer. In both cases the SRB were largely restricted to anoxic layers.