Alignment of the c-Type Cytochrome OmcS along Pili of Geobacter sulfurreducens

Immunogold localization revealed that OmcS, a cytochrome that is required for Fe(III) oxide reduction by Geobacter sulfurreducens, was localized along the pili. The apparent spacing between OmcS molecules suggests that OmcS facilitates electron transfer from pili to Fe(III) oxides rather than promoting electron conduction along the length of the pili.There are multiple competing/complementary models for extracellular electron transfer in Fe(III)- and electrode-reducing microorganisms (8, 18, 20, 44). Which mechanisms prevail in different microorganisms or environmental conditions may greatly influence which microorganisms compete most successfully in sedimentary environments or on the surfaces of electrodes and can impact practical decisions on the best strategies to promote Fe(III) reduction for bioremediation applications (18, 19) or to enhance the power output of microbial fuel cells (18, 21).The three most commonly considered mechanisms for electron transfer to extracellular electron acceptors are (i) direct contact between redox-active proteins on the outer surfaces of the cells and the electron acceptor, (ii) electron transfer via soluble electron shuttling molecules, and (iii) the conduction of electrons along pili or other filamentous structures. Evidence for the first mechanism includes the necessity for direct cell-Fe(III) oxide contact in Geobacter species (34) and the finding that intensively studied Fe(III)- and electrode-reducing microorganisms, such as Geobacter sulfurreducens and Shewanella oneidensis MR-1, display redox-active proteins on their outer cell surfaces that could have access to extracellular electron acceptors (1, 2, 12, 15, 27, 28, 31-33). Deletion of the genes for these proteins often inhibits Fe(III) reduction (1, 4, 7, 15, 17, 28, 40) and electron transfer to electrodes (5, 7, 11, 33). In some instances, these proteins have been purified and shown to have the capacity to reduce Fe(III) and other potential electron acceptors in vitro (10, 13, 29, 38, 42, 43, 48, 49).Evidence for the second mechanism includes the ability of some microorganisms to reduce Fe(III) that they cannot directly contact, which can be associated with the accumulation of soluble substances that can promote electron shuttling (17, 22, 26, 35, 36, 47). In microbial fuel cell studies, an abundance of planktonic cells and/or the loss of current-producing capacity when the medium is replaced is consistent with the presence of an electron shuttle (3, 14, 26). Furthermore, a soluble electron shuttle is the most likely explanation for the electrochemical signatures of some microorganisms growing on an electrode surface (26, 46).Evidence for the third mechanism is more circumstantial (19). Filaments that have conductive properties have been identified in Shewanella (7) and Geobacter (41) species. To date, conductance has been measured only across the diameter of the filaments, not along the length. The evidence that the conductive filaments were involved in extracellular electron transfer in Shewanella was the finding that deletion of the genes for the c-type cytochromes OmcA and MtrC, which are necessary for extracellular electron transfer, resulted in nonconductive filaments, suggesting that the cytochromes were associated with the filaments (7). However, subsequent studies specifically designed to localize these cytochromes revealed that, although the cytochromes were extracellular, they were attached to the cells or in the exopolymeric matrix and not aligned along the pili (24, 25, 30, 40, 43). Subsequent reviews of electron transfer to Fe(III) in Shewanella oneidensis (44, 45) appear to have dropped the nanowire concept and focused on the first and second mechanisms.Geobacter sulfurreducens has a number of c-type cytochromes (15, 28) and multicopper proteins (12, 27) that have been demonstrated or proposed to be on the outer cell surface and are essential for extracellular electron transfer. Immunolocalization and proteolysis studies demonstrated that the cytochrome OmcB, which is essential for optimal Fe(III) reduction (15) and highly expressed during growth on electrodes (33), is embedded in the outer membrane (39), whereas the multicopper protein OmpB, which is also required for Fe(III) oxide reduction (27), is exposed on the outer cell surface (39).OmcS is one of the most abundant cytochromes that can readily be sheared from the outer surfaces of G. sulfurreducens cells (28). It is essential for the reduction of Fe(III) oxide (28) and for electron transfer to electrodes under some conditions (11). Therefore, the localization of this important protein was further investigated.     

Identification of Diverse Antimicrobial Resistance Determinants Carried on Bacterial,Plasmid, or Viral Metagenomes from an Activated Sludge Microbial Assemblage

Using both sequence- and function-based metagenomic approaches, multiple antibiotic resistance determinants were identified within metagenomic libraries constructed from DNA extracted from bacterial chromosomes, plasmids, or viruses within an activated sludge microbial assemblage. Metagenomic clones and a plasmid that in Escherichia coli expressed resistance to chloramphenicol, ampicillin, or kanamycin were isolated, with many cloned DNA sequences lacking any significant homology to known antibiotic resistance determinants.Activated sludge in wastewater treatment plants is an open system with a dynamic and phylogenetically diverse microbial community (2, 3, 6, 7, 10, 11). Since the activated sludge process promotes cellular interactions among diverse microorganisms, there is great potential for the lateral transfer of antibiotic resistance genes between microbes in activated sludge and in downstream environments. Several studies have previously identified antibiotic resistance determinants from wastewater communities that are carried on bacterial chromosomes (1, 4, 14) and plasmids (9, 12, 13), but to our knowledge, a simultaneous metagenomic survey of antibiotic resistance determinants from all three genetic reservoirs (i.e., chromosomes, plasmids, and viruses) has never been performed within the same environment. To achieve a more comprehensive assessment of antibiotic resistance genes in the activated sludge microbial community, this study used both function- and sequence-based metagenomic approaches to identify antibiotic resistance determinants carried on bacterial chromosomes, plasmids, or viruses within an activated sludge microbial assemblage.     

A New Borrelia Species Defined by Multilocus Sequence Analysis of Housekeeping Genes

Analysis of Lyme borreliosis (LB) spirochetes, using a novel multilocus sequence analysis scheme, revealed that OspA serotype 4 strains (a rodent-associated ecotype) of Borrelia garinii were sufficiently genetically distinct from bird-associated B. garinii strains to deserve species status. We suggest that OspA serotype 4 strains be raised to species status and named Borrelia bavariensis sp. nov. The rooted phylogenetic trees provide novel insights into the evolutionary history of LB spirochetes.Multilocus sequence typing (MLST) and multilocus sequence analysis (MLSA) have been shown to be powerful and pragmatic molecular methods for typing large numbers of microbial strains for population genetics studies, delineation of species, and assignment of strains to defined bacterial species (4, 13, 27, 40, 44). To date, MLST/MLSA schemes have been applied only to a few vector-borne microbial populations (1, 6, 30, 37, 40, 41, 47).Lyme borreliosis (LB) spirochetes comprise a diverse group of zoonotic bacteria which are transmitted among vertebrate hosts by ixodid (hard) ticks. The most common agents of human LB are Borrelia burgdorferi (sensu stricto), Borrelia afzelii, Borrelia garinii, Borrelia lusitaniae, and Borrelia spielmanii (7, 8, 12, 35). To date, 15 species have been named within the group of LB spirochetes (6, 31, 32, 37, 38, 41). While several of these LB species have been delineated using whole DNA-DNA hybridization (3, 20, 33), most ecological or epidemiological studies have been using single loci (5, 9-11, 29, 34, 36, 38, 42, 51, 53). Although some of these loci have been convenient for species assignment of strains or to address particular epidemiological questions, they may be unsuitable to resolve evolutionary relationships among LB species, because it is not possible to define any outgroup. For example, both the 5S-23S intergenic spacer (5S-23S IGS) and the gene encoding the outer surface protein A (ospA) are present only in LB spirochete genomes (36, 43). The advantage of using appropriate housekeeping genes of LB group spirochetes is that phylogenetic trees can be rooted with sequences of relapsing fever spirochetes. This renders the data amenable to detailed evolutionary studies of LB spirochetes.LB group spirochetes differ remarkably in their patterns and levels of host association, which are likely to affect their population structures (22, 24, 46, 48). Of the three main Eurasian Borrelia species, B. afzelii is adapted to rodents, whereas B. valaisiana and most strains of B. garinii are maintained by birds (12, 15, 16, 23, 26, 45). However, B. garinii OspA serotype 4 strains in Europe have been shown to be transmitted by rodents (17, 18) and, therefore, constitute a distinct ecotype within B. garinii. These strains have also been associated with high pathogenicity in humans, and their finer-scale geographical distribution seems highly focal (10, 34, 52, 53).In this study, we analyzed the intra- and interspecific phylogenetic relationships of B. burgdorferi, B. afzelii, B. garinii, B. valaisiana, B. lusitaniae, B. bissettii, and B. spielmanii by means of a novel MLSA scheme based on chromosomal housekeeping genes (30, 48).     

Role of Geobacter sulfurreducens Outer Surface c-Type Cytochromes in Reduction of Soil Humic Acid and Anthraquinone-2,6-Disulfonate

Deleting individual genes for outer surface c-type cytochromes in Geobacter sulfurreducens partially inhibited the reduction of humic substances and anthraquinone-2,6,-disulfonate. Complete inhibition was obtained only when five of these genes were simultaneously deleted, suggesting that diverse outer surface cytochromes can contribute to the reduction of humic substances and other extracellular quinones.Humic substances can play an important role in the reduction of Fe(III), and possibly other metals, in sedimentary environments (6, 34). Diverse dissimilatory Fe(III)-reducing microorganisms (3, 5, 7, 9, 11, 19-22, 25) can transfer electrons onto the quinone moieties of humic substances (38) or the model compound anthraquinone-2,6-disulfonate (AQDS). Reduced humic substances or AQDS abiotically reduces Fe(III) to Fe(II), regenerating the quinone. Electron shuttling in this manner can greatly increase the rate of electron transfer to insoluble Fe(III) oxides, presumably because soluble quinone-containing molecules are more accessible for microbial reduction than insoluble Fe(III) oxides (19, 22). Thus, catalytic amounts of humic substances have the potential to dramatically influence rates of Fe(III) reduction in soils and sediments and can promote more rapid degradation of organic contaminants coupled to Fe(III) reduction (1, 2, 4, 10, 24).To our knowledge, the mechanisms by which Fe(III)-reducing microorganisms transfer electrons to humic substances have not been investigated previously for any microorganism. However, reduction of AQDS has been studied using Shewanella oneidensis (17, 40). Disruption of the gene for MtrB, an outer membrane protein required for proper localization of outer membrane cytochromes (31), inhibited reduction of AQDS, as did disruption of the gene for the outer membrane c-type cytochrome, MtrC (17). However, in each case inhibition was incomplete, and it was suggested that there was a possibility of some periplasmic reduction (17), which would be consistent with the ability of AQDS to enter the cell (40).The mechanisms for electron transfer to humic substances in Geobacter species are of interest because molecular studies have frequently demonstrated that Geobacter species are the predominant Fe(III)-reducing microorganisms in sedimentary environments in which Fe(III) reduction is an important process (references 20, 32, and 42 and references therein). Geobacter sulfurreducens has routinely been used for investigations of the physiology of Geobacter species because of the availability of its genome sequence (29), a genetic system (8), and a genome-scale metabolic model (26) has made it possible to take a systems biology approach to understanding the growth of this organism in sedimentary environments (23).     

Cultivation of Fastidious Bacteria by Viability Staining and Micromanipulation in a Soil Substrate Membrane System

Soil substrate membrane systems allow for microcultivation of fastidious soil bacteria as mixed microbial communities. We isolated established microcolonies from these membranes by using fluorescence viability staining and micromanipulation. This approach facilitated the recovery of diverse, novel isolates, including the recalcitrant bacterium Leifsonia xyli, a plant pathogen that has never been isolated outside the host.The majority of bacterial species have never been recovered in the laboratory (1, 14, 19, 24). In the last decade, novel cultivation approaches have successfully been used to recover “unculturables” from a diverse range of divisions (23, 25, 29). Most strategies have targeted marine environments (4, 23, 25, 32), but soil offers the potential for the investigation of vast numbers of undescribed species (20, 29). Rapid advances have been made toward culturing soil bacteria by reformulating and diluting traditional media, extending incubation times, and using alternative gelling agents (8, 21, 29).The soil substrate membrane system (SSMS) is a diffusion chamber approach that uses extracts from the soil of interest as the growth substrate, thereby mimicking the environment under investigation (12). The SSMS enriches for slow-growing oligophiles, a proportion of which are subsequently capable of growing on complex media (23, 25, 27, 30, 32). However, the SSMS results in mixed microbial communities, with the consequent difficulty in isolation of individual microcolonies for further characterization (10).Micromanipulation has been widely used for the isolation of specific cell morphotypes for downstream applications in molecular diagnostics or proteomics (5, 15). This simple technology offers the opportunity to select established microcolonies of a specific morphotype from the SSMS when combined with fluorescence visualization (3, 11). Here, we have combined the SSMS, fluorescence viability staining, and advanced micromanipulation for targeted isolation of viable, microcolony-forming soil bacteria.     

Functional diversity and electron donor dependence of microbial populations capable of U(VI) reduction in radionuclide-contaminated subsurface sediments

In order to elucidate the potential mechanisms of U(VI) reduction for the optimization of bioremediation strategies, the structure-function relationships of microbial communities were investigated in microcosms of subsurface materials cocontaminated with radionuclides and nitrate. A polyphasic approach was used to assess the functional diversity of microbial populations likely to catalyze electron flow under conditions proposed for in situ uranium bioremediation. The addition of ethanol and glucose as supplemental electron donors stimulated microbial nitrate and Fe(III) reduction as the predominant terminal electron-accepting processes (TEAPs). U(VI), Fe(III), and sulfate reduction overlapped in the glucose treatment, whereas U(VI) reduction was concurrent with sulfate reduction but preceded Fe(III) reduction in the ethanol treatments. Phyllosilicate clays were shown to be the major source of Fe(III) for microbial respiration by using variable-temperature Mössbauer spectroscopy. Nitrate- and Fe(III)-reducing bacteria (FeRB) were abundant throughout the shifts in TEAPs observed in biostimulated microcosms and were affiliated with the genera Geobacter, Tolumonas, Clostridium, Arthrobacter, Dechloromonas, and Pseudomonas. Up to two orders of magnitude higher counts of FeRB and enhanced U(VI) removal were observed in ethanol-amended treatments compared to the results in glucose-amended treatments. Quantification of citrate synthase (gltA) levels demonstrated a stimulation of Geobacteraceae activity during metal reduction in carbon-amended microcosms, with the highest expression observed in the glucose treatment. Phylogenetic analysis indicated that the active FeRB share high sequence identity with Geobacteraceae members cultivated from contaminated subsurface environments. Our results show that the functional diversity of populations capable of U(VI) reduction is dependent upon the choice of electron donor.Uranium contamination in subsurface environments is a widespread problem at mining and milling sites across North America, South America, and Eastern Europe (1). Uranium in the oxidized state, U(VI), is highly soluble and toxic and thus is a potential contaminant to local drinking-water supplies (46). Nitrate is often a cocontaminant with U(VI) as a result of the use of nitric acid in the processing of uranium and uranium-bearing waste (6, 45). Oxidized uranium can be immobilized in contaminated groundwater through the reduction of U(VI) to insoluble U(IV) by indirect (abiotic) and direct (enzymatic) processes catalyzed by microorganisms. Current remediation practices favor the stimulation of reductive uranium immobilization catalyzed by indigenous microbial communities along with natural attenuation and monitoring (5, 24, 40, 44, 65, 68, 69). Microbial uranium reduction activity in contaminated subsurface environments is often limited by carbon or electron donor availability (13, 24, 44, 69). Previous studies have indicated that U(VI) reduction does not proceed until nitrate is depleted (13, 16, 24, 44, 68, 69), as high nitrate concentrations inhibit the reduction of U(VI) by serving as a competing and more energetically favorable terminal electron acceptor for microorganisms (11, 16). The fate and transport of uranium in groundwater are also strongly linked through sorption and precipitation processes to the bioreduction of Fe minerals, including oxides, layer-silicate clay minerals, and sulfides (7, 23, 53).In order to appropriately design U(VI) bioremediation strategies, the potential function and phylogenetic structure of indigenous subsurface microbial communities must be further understood (24, 34, 46). Conflicting evidence has been presented on which microbial groups, Fe(III)- or sulfate-reducing bacteria (FeRB or SRB), effectively catalyze the reductive immobilization of U(VI) in the presence of amended electron donors (5, 44, 69). The addition of acetate to the subsurface at a uranium-contaminated site in Rifle, Colorado, initially stimulated FeRB within the family Geobacteraceae to reduce U(VI) (5, 65). However, with long-term acetate addition, SRB within the family Desulfobacteraceae, which are not capable of U(VI) reduction, increased in abundance and a concomitant reoxidation of U(IV) was observed (5, 65). At a uranium-contaminated site in Oak Ridge, Tennessee, in situ and laboratory-based experiments successfully employed ethanol amendments to stimulate denitrification followed by the reduction of U(VI) by indigenous microbial communities (13, 24, 44, 48, 50, 57, 68). In these studies, ethanol amendments stimulated both SRB and FeRB, with SRB likely catalyzing the reduction of U(VI). This suggests that the potential for bioremediation will be affected by the choice of electron donor amendment through effects on the functional diversity of U(VI)-reducing microbial populations. As uranium reduction is dependent on the depletion of nitrate, the microbial populations mediating nitrate reduction are also critical to the design of bioremediation strategies. Although nitrate-reducing bacteria (NRB) have been studied extensively in subsurface environments (2, 15, 19, 24, 56, 58, 70), the mechanisms controlling the in situ metabolism of NRB remain poorly understood.The dynamics of microbial populations capable of U(VI) reduction in subsurface sediments are poorly understood, and the differences in the microbial community dynamics during bioremediation have not been explored. Based on the results of previous studies (13, 44, 49, 57, 68, 69), we hypothesized that the activity of nitrate- and Fe(III)-reducing microbial populations, catalyzing the reductive immobilization of U(VI) in subsurface radionuclide-contaminated sediments, would be dependent on the choice of electron donor. The objectives of the present study were (i) to characterize structure-function relationships for microbial groups likely to catalyze or limit U(VI) reduction in radionuclide-contaminated sediments and (ii) to further develop a proxy for the metabolic activity of FeRB. Microbial activity was assessed by monitoring terminal electron-accepting processes (TEAPs), electron donor utilization, and Fe(III) mineral transformations in microcosms conducted with subsurface materials cocontaminated with high levels of U(VI) and nitrate. In parallel, microbial functional groups (i.e., NRB and FeRB) were enumerated and characterized using a combination of cultivation-dependent and -independent methods.     

Use of Ichip for High-Throughput In Situ Cultivation of “Uncultivable” Microbial Species

One of the oldest unresolved microbiological phenomena is why only a small fraction of the diverse microbiological population grows on artificial media. The “uncultivable” microbial majority arguably represents our planet''s largest unexplored pool of biological and chemical novelty. Previously we showed that species from this pool could be grown inside diffusion chambers incubated in situ, likely because diffusion provides microorganisms with their naturally occurring growth factors. Here we utilize this approach and develop a novel high-throughput platform for parallel cultivation and isolation of previously uncultivated microbial species from a variety of environments. We have designed and tested an isolation chip (ichip) composed of several hundred miniature diffusion chambers, each inoculated with a single environmental cell. We show that microbial recovery in the ichip exceeds manyfold that afforded by standard cultivation, and the grown species are of significant phylogenetic novelty. The new method allows access to a large and diverse array of previously inaccessible microorganisms and is well suited for both fundamental and applied research.It has been known for over a century that the overwhelming majority of microbial species do not grow on synthetic media in vitro and remain unexplored (13, 32, 37, 39, 40, 43). The rRNA and metagenomics approaches demonstrated a spectacular diversity of these uncultivated species (11, 21, 25-27, 30, 36). Accessing this “missing” microbial diversity is of significant interest for both basic and applied sciences and has been recognized as one of the principal challenges for microbiology today (12, 29, 41). In recent years, technical advances in cultivation methodologies have recovered a diverse set of ecologically relevant species (1, 3, 5, 7, 15, 20, 24, 28, 33, 42). However, by and large the gap between microbial diversity in nature and that in culture collections remains unchanged, and most microbial phyla still have no cultivable representatives (25, 29). Earlier, we developed a novel method of in situ cultivation of environmental microorganisms inside diffusion chambers (15). The rationale for such an approach was that diffusion would provide cells inside the chamber with naturally occurring growth components and enable those species that grew in nature at the time of the experiment to also grow inside the diffusion chambers. Expectedly, this method yields a rate of microbial recovery many times larger than those of standard techniques. Even so, this method is laborious and does not allow an efficient, high-throughput isolation of microbial species en masse. This limits the method''s applicability, for example, in the drug discovery effort. Here we transform this methodology into a high-throughput technology platform for massively parallel cultivation of “uncultivable” species. Capitalizing on earlier microfluidics methods developed for microbial storage and screening (4, 16), we have designed and tested an isolation chip, or ichip for short, which consists of hundreds of miniature diffusion chambers. If each diffusion minichamber is loaded with a single cell, the resulting culture is monospecific. The ichip thus allows microbial growth and isolation into pure culture in one step. Here we demonstrate that cultivation of environmental microorganisms inside the ichip incubated in situ leads to a significantly increased colony count over that observed on synthetic media. Perhaps even more significantly, species grown in ichips are different from those registered in standard petri dishes and are highly novel.     

Characterization of the Replication,Transfer, and Plasmid/Lytic Phage Cycle of the Streptomyces Plasmid-Phage pZL12

We report here the isolation and recombinational cloning of a large plasmid, pZL12, from endophytic Streptomyces sp. 9R-2. pZL12 comprises 90,435 bp, encoding 112 genes, 30 of which are organized in a large operon resembling bacteriophage genes. A replication locus (repA) and a conjugal transfer locus (traA-traC) were identified in pZL12. Surprisingly, the supernatant of a 9R-2 liquid culture containing partially purified phage particles infected 9R-2 cured of pZL12 (9R-2X) to form plaques, and a phage particle (φZL12) was observed by transmission electron microscopy. Major structural proteins (capsid, portal, and tail) of φZL12 virions were encoded by pZL12 genes. Like bacteriophage P1, linear φZL12 DNA contained ends from a largely random pZL12 sequence. There was also a hot end sequence in linear φZL12. φZL12 virions efficiently infected only one host, 9R-2X, but failed to infect and form plaques in 18 other Streptomyces strains. Some 9R-2X spores rescued from lysis by infection of φZL12 virions contained a circular pZL12 plasmid, completing a cycle comprising autonomous plasmid pZL12 and lytic phage φZL12. These results confirm pZL12 as the first example of a plasmid-phage in Streptomyces.Streptomyces species, a major source of antibiotics and pharmacologically active metabolites, are Gram-positive, mycelial bacteria with high G+C content in their DNA (15). They usually harbor conjugative circular and/or linear plasmids, propagating in autonomous and/or chromosomally integrated forms (14). Most Streptomyces circular plasmids reported are small (8 to 14 kb), including rolling-circle-replication (RCR) plasmids (pIJ101, pJV1, pSG5, pSN22, pSVH1, pSB24.2, pSY10, pSNA1, pSLG33, pEN2701, etc.) (12, 14) and chromosomally integrating/autonomous plasmids (SLP1 and pSAM2) (4, 27, 28). Some theta replication plasmids are of intermediate size (31 to 39 kb), such as SCP2, pFP1, and pFP11 (13, 40). These theta replication loci comprise a rep gene and an adjacent noncoding or iteron sequence, to which Rep protein binds specifically in vitro (10, 40). The occurrence of an ∼163-kb large plasmid, pSV1, in Streptomyces violaceoruber SANK95570 was confirmed (1, 37), but this plasmid could not be physically isolated by standard procedures for plasmid preparation (17). In contrast to more than 30 genes for conjugal transfer on the Escherichia coli F plasmid (20), Streptomyces plasmids usually need a single tra gene (encoding a DNA translocase containing a cell division FtsK/SpoIIIE domain) (15, 29). The transfer of Streptomyces circular plasmids involves binding of the nonnicked double-stranded DNA (dsDNA) by multimers of Tra proteins at a noncoding sequence and ATP hydrolysis-dependent translocation of this DNA through the hyphal tips of the Streptomyces mycelium (15, 32).Numerous Streptomyces phages have been described, including φC31 (22), SAt1 (26), TG1 (11), FP43 (24), φSPK1 (19), φSC623 (34), DAH2/DAH4/DAH5/DAH6 (6), and mu1/6 (9). They range in size from 36 kb (19) to 121 kb (6), with 50 to 71.2% GC content (9, 23, 35). Streptomyces phages often have a wide host range; for example, 16 of 27 Streptomyces strains are susceptible to infection by φSPK1 (19), and phage FP43 transduces species of Streptoverticillium, Chainia, and Sacchropolyspora (24). φC31 is the most-studied Streptomyces phage and cloning vector (8). The sequences of the φC31 head proteins (e.g., portal, capsid, and head protease) resemble those of other bacterial dsDNA phages, suggesting evolutionary relationships to other viruses (35).We report here the isolation and recombinational cloning of a 90,435-bp plasmid, pZL12, from endophytic Streptomyces sp. 9R-2 and the characterization of its replication and transfer. Surprisingly, the supernatant of 9R-2 liquid culture infected 9R-2 cured of pZL12 to form plaques. A cycle comprising autonomous plasmid pZL12 and lytic phage φZL12 is described.     

Conjugative Plasmid Transfer and Adhesion Dynamics in an Escherichia coli Biofilm

A conjugative plasmid from the catheter-associated urinary tract infection strain Escherichia coli MS2027 was sequenced and annotated. This 42,644-bp plasmid, designated pMAS2027, contains 58 putative genes and is most closely related to plasmids belonging to incompatibility group X (IncX1). Plasmid pMAS2027 encodes two important virulence factors: type 3 fimbriae and a type IV secretion (T4S) system. Type 3 fimbriae, recently found to be functionally expressed in E. coli, played an important role in biofilm formation. Biofilm formation by E. coli MS2027 was specifically due to expression of type 3 fimbriae and not the T4S system. The T4S system, however, accounted for the conjugative ability of pMAS2027 and enabled a non-biofilm-forming strain to grow as part of a mixed biofilm following acquisition of this plasmid. Thus, the importance of conjugation as a mechanism to spread biofilm determinants was demonstrated. Conjugation may represent an important mechanism by which type 3 fimbria genes are transferred among the Enterobacteriaceae that cause device-related infections in nosocomial settings.Bacterial biofilms are complex communities of bacterial cells living in close association with a surface (17). Bacterial cells in these protected environments are often resistant to multiple factors, including antimicrobials, changes in the pH, oxygen radicals, and host immune defenses (19, 38). Biofilm formation is a property of many bacterial species, and a range of molecular mechanisms that facilitate this process have been described (2, 3, 11, 14, 16, 29, 33, 34). Often, the ability to form a biofilm is dependent on the production of adhesins on the bacterial cell surface. In Escherichia coli, biofilm formation is enhanced by the production of certain types of fimbriae (e.g., type 1 fimbriae, type 3 fimbriae, F1C, F9, curli, and conjugative pili) (14, 23, 25, 29, 33, 39, 46), cell surface adhesins (e.g., autotransporter proteins such as antigen 43, AidA, TibA, EhaA, and UpaG) (21, 34, 35, 40, 43), and flagella (22, 45).The close proximity of bacterial cells in biofilms creates an environment conducive for the exchange of genetic material. Indeed, plasmid-mediated conjugation in monospecific and mixed E. coli biofilms has been demonstrated (6, 18, 24, 31). The F plasmid represents the best-characterized conjugative system for biofilm formation by E. coli. The F pilus mediates adhesion to abiotic surfaces and stabilizes the biofilm structure through cell-cell interactions (16, 30). Many other conjugative plasmids also contribute directly to biofilm formation upon derepression of the conjugative function (16).One example of a conjugative system employed by gram-negative Enterobacteriaceae is the type 4 secretion (T4S) system. The T4S system is a multisubunit structure that spans the cell envelope and contains a secretion channel often linked to a pilus or other surface filament or protein (8). The Agrobacterium tumefaciens VirB-VirD4 system is the archetypical T4S system and is encoded by 11 genes in the virB operon and one gene (virD4) in the virD operon (7, 8). Genes with strong homology to genes in the virB operon have also been identified on other conjugative plasmids. For example, the pilX1 to pilX11 genes on the E. coli R6K IncX plasmid and the virB1 to virB11 genes are highly conserved at the nucleotide level (28).We recently described identification and characterization of the mrk genes encoding type 3 fimbriae in a uropathogenic strain of E. coli isolated from a patient with a nosocomial catheter-associated urinary tract infection (CAUTI) (29). The mrk genes were located on a conjugative plasmid (pMAS2027) and were strongly associated with biofilm formation. In this study we determined the entire sequence of plasmid pMAS2027 and revealed the presence of conjugative transfer genes homologous to the pilX1 to pilX11 genes of E. coli R6K (in addition to the mrk genes). We show here that biofilm formation is driven primarily by type 3 fimbriae and that the T4S apparatus is unable to mediate biofilm growth in the absence of the mrk genes. Finally, we demonstrate that conjugative transfer of pMAS2027 within a mixed biofilm confers biofilm formation properties on recipient cells due to acquisition of the type 3 fimbria-encoding mrk genes.     

Antibiotic Resistance Markers for Genetic Manipulations of Leptospira spp.

We measured the frequency of appearance of spontaneous mutants resistant to gentamicin, kanamycin, streptomycin, and spectinomycin in saprophytic and pathogenic Leptospira strains. The mutations responsible for the spontaneous resistance to streptomycin and spectinomycin were identified in the rpsL and rrs genes, respectively. We also generated a gentamicin resistance cassette that allows the use of a third selectable marker in leptospires. These results may facilitate further advances in gene transfer systems in Leptospira spp.Our understanding of leptospiral pathogenesis depends on reliable genetic tools for fully characterizing genes of interest. Significant advances in genetics of Leptospira spp. have been made over the last few years (8, 11). For generating antibiotic resistance genetic markers, our group focused on antibiotics other than those used therapeutically. We therefore excluded the use of β-lactams, as they are used to treat leptospirosis, which is an emerging disease with more 500,000 severe cases occurring annually (8). Plasmid DNA can be introduced into Leptospira by electroporation (2, 21) or conjugation (16). In 1990, Saint Girons et al. used the replication origin of the LE1 leptophage (22) to generate a plasmid that was able to replicate autonomously in both the saprophyte Leptospira biflexa and Escherichia coli (21). They used resistance to kanamycin (Kan), which was conferred by a gene from the Gram-positive bacterium Enterococcus faecalis, as a genetic marker to select for introduced DNA. Another marker, a spectinomycin (Spc) resistance cassette from Staphylococcus aureus, was also used as a selectable marker in Leptospira spp. (1). Further studies have used Spc and Kan markers to screen for transformants resulting from plasmid replication or chromosomal integration in leptospires (8, 11). As the proportion of allelic-exchange mutants is low and as chromosomal integration generally occurs through a single recombination event, a plasmid containing the rpsL wild-type gene as a counterselectable marker in a streptomycin (Str)-resistant strain of L. biflexa (due to a mutation in rpsL) was also used to eliminate clones harboring the plasmid and/or clones that have integrated the plasmid through a single-crossover event (9, 17, 20).     

The Putative Coupling Protein TcpA Interacts with Other pCW3-Encoded Proteins To Form an Essential Part of the Conjugation Complex

Conjugative plasmids encode antibiotic resistance determinants or toxin genes in the anaerobic pathogen Clostridium perfringens. The paradigm conjugative plasmid in this bacterium is pCW3, a 47-kb tetracycline resistance plasmid that encodes the unique tcp transfer locus. The tcp locus consists of 11 genes, intP and tcpA-tcpJ, at least three of which, tcpA, tcpF, and tcpH, are essential for the conjugative transfer of pCW3. In this study we examined protein-protein interactions involving TcpA, the putative coupling protein. Use of a bacterial two-hybrid system identified interactions between TcpA and TcpC, TcpG, and TcpH. This analysis also demonstrated TcpA, TcpC, and TcpG self-interactions, which were confirmed by chemical cross-linking studies. Examination of a series of deletion and site-directed derivatives of TcpA identified the domains and motifs required for these interactions. Based on these results, we have constructed a model for this unique conjugative transfer apparatus.Conjugation systems are important contributors to the dissemination of antibiotic resistance determinants and virulence factors. Extensive analysis of conjugative plasmids from gram-negative bacteria has led to the elucidation of a general mechanism of conjugative transfer (10, 22). In this process, the transferred DNA is processed by components of a relaxosome complex. Specifically, the DNA is nicked at the origin of transfer (oriT) by a relaxase, which remains covalently coupled to the transferred DNA strand. The single-stranded DNA complex then interacts with the coupling protein, a DNA-dependent ATPase that provides the energy to actively pump the DNA through the mating pair formation (Mpf) complex into the recipient cell (36). The coupling protein interacts with both DNA processing proteins and components of the Mpf complex (1, 4, 12, 35, 38). These interactions have been demonstrated using bacterial and yeast two-hybrid approaches as well as gel filtration, pull-down, and coimmunoprecipitation studies.The mechanism of conjugative transfer has yet to be precisely determined for conjugative plasmids from gram-positive bacteria although bioinformatics analysis has identified similar gene arrangements and conservation of gene sequences within the transfer regions encoded on conjugative plasmids identified from strains of streptococcal, staphylococcal, enterococcal, and lactococcal origin (15). It was proposed that gram-positive and gram-negative conjugation systems utilize a similar transfer mechanism (15).In the anaerobic pathogen Clostridium perfringens conjugative plasmids have been shown to encode antibiotic resistance genes or extracellular toxins (3, 8, 9, 18). Although the contribution of conjugation to disease dissemination has not been systematically evaluated, it has been proposed that transfer of the C. perfringens enterotoxin plasmid pCPF4969 to normal flora isolates of C. perfringens may contribute to the severity of disease caused by non-food-borne isolates of C. perfringens (9).The prototype conjugative plasmid in C. perfringens is the 47-kb tetracycline resistance plasmid, pCW3. The complete sequence of pCW3 has been determined, and its unique replication protein and conjugation locus have been identified (8). Bioinformatics analysis of this C. perfringens tcp conjugation locus identified several proteins with limited similarity to proteins encoded within the transfer region of the conjugative transposon, Tn916 (8). The role of the tcp locus in the transfer of pCW3 has been confirmed by isolation of independent tcpA, tcpF, and tcpH mutants and subsequent complementation studies (8, 29). Since the region that encompasses the tcp locus is conserved in all conjugative plasmids from C. perfringens (2, 3, 8, 9, 18, 27) and since divergent tcpA homologues can complement a pCW3tcpA mutant (29), it appears that the conjugative transfer of both antibiotic resistance and toxin plasmids from this bacterium utilizes a common but poorly understood mechanism. Note that the C. perfringens tcp conjugation locus is different from the transfer regions of conjugative plasmids from other gram-positive bacteria.We have recently shown that the essential conjugation protein TcpH, a putative membrane-associated Mpf complex component, is localized to the poles of C. perfringens cells, as is another essential conjugation protein, TcpF (37). TcpH has also been shown to interact with itself and with the pCW3-encoded TcpC protein (37). In this study we have focused on the essential conjugation protein TcpA. Since TcpA encodes an FtsK/SpoIIIE domain found in DNA translocases (8), it is proposed that TcpA is involved in the movement of DNA during conjugative transfer, fulfilling a role equivalent to that of coupling proteins in other conjugation systems. Like such proteins, TcpA encodes two N-terminal transmembrane domains (TMDs) and a C-terminal cytoplasmic region that contains three motifs predicted to be involved in ATP binding and hydrolysis (8). Our previous studies revealed that the conserved motifs, motif I (Walker A box), motif II (Walker B box), and motif III (RAAG box), are essential for the function of TcpA. The C-terminal 61 amino acids (aa), though not essential for TcpA function, were shown to be important for efficient transfer of pCW3, as were the putative TMDs (29).To further investigate pCW3 transfer and the role of TcpA in this process, we have used bacterial two-hybrid analysis to examine protein-protein interactions involving TcpA. Using this system, interactions were observed between TcpA and itself, TcpC, TcpG, and TcpH. In addition, TcpC and TcpG were also found to self-interact. By combining these data with other data generated in this laboratory (37), we have constructed a model for the conjugative transfer of pCW3.     

Rickettsia felis Infection in a Common Household Insect Pest,Liposcelis bostrychophila (Psocoptera: Liposcelidae)

Many species of Rickettsia are well-known mammalian pathogens transmitted by blood-feeding arthropods. However, molecular surveys are continually uncovering novel Rickettsia species, often in unexpected hosts, including many arthropods that do not feed on blood. This study reports a systematic molecular characterization of a Rickettsia infecting the psocid Liposcelis bostrychophila (Psocoptera: Liposcelidae), a common and cosmopolitan household pest. Surprisingly, the psocid Rickettsia is shown to be Rickettsia felis, a human pathogen transmitted by fleas that causes serious morbidity and occasional mortality. The plasmid from the psocid R. felis was sequenced and was found to be virtually identical to the one in R. felis from fleas. As Liposcelis insects are often intimately associated with humans and other vertebrates, it is speculated that they acquired R. felis from fleas. Whether the R. felis in psocids causes disease in vertebrates is not known and warrants further study.Many species of Rickettsia are well-known mammalian pathogens that are transmitted by blood-feeding arthropods via bites or feces and can cause mild to fatal diseases in humans (33). Some species are also considered potential bioterrorism agents (4). Most Rickettsia research has focused on pathogens that are found in two closely related species groups, the typhus and spotted fever groups, such as Rickettsia prowazekii, Rickettsia rickettsii, and Rickettsia typhi, the causal agents of epidemic typhus, Rocky Mountain spotted fever, and murine typhus, respectively (3, 4, 33). However, recent surveys suggest that Rickettsia bacteria are much more widespread than previously suspected and that they are being detected in novel hosts, the vast majority of which are arthropods, including many that do not feed on blood (29, 45).The number of new rickettsial species that cause diseases in humans is rapidly increasing (33). One such species that has been generating much interest in recent years is Rickettsia felis, the causative agent of a murine typhus-like disease (1, 2, 13, 16, 17, 28, 44). The disease is often unrecognized, and even though it is considered clinically mild, it can cause severe illness and death in older patients and in cases of delayed diagnosis (2). R. felis was identified only in 1990 (1) and has since been found worldwide in fleas, where it is maintained transovarially and can reach high infection rates (e.g., 86% to 94% in cat fleas) (2, 3, 44), as well as in ticks and mites (34). While experimental infections have confirmed that R. felis is transmitted to vertebrate hosts via blood feeding and that R. felis occurs in an infectious extracellular state (39), it is not known whether transmission can also occur through contamination of broken skin by infected vector feces, as in R. typhi (3, 34).A number of features distinguish R. felis from species in both the typhus and spotted fever groups. Lately, it has been proposed that R. felis be in its own group, allied with Rickettsia akari and Rickettsia australis, the causal agents of rickettsial pox and Queensland tick typhus, respectively, and a number of recently discovered strains infecting insects that do not feed on blood (16, 17, 29, 45). Moreover, R. felis was the first Rickettsia species shown to have a plasmid (28). While plasmids now appear to be quite widespread in the genus, the R. felis plasmid stands out with respect to its relatively large size and distinctive gene content (5, 6, 9, 14, 17).This study reports that a common and cosmopolitan insect, the psocid Liposcelis bostrychophila (Psocoptera: Liposcelidae) harbors R. felis. Liposcelids are the closest free-living relatives of parasitic lice (19) and are well-known for their close proximity to humans, particularly as pests in houses and grain storage facilities (8, 41). Through 16S rRNA gene sequencing, L. bostrychophila was recently shown to harbor a strain of Rickettsia (29, 30, 42). A systematic molecular characterization of this Rickettsia was conducted, demonstrating that it is authentic R. felis. Furthermore, the psocid symbiont plasmid was sequenced and was shown to be virtually identical to the plasmid from R. felis that infects cat fleas.     

Analyses of Current-Generating Mechanisms of Shewanella loihica PV-4 and Shewanella oneidensis MR-1 in Microbial Fuel Cells

Although members of the genus Shewanella have common features (e.g., the presence of decaheme c-type cytochromes [c-cyts]), they are widely variable in genetic and physiological features. The present study compared the current-generating ability of S. loihica PV-4 in microbial fuel cells (MFCs) with that of well-characterized S. oneidensis MR-1 and examined the roles of c-cyts in extracellular electron transfer. We found that strains PV-4 and MR-1 exhibited notable differences in current-generating mechanisms. While the MR-1 MFCs maintained a constant current density over time, the PV-4 MFCs continued to increase in current density and finally surpassed the MR-1 MFCs. Coulombic efficiencies reached 26% in the PV-4 MFC but 16% in the MR-1 MFCs. Although both organisms produced quinone-like compounds, anode exchange experiments showed that anode-attached cells of PV-4 produced sevenfold more current than planktonic cells in the same chamber, while planktonic cells of MR-1 produced twice the current of the anode-attached cells. Examination of the genome sequence indicated that PV-4 has more c-cyt genes in the metal reductase-containing locus than MR-1. Mutational analysis revealed that PV-4 relied predominantly on a homologue of the decaheme c-cyt MtrC in MR-1 for current generation, even though it also possesses two homologues of the decaheme c-cyt OmcA in MR-1. These results suggest that current generation in a PV-4 MFC is in large part accomplished by anode-attached cells, in which the MtrC homologue constitutes the main path of electrons toward the anode.Some species of dissimilatory metal-reducing bacteria (DMRB) are able to reduce solid metal oxides as terminal electron acceptors and generate currents in microbial fuel cells (MFCs) (2, 11, 14, 30, 46). Although mixed cultures are often used in MFC experiments (13), studies seeking a mechanistic understanding of electron transfer to electrode surfaces typically target pure cultures of such DMRB, due to the complexity in microbial communities. Presently, two model DMRB, Shewanella oneidensis MR-1 and Geobacter sulfurreducens PCA (2, 3, 12, 18, 31), are used in most investigations.S. oneidensis MR-1 is a metabolically diverse DMRB that has been studied extensively for its potential use in bioremediation applications. For this reason, MR-1 was the first Shewanella species to have its genome completely sequenced and annotated (10). In addition, since the first report in 1999 when this microorganism was shown to have the ability to transfer electrons to the electrode without an exogenously added mediator (14), it has also become one of the model organisms for the study of electron transfer mechanisms in MFCs.Although the molecular mechanisms for extracellular electron transfer have not yet been elucidated fully, c-type cytochromes (c-cyts) appear to be the key cellular components involved in this process (38). In S. oneidensis MR-1, OmcA and MtrC are outer membrane (OM), decaheme c-cyts that are considered to be involved in the direct (directly attached) electron transfer to solid metal oxides and anodes of MFCs (9, 20, 22, 23, 47). Several pieces of evidence suggest that OmcA and MtrC form a complex and act in a cooperative manner (33, 37, 42), and these results correlate with the fact that the genes encoding these proteins constitute an operon-like cluster in the chromosome (1). It has also been shown that MtrC and OmcA have overlapping functions as terminal reductases of metal oxides (25, 38). OmcA and MtrC are also present on the surface of nanowires and may be involved in the long-range transfer of electrons (8). In addition to direct electron transfer, MR-1 has the ability to produce water-soluble electron-shuttle compounds (quinones and flavins) that are involved in the mediated electron transfer from cells to distant solid electron acceptors (metal oxides or MFC anodes) (21, 27, 44).Recently, the genome sequences of nearly 20 Shewanella strains have been completed and annotated, opening the door to study the diversity of their extracellular electron transfer mechanisms. A comparison of their genomes has shown that although they have some consensus OM c-cyt genes, variations exist in the number and order of these genes in their metal reductase-containing loci (6). One such species is S. loihica strain PV-4, which was recently isolated from an iron-rich microbial mat near a deep-sea hydrothermal vent located on the Loihi Seamount in Hawaii (7, 32). The phenotypic and phylogenetic characteristics of PV-4 were determined, with a subsequent study focusing on the metal reduction and iron biomineralization capabilities of this bacterium (32). Initial experiments performed in our laboratory revealed that PV-4 developed a c-cyt-dependent deep red color that was much more striking than that of strain MR-1 when grown anaerobically with iron oxide as the terminal electron acceptor (26). This allowed us to assume that PV-4 could have a high extracellular electron transfer ability. Accordingly, the present study evaluated the current-producing ability of strain PV-4 in MFCs and examined the roles of some c-cyts in extracellular electron transfer. Special attention was paid to the comparison of PV-4 with MR-1 to reveal differences in mechanisms for extracellular electron transfer. We report herein differences between these strains in the roles of OM c-cyts for extracellular electron transfer, the behaviors and metabolic patterns of MFC, and the resultant MFC performances.