A Novel Dehalobacter Species Is Involved in Extensive 4,5,6,7-Tetrachlorophthalide Dechlorination

The purpose of this study was the enrichment and phylogenetic identification of bacteria that dechlorinate 4,5,6,7-tetrachlorophthalide (commercially designated “fthalide”), an effective fungicide for rice blast disease. Sequential transfer culture of a paddy soil with lactate and fthalide produced a soil-free enrichment culture (designated the “KFL culture”) that dechlorinated fthalide by using hydrogen, which is produced from lactate. Phylogenetic analysis based on 16S rRNA genes revealed the dominance of two novel phylotypes of the genus Dehalobacter (FTH1 and FTH2) in the KFL culture. FTH1 and FTH2 disappeared during culture transfer in medium without fthalide and increased in abundance with the dechlorination of fthalide, indicating their growth dependence on the dechlorination of fthalide. Dehalobacter restrictus TEA is their closest relative, with 97.5% and 97.3% 16S rRNA gene similarities to FTH1 and FTH2, respectively.4,5,6,7-Tetrachlorophthalide (commercially designated “fthalide”) is an effective fungicide for rice blast disease, which inhibits melanin biosynthesis and the formation of the mature appressorial cells of the rice blast pathogen on the host plant (5, 16). Fthalide has been reported to be reductively dechlorinated in soil (16) and compost (28), although its fates in paddy soil and the fthalide-dechlorinating bacteria are unknown. Besides fthalide, polychlorinated aromatic compounds are known to be reductively dechlorinated by the bacteria of several phyla. Six strains of Desulfitobacterium spp. of the phylum Firmicutes (2, 3, 6, 10, 23, 29) and Desulfomonile tiedjei DCB-1 of the phylum Proteobacteria (21) can dechlorinate polychlorinated phenols. Three strains of the phylum Chloroflexi can dechlorinate a variety of compounds, including polychlorinated phenols, benzenes, biphenyls, or dibenzo-p-dioxins: Dehalococcoides ethenogenes 195 (9, 19), Dehalococcoides sp. strain CBDB1 (1, 4), and strain DF-1 of Chloroflexi, collectively called the “o-17/DF-1 group” (18). Dehalococcoides spp. utilize hydrogen as an electron donor and acetate as a carbon source for growth coupled to the reductive dechlorination of chlorinated compounds (1, 12, 13, 19, 26). In contrast, Desulfitobacterium spp. can dechlorinate chlorinated compounds not only with hydrogen, but also organic acids, such as formate, pyruvate, lactate, or butyrate (3, 10, 23). Strain DF-1 can utilize hydrogen and formate for the dechlorination of polychlorinated biphenyls (PCBs) (18).In this study, bacteria that dechlorinate fthalide were enriched from a paddy soil with sequentially transferred cultures using a soil-free medium supplemented with single organic acids. Acetate, formate, lactate, and butyrate were used in this study because they are frequently used in the enrichment of dechlorinators and release hydrogen at different concentrations (8, 11, 14). Fthalide-dechlorinating bacteria in the enriched culture were phylogenetically identified based on the 16S rRNA gene with PCR-denaturing gradient gel electrophoresis (DGGE), a 16S rRNA gene clone library, and quantitative real-time PCR (qPCR).     

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.     

Immune Evasion Proteins of Murine Cytomegalovirus Preferentially Affect Cell Surface Display of Recently Generated Peptide Presentation Complexes

For recognition of infected cells by CD8 T cells, antigenic peptides are presented at the cell surface, bound to major histocompatibility complex class I (MHC-I) molecules. Downmodulation of cell surface MHC-I molecules is regarded as a hallmark function of cytomegalovirus-encoded immunoevasins. The molecular mechanisms by which immunoevasins interfere with the MHC-I pathway suggest, however, that this downmodulation may be secondary to an interruption of turnover replenishment and that hindrance of the vesicular transport of recently generated peptide-MHC (pMHC) complexes to the cell surface is the actual function of immunoevasins. Here we have used the model of murine cytomegalovirus (mCMV) infection to provide experimental evidence for this hypothesis. To quantitate pMHC complexes at the cell surface after infection in the presence and absence of immunoevasins, we generated the recombinant viruses mCMV-SIINFEKL and mCMV-Δm06m152-SIINFEKL, respectively, expressing the K^b-presented peptide SIINFEKL with early-phase kinetics in place of an immunodominant peptide of the viral carrier protein gp36.5/m164. The data revealed ∼10,000 K^b molecules presenting SIINFEKL in the absence of immunoevasins, which is an occupancy of ∼10% of all cell surface K^b molecules, whereas immunoevasins reduced this number to almost the detection limit. To selectively evaluate their effect on preexisting pMHC complexes, cells were exogenously loaded with SIINFEKL peptide shortly after infection with mCMV-SIINFEKA, in which endogenous presentation is prevented by an L174A mutation of the C-terminal MHC-I anchor residue. The data suggest that pMHC complexes present at the cell surface in advance of immunoevasin gene expression are downmodulated due to constitutive turnover in the absence of resupply.CD8 T cells recognize infected cells by interaction of their T-cell receptor (TCR) with a cell surface presentation complex composed of a cognate antigenic peptide bound to a presenting allelic form of a major histocompatibility complex class I (MHC-I) glycoprotein (77, 85, 97, 98). The number of such “peptide receptors” per cell has been estimated to be on the order of 10⁵ to 10⁶ for each MHC-I allomorph (for a review, see reference 82). Viral antigenic peptides are generated within infected cells by proteolytic processing of viral proteins, usually in the proteasome, and associate with nascent MHC-I proteins in the endoplasmic reticulum (ER) before the peptide-MHC (pMHC) complexes travel to the cell surface with the cellular vesicular flow (for reviews, see references 13, 87, 92, and 93). CD8 T cells have long been known to protect against cytomegalovirus (CMV) infection and disease in animal models (60, 72; reviewed in references 33 and 36) and in humans (9, 61, 67, 75, 76). As shown only recently in the murine CMV (mCMV) model of infection of immunocompromised mice by adoptive transfer of epitope-specific CD8 T cells, antiviral protection against CMV is indeed TCR mediated and epitope dependent. Specifically, memory cells purified by TCR-based epitope-specific cell sorting, as well as cells of a peptide-selected cytolytic T-lymphocyte line, protected against mCMV expressing the cognate antigenic peptide, the IE1 peptide 168-YPHFMPTNL-176 in this example, but failed to control infection with a recombinant mCMV expressing a peptide analogue in which the C-terminal MHC-I anchor residue leucine was replaced with alanine (3).Interference with the MHC-I pathway of antigen presentation has evolved as a viral immune evasion mechanism of CMVs and other viruses, mediated by virally encoded proteins that inhibit MHC-I trafficking to the cell surface (for reviews, see references 1, 24, 27, 29, 63, 70, 71, 84, and 95). These molecules are known as immunoevasins (50, 70, 89), as “viral proteins interfering with antigen presentation” (VIPRs) (95), or as negative “viral regulators of antigen presentation” (vRAPs) (34). Although the detailed molecular mechanisms differ between different CMV species in their respective hosts, the common biological outcome is the inhibition of antigen presentation. Accordingly, downmodulation of MHC-I cell surface expression is a hallmark of molecular immune evasion and actually led to the discovery of this class of molecules. Since CD8 T cells apparently protect against infection with wild-type CMV strains despite the expression of immunoevasins, the in vivo relevance of these molecules is an issue of current interest and investigation (for a review, see reference 14). As shown recently with the murine model, antigen presentation in infected host cells is not completely blocked for all epitopes, because pMHC complexes that are constitutively formed in sufficiently large amounts can exhaust the inhibitory capacity of the immunoevasins (40). Likewise, enhancing antigen processing conditionally with gamma interferon (IFN-γ) aids in peptide presentation in the presence of immunoevasins (18, 28). Thus, by raising the threshold of the amount of peptide required for presentation, immunoevasins determine whether a particular viral peptide can function as a protective epitope—an issue of relevance for rational vaccine design as well (94). Whereas deletion of immunoevasin genes gives only incremental improvement to the control of infection in immunocompetent mice (22, 51), expression of immunoevasins reduces the protective effect of adoptively transferred CD8 T cells in immunocompromised recipients (37, 40, 47, 48). In a bone marrow transplantation model, immunoevasins were recently found to contribute to enhanced and prolonged virus replication during hematopoietic reconstitution and, consequently, also to higher latent viral genome loads in the lungs and a higher incidence of virus recurrence (4). Notably, however, immunoevasins do not inhibit but, rather, enhance CD8 T-cell priming (5, 21, 22, 56), due to higher viral replication levels in draining lymph nodes associated with sustained antigen supply for the cross-priming of CD8 T cells by uninfected antigen-presenting cells (5).For mCMV, three molecules are proposed to function as vRAPs, only two of which are confirmed negative regulators that downmodulate cell surface MHC-I (34, 62, 89) and inhibit the presentation of antigenic peptides to CD8 T cells (34, 62). Immunoevasin gp40/m152 transiently interacts with MHC-I molecules and mediates their retention in a cis-Golgi compartment (96), whereas gp48/m06 stably binds to MHC-I molecules in the ER and mediates sorting of the complexes for lysosomal degradation by a mechanism that involves the cellular cargo sorting adaptor proteins AP1-A and AP3-A (73, 74). The third proposed immunoevasin of mCMV, gp34/m04 (46), also binds stably to MHC-I molecules. A function as a CD8 T-cell immunoevasin was predicted from some alleviation of immune evasion for certain epitopes and MHC-I molecules in cells infected with the deletion mutant mCMV-Δm04 (34, 42, 89), but gp34/m04 does not reduce the steady-state level of cell surface class I molecules and does not inhibit peptide presentation when expressed selectively after infection with mCMV-Δm06m152 (34, 62). The m04-MHC-I complexes are expressed on the cell surface (46) and appear to be involved in the modulation of natural killer cell activity (45).Here we give the first report on quantitating the efficacy of immunoevasins in terms of absolute numbers of pMHC complexes displayed at the cell surface. By comparing the fate of pMHC complexes already present at the cell surface in advance of immunoevasin gene expression with that of newly formed pMHC complexes, our data provide direct evidence to conclude that downmodulation of cell surface MHC-I molecules is secondary to an interruption of the flow of newly formed pMHC complexes to the cell surface.(Part of this work was presented at the 12th International CMV/Betaherpesvirus Workshop, 10 to 14 May 2009, Boston, MA.)     

Environmental Factors Shape Sediment Anammox Bacterial Communities in Hypernutrified Jiaozhou Bay,China

Bacterial anaerobic ammonium oxidation (anammox) is an important process in the marine nitrogen cycle. Because ongoing eutrophication of coastal bays contributes significantly to the formation of low-oxygen zones, monitoring of the anammox bacterial community offers a unique opportunity for assessment of anthropogenic perturbations in these environments. The current study used targeting of 16S rRNA and hzo genes to characterize the composition and structure of the anammox bacterial community in the sediments of the eutrophic Jiaozhou Bay, thereby unraveling their diversity, abundance, and distribution. Abundance and distribution of hzo genes revealed a greater taxonomic diversity in Jiaozhou Bay, including several novel clades of anammox bacteria. In contrast, the targeting of 16S rRNA genes verified the presence of only “Candidatus Scalindua,” albeit with a high microdiversity. The genus “Ca. Scalindua” comprised the apparent majority of active sediment anammox bacteria. Multivariate statistical analyses indicated a heterogeneous distribution of the anammox bacterial assemblages in Jiaozhou Bay. Of all environmental parameters investigated, sediment organic C/organic N (OrgC/OrgN), nitrite concentration, and sediment median grain size were found to impact the composition, structure, and distribution of the sediment anammox bacterial community. Analysis of Pearson correlations between environmental factors and abundance of 16S rRNA and hzo genes as determined by fluorescent real-time PCR suggests that the local nitrite concentration is the key regulator of the abundance of anammox bacteria in Jiaozhou Bay sediments.Anaerobic ammonium oxidation (anammox, NH₄⁺ + NO₂⁻ → N₂ + 2H₂O) was proposed as a missing N transformation pathway decades ago. It was found 20 years later to be mediated by bacteria in artificial environments, such as anaerobic wastewater processing systems (see reference 32 and references therein). Anammox in natural environments was found even more recently, mainly in O₂-limited environments such as marine sediments (28, 51, 54, 67, 69) and hypoxic or anoxic waters (10, 25, 39-42). Because anammox may remove as much as 30 to 70% of fixed N from the oceans (3, 9, 64), this process is potentially as important as denitrification for N loss and bioremediation (41, 42, 73). These findings have significantly changed our understanding of the budget of the marine and global N cycles as well as involved pathways and their evolution (24, 32, 35, 72). Studies indicate variable anammox contributions to local or regional N loss (41, 42, 73), probably due to distinct environmental conditions that may influence the composition, abundance, and distribution of the anammox bacteria. However, the interactions of anammox bacteria with their environment are still poorly understood.The chemolithoautotrophic anammox bacteria (64, 66) comprise the new Brocadiaceae family in the Planctomycetales, for which five Candidatus genera have been described (see references 32 and 37 and references therein): “Candidatus Kuenenia,” “Candidatus Brocadia,” “Candidatus Scalindua,” “Candidatus Anammoxoglobus,” and “Candidatus Jettenia.” Due to the difficulty of cultivation and isolation, anammox bacteria are not yet in pure culture. Molecular detection by using DNA probes or PCR primers targeting the anammox bacterial 16S rRNA genes has thus been the main approach for the detection of anammox bacteria and community analyses (58). However, these studies revealed unexpected target sequence diversity and led to the realization that due to biased coverage and specificity of most of the PCR primers (2, 8), the in situ diversity of anammox bacteria was likely missed. Thus, the use of additional marker genes for phylogenetic analysis was suggested in hopes of better capturing the diversity of this environmentally important group of bacteria. By analogy to molecular ecological studies of aerobic ammonia oxidizers, most recent studies have attempted to include anammox bacterium-specific functional genes. All anammox bacteria employ hydrazine oxidoreductase (HZO) (= [Hzo]₃) to oxidize hydrazine to N₂ as the main source for a useable reductant, which enables them to generate proton-motive force for energy production (32, 36, 65). Phylogenetic analyses of Hzo protein sequences revealed three sequence clusters, of which the cladistic structure of cluster 1 is in agreement with the anammox bacterial 16S rRNA gene phylogeny (57). The hzo genes have emerged as an alternative phylogenetic and functional marker for characterization of anammox bacterial communities (43, 44, 57), allowing the 16S rRNA gene-based investigation methods to be corroborated and improved.The contribution of anammox to the removal of fixed N is highly variable in estuarine and coastal sediments (50). For instance, anammox may be an important pathway for the removal of excess N (23) or nearly negligible (48, 54, 67, 68). This difference may be attributable to a difference in the structure and composition of anammox bacterial communities, in particular how the abundance of individual cohorts depends on particular environmental conditions. Anthropogenic disturbance with variable source and intensity of eutrophication and pollution may further complicate the anammox bacterium-environment relationship.Jiaozhou Bay is a large semienclosed water body of the temperate Yellow Sea in China. Eutrophication has become its most serious environmental problem, along with red tides (harmful algal blooms), species loss, and contamination with toxic chemicals and harmful microbes (14, 15, 21, 61, 71). Due to different sources of pollution and various levels of eutrophication across Jiaozhou Bay (mariculture, municipal and industrial wastewater, crude oil shipyard, etc.), a wide spectrum of environmental conditions may contribute to a widely varying community structure of anammox bacteria. This study used both 16S rRNA and hzo genes as targets to measure their abundance, diversity, and spatial distribution and assess the response of the resident anammox bacterial community to different environmental conditions. Environmental factors with potential for regulating the sediment anammox microbiota are discussed.     

Cultivation of Autotrophic Ammonia-Oxidizing Archaea from Marine Sediments in Coculture with Sulfur-Oxidizing Bacteria

The role of ammonia-oxidizing archaea (AOA) in nitrogen cycling in marine sediments remains poorly characterized. In this study, we enriched and characterized AOA from marine sediments. Group I.1a crenarchaea closely related to those identified in marine sediments and “Candidatus Nitrosopumilus maritimus” (99.1 and 94.9% 16S rRNA and amoA gene sequence identities to the latter, respectively) were substantially enriched by coculture with sulfur-oxidizing bacteria (SOB). The selective enrichment of AOA over ammonia-oxidizing bacteria (AOB) is likely due to the reduced oxygen levels caused by the rapid initial growth of SOB. After biweekly transfers for ca. 20 months, archaeal cells became the dominant prokaryotes (>80%), based on quantitative PCR and fluorescence in situ hybridization analysis. The increase of archaeal 16S rRNA gene copy numbers was coincident with the amount of ammonia oxidized, and expression of the archaeal amoA gene was observed during ammonia oxidation. Bacterial amoA genes were not detected in the enrichment culture. The affinities of these AOA to oxygen and ammonia were substantially higher than those of AOB. [¹³C]bicarbonate incorporation and the presence and activation of genes of the 3-hydroxypropionate/4-hydroxybutyrate cycle indicated autotrophy during ammonia oxidation. In the enrichment culture, ammonium was oxidized to nitrite by the AOA and subsequently to nitrate by Nitrospina-like bacteria. Our experiments suggest that AOA may be important nitrifiers in low-oxygen environments, such as oxygen-minimum zones and marine sediments.Archaea have long been known as extremophiles, since most cultivated archaeal strains were cultivated from extreme environments, such as acidic, hot, and high-salt environments. The view of archaea as extremophiles (i.e., acidophiles, thermophiles, and halophiles) has radically changed by the application of molecular technologies, including PCR in environmental microbiology. Using Archaea-specific PCR primers, novel archaeal 16S rRNA gene sequences were discovered in seawater (23, 27). Following these discoveries, an ever-increasing and unexpectedly high variety of archaeal 16S rRNA gene sequences has been reported from diverse “nonextreme” environments (67). This indicates that archaea are, like bacteria, ubiquitous in the biosphere rather than exclusively inhabiting specific extreme niches. Archaea are abundant in water columns of some oceanic provinces (33, 36) and deep-subsea floor sediments (11, 12, 48). Despite the increasing number of reports of the diversity and abundance of these nonextreme archaea by molecular ecological studies, their physiology and ecological roles have remained enigmatic.Oxidation of ammonia, a trait long thought to be exclusive to the domain Bacteria (13), was recently suggested to be a trait of archaea of the crenarchaeal groups I.1a and I.1b, based on a metagenome analysis (79) and supported by the discovery of archaeal amoA-like genes in environmental shotgun sequencing studies of Sargasso Sea water (80) and genomic analysis of “Candidatus Cenarchaeum symbiosum,” a symbiont of a marine sponge (30). Molecular ecological studies indicated that these ammonia-oxidizing archaea (AOA) are often predominant over ammonia-oxidizing bacteria (AOB) in ocean waters (9, 53, 87), soils (17, 47), and marine sediments (61). Critical evidence for autotrophic archaeal ammonia oxidation was obtained by the characterization of the first cultivated mesophilic crenarchaeon (group I.1a), “Candidatus Nitrosopumilus maritimus SCM1,” from an aquarium (38), and a related archaeon from North Sea water (87) and subsequently by enrichment of thermophilic AOA (22, 31). Whole-genome-based phylogenetic studies recently indicated that the nonthermophilic crenarchaea, including the AOA, likely form a phylum separate from the Crenarchaeota and Euryarchaeota phyla (15, 16, 72). This proposed new phylum was called Thaumarchaeota (15).Microorganisms in marine sediments contribute significantly to global biogeochemical cycles because of their abundance (85). Nitrification is essential to the nitrogen cycle in marine sediments and may be metabolically coupled with denitrification and anaerobic ammonium oxidation, resulting in the removal of nitrogen as molecular nitrogen and the generation of greenhouse gases, such as nitrous oxide (19, 75). Compared with studies on archaeal nitrification in the marine water column, only limited information on archaeal nitrification in marine sediments is available so far. Archaeal amoA genes have been retrieved from marine and coastal sediments (8, 26, 61), and the potentially important role of AOA in nitrification has been suggested based on the abundance of archaeal amoA genes relative to that of bacterial amoA genes in surface marine sediments from Donghae (South Korea) (61). Cultivation of AOA, although difficult (38), remains essential to estimating the metabolic potential of archaea in environments such as soils (47) and marine sediments (61). Here, we report the successful enrichment of AOA of crenarchaeal group I.1a from marine sediments by employing a coculture with sulfur-oxidizing bacteria (SOB) which was maintained for ca. 20 months with biweekly transfers. In this way, we were able to characterize AOA from marine sediments, providing a clue for the role of AOA in the nitrogen cycle of marine sediments.     

The Genome of the Amoeba Symbiont “Candidatus Amoebophilus asiaticus” Reveals Common Mechanisms for Host Cell Interaction among Amoeba-Associated Bacteria

Protozoa play host for many intracellular bacteria and are important for the adaptation of pathogenic bacteria to eukaryotic cells. We analyzed the genome sequence of “Candidatus Amoebophilus asiaticus,” an obligate intracellular amoeba symbiont belonging to the Bacteroidetes. The genome has a size of 1.89 Mbp, encodes 1,557 proteins, and shows massive proliferation of IS elements (24% of all genes), although the genome seems to be evolutionarily relatively stable. The genome does not encode pathways for de novo biosynthesis of cofactors, nucleotides, and almost all amino acids. “Ca. Amoebophilus asiaticus” encodes a variety of proteins with predicted importance for host cell interaction; in particular, an arsenal of proteins with eukaryotic domains, including ankyrin-, TPR/SEL1-, and leucine-rich repeats, which is hitherto unmatched among prokaryotes, is remarkable. Unexpectedly, 26 proteins that can interfere with the host ubiquitin system were identified in the genome. These proteins include F- and U-box domain proteins and two ubiquitin-specific proteases of the CA clan C19 family, representing the first prokaryotic members of this protein family. Consequently, interference with the host ubiquitin system is an important host cell interaction mechanism of “Ca. Amoebophilus asiaticus”. More generally, we show that the eukaryotic domains identified in “Ca. Amoebophilus asiaticus” are also significantly enriched in the genomes of other amoeba-associated bacteria (including chlamydiae, Legionella pneumophila, Rickettsia bellii, Francisella tularensis, and Mycobacterium avium). This indicates that phylogenetically and ecologically diverse bacteria which thrive inside amoebae exploit common mechanisms for interaction with their hosts, and it provides further evidence for the role of amoebae as training grounds for bacterial pathogens of humans.Free-living amoebae, such as Acanthamoeba spp., are ubiquitous protozoa which can be found in such diverse habitats as soil, marine water, and freshwater and in many engineered environments (62, 100). They are important predators of prokaryotic and eukaryotic microorganisms, thereby having great influence on microbial community composition, soil mineralization, plant growth, and nutrient cycles (14, 100). Interestingly, many well-known pathogens of humans are able to infect, survive, and multiply within amoebae (39, 51). These protozoa can thus serve as reservoirs and vectors for the transmission of pathogenic bacteria to humans, as demonstrated for L. pneumophila and Mycobacterium avium (2, 115). It is also increasingly being recognized that protozoa are important for the adaptation of (pathogenic) bacteria to higher eukaryotic cells as a niche for growth (2, 24, 42, 78, 89).In addition to the many recognized transient associations between amoeba and pathogens, stable and obligate relationships between bacteria and amoebae also were described for members of the Alphaproteobacteria (11, 34, 48), the Betaproteobacteria (49), the Bacteroidetes (50), and the Chlamydiae (4, 12, 35, 52). These obligate amoeba symbionts show a worldwide distribution, since phylogenetically highly similar strains were found in amoeba isolates from geographically distant sources (51, 107). The phylogenetic diversity and the different lifestyles of these obligate intracellular bacteria—some are located directly in the host cell cytoplasm (11, 34, 48-50, 52), while others are enclosed in host-derived vacuoles (4, 35, 44)—suggest fundamentally different mechanisms of host cell interaction. However, with the exception of chlamydia-related amoeba symbionts (37, 46, 47), our knowledge of the biology of obligate intracellular symbionts of amoebae is still scarce.Comparative genomics has been extremely helpful for the analysis of intracellular bacteria. Numerous genome sequences from the Alpha- and Gammaproteobacteria and the Chlamydiae are available and have contributed significantly to our understanding of genome evolution, the biology of intracellular bacteria, and the interactions with their host cells (24, 26, 46, 79, 82). In this study, we determined and analyzed the complete genome sequence of “Candidatus Amoebophilus asiaticus” strain 5a2 in order to gain novel insights into its biology. “Ca. Amoebophilus asiaticus” is a Gram-negative, obligate intracellular amoeba symbiont belonging to the Bacteroidetes which has been discovered within an amoeba isolated from lake sediment (107). “Ca. Amoebophilus asiaticus” shows highest 16S rRNA similarity to “Candidatus Cardinium hertigii,” an obligate intracellular parasite of arthropods able to manipulate the reproduction of its hosts (131). According to 16S rRNA trees, both organisms are members of a monophyletic group within the phylogenetically diverse phylum Bacteroidetes, consisting only of symbionts and sequences which were directly retrieved from corals (113). Among members of the Bacteroidetes, the genome sequences of only three symbionts, which are only distantly related (75 to 80% 16S rRNA sequence similarity) to “Ca. Amoebophilus asiaticus,” have been determined to date: two strains of “Candidatus Sulcia muelleri,” a symbiont of sharpshooters, and “Azobacteroides pseudotrichonymphae,” a symbiont of an anaerobic termite gut ciliate (45, 72, 74, 127).The genome of “Ca. Amoebophilus asiaticus” is only moderately reduced in size compared to those of many other obligate intracellular bacteria (75, 123), but nevertheless, its biosynthetic capabilities are extremely limited. A large fraction of the genome consists of IS elements and an unparalleled high number of proteins with eukaryotic domains, such as ankyrin repeats, TPR/SEL1 repeats, leucine-rich repeats, and domains from the eukaryotic ubiquitin system, all of them most likely important for host cell interaction. Feature enrichment analysis across a nonredundant data set of all bacterial genomes showed that these domains are enriched in the genomes of bacteria (including several pathogens of humans) known to be able to infect amoebae, providing further evidence for an important role of amoebae in the evolution of mechanisms for host cell interaction in intracellular bacteria.     

Lipid Phosphate Phosphatase 3 Stabilization of β-Catenin Induces Endothelial Cell Migration and Formation of Branching Point Structures

Endothelial cell (EC) migration, cell-cell adhesion, and the formation of branching point structures are considered hallmarks of angiogenesis; however, the underlying mechanisms of these processes are not well understood. Lipid phosphate phosphatase 3 (LPP3) is a recently described p120-catenin-associated integrin ligand localized in adherens junctions (AJs) of ECs. Here, we tested the hypothesis that LPP3 stimulates β-catenin/lymphoid enhancer binding factor 1 (β-catenin/LEF-1) to induce EC migration and formation of branching point structures. In subconfluent ECs, LPP3 induced expression of fibronectin via β-catenin/LEF-1 signaling in a phosphatase and tensin homologue (PTEN)-dependent manner. In confluent ECs, depletion of p120-catenin restored LPP3-mediated β-catenin/LEF-1 signaling. Depletion of LPP3 resulted in destabilization of β-catenin, which in turn reduced fibronectin synthesis and deposition, which resulted in inhibition of EC migration. Accordingly, reexpression of β-catenin but not p120-catenin in LPP3-depleted ECs restored de novo synthesis of fibronectin, which mediated EC migration and formation of branching point structures. In confluent ECs, however, a fraction of p120-catenin associated and colocalized with LPP3 at the plasma membrane, via the C-terminal cytoplasmic domain, thereby limiting the ability of LPP3 to stimulate β-catenin/LEF-1 signaling. Thus, our study identified a key role for LPP3 in orchestrating PTEN-mediated β-catenin/LEF-1 signaling in EC migration, cell-cell adhesion, and formation of branching point structures.Angiogenesis, the formation of new blood vessels, involves several well-coordinated cellular processes, including endothelial cell (EC) migration, synthesis and deposition of extracellular matrix proteins, such as fibronectin, cell-cell adhesion, and formation of branching point structures (1-3, 19, 33); however, less is known about the underlying mechanisms of these processes (6, 8, 12, 14, 16, 17). For example, adherens junctions (AJs), which mediate cell-cell adhesion between ECs, may be involved in limiting the extent of cell migration (2, 14, 38, 40). VE-cadherin, a protein found in AJs, is a single-pass transmembrane polypeptide responsible for calcium-dependent homophilic interactions through its extracellular domains (2, 38, 40). The VE-cadherin cytoplasmic domain interacts with the Armadillo domain-containing proteins, β-catenin, γ-catenin (plakoglobin), and p120-catenin (p120ctn) (2, 15, 38, 40, 43). Genetic and biochemical evidence documents a crucial role of β-catenin in regulating cell adhesion as well as proliferation secondary to the central position of β-catenin in the Wnt signaling pathway (13, 16, 25, 31, 44). In addition, the juxtamembrane protein p120ctn regulates AJ stability via binding to VE-cadherin (2, 7, 9, 15, 21, 28, 32, 43). The absence of regulation or inappropriate regulation of β-catenin and VE-cadherin functions is linked to cardiovascular disease and tumor progression (2, 6).We previously identified lipid phosphate phosphatase 3 (LPP3), also known as phosphatidic acid phosphatase 2b (PAP2b), in a functional assay of angiogenesis (18, 19, 41, 42). LPP3 not only exhibits lipid phosphatase activity but also functions as a cell-associated integrin ligand (18, 19, 35, 41, 42). The known LPPs (LPP1, LPP2, and LPP3) (20-23) are six transmembrane domain-containing plasma membrane-bound enzymes that dephosphorylate sphingosine-1-phosphate (S1P) and its structural homologues, and thus, these phosphatases generate lipid mediators (4, 5, 23, 35, 39). All LPPs, which contain a single N-glycosylation site and a putative lipid phosphatase motif, are situated such that their N and C termini are within the cell (4, 5, 22, 23, 35, 39). Only the LPP3 isoform contains an Arg-Gly-Asp (RGD) sequence in the second extracellular loop, and this RGD sequence enables LPP3 to bind integrins (18, 19, 22). Transfection experiments with green fluorescent protein (GFP)-tagged LPP1 and LPP3 showed that LPP1 is apically sorted, whereas LPP3 colocalized with E-cadherin at cell-cell contact sites with other Madin-Darby canine kidney (MDCK) cells (22). Mutagenesis and domain swapping experiments established that LPP1 contains an apical targeting signal sequence (FDKTRL) in its N-terminal segment. In contrast, LPP3 contains a dityrosine (109Y/110Y) basolateral sorting motif (22). Interestingly, conventional deletion of Lpp3 is embryonic lethal, since the Lpp3 gene plays a critical role in extraembryonic vasculogenesis independent of its lipid phosphatase activity (11). In addition, an LPP3-neutralizing antibody was shown to prevent cell-cell interactions (19, 42) and angiogenesis (42). Here, we addressed the hypothesis that LPP3 plays a key role in EC migration, cell-cell adhesion, and formation of branching point structures by stimulating β-catenin/lymphoid enhancer binding factor 1 (β-catenin/LEF-1) signaling.     

The Silencing Domain of GW182 Interacts with PABPC1 To Promote Translational Repression and Degradation of MicroRNA Targets and Is Required for Target Release

GW182 family proteins are essential in animal cells for microRNA (miRNA)-mediated gene silencing, yet the molecular mechanism that allows GW182 to promote translational repression and mRNA decay remains largely unknown. Previous studies showed that while the GW182 N-terminal domain interacts with Argonaute proteins, translational repression and degradation of miRNA targets are promoted by a bipartite silencing domain comprising the GW182 middle and C-terminal regions. Here we show that the GW182 C-terminal region is required for GW182 to release silenced mRNPs; moreover, GW182 dissociates from miRNA targets at a step of silencing downstream of deadenylation, indicating that GW182 is required to initiate but not to maintain silencing. In addition, we show that the GW182 bipartite silencing domain competes with eukaryotic initiation factor 4G for binding to PABPC1. The GW182-PABPC1 interaction is also required for miRNA target degradation; accordingly, we observed that PABPC1 associates with components of the CCR4-NOT deadenylase complex. Finally, we show that PABPC1 overexpression suppresses the silencing of miRNA targets. We propose a model in which the GW182 silencing domain promotes translational repression, at least in part, by interfering with mRNA circularization and also recruits the deadenylase complex through the interaction with PABPC1.In multicellular eukaryotes, the regulation of gene expression by microRNAs (miRNAs) is critical for biological processes as diverse as cell differentiation and proliferation, apoptosis, metabolism, and development (4). To exert a regulatory function, miRNAs associate with Argonaute proteins to form RNA-induced silencing complexes, which repress translation and trigger the degradation of target mRNAs (4, 10, 16). The extent to which translational repression and degradation contribute to silencing depends on the specific target-miRNA combination; some targets are regulated predominantly at the translational level, whereas others can be regulated mainly at the mRNA level (3). A large-scale proteomic analysis performed in parallel with measurements of mRNA levels showed that for the vast majority of miRNA targets, silencing correlates with changes at both the protein and mRNA levels (1, 27).In animal cells, the degradation of miRNA targets is initiated by deadenylation and decapping, which are followed by the exonucleolytic decay of the mRNA body (2, 3, 9, 11, 12, 17, 19, 24, 30, 31). miRNA-dependent mRNA degradation requires a variety of proteins: an Argonaute and a GW182 protein, the CCR4-NOT deadenylase complex, the decapping enzyme DCP2, and several decapping activators including DCP1, Ge-1, HPat, EDC3, and Me31B (also known as RCK/p54) (3, 6, 9, 12, 19). Several studies previously demonstrated that miRNAs trigger deadenylation and decapping even when the mRNA target is not translated (9, 12, 19, 24, 30, 31), indicating that mRNA decay is not merely a consequence of a primary effect of miRNAs on translation but rather is an independent mechanism by which miRNAs silence gene expression.Although how miRNAs trigger mRNA degradation is well established, the mechanisms driving the inhibition of translation are unclear. Multiple mechanisms have been proposed: the displacement of eukaryotic initiation factor 4E (eIF4E) from the mRNA cap structure, interference with the function of the eIF4F complex, a block of 60S ribosomal subunit joining, or an inhibition of translation elongation (4, 10, 16). Regardless of the precise mechanism, the translational repression of miRNA targets also requires GW182 family proteins (11, 13).GW182 proteins are essential components of the miRNA pathway in animal cells, as their depletion suppresses miRNA-mediated gene silencing (reviewed in references 8 and 13). Recent studies have revealed that the silencing activity of these proteins resides predominantly in a bipartite silencing domain containing the middle and C-terminal regions (14, 22, 33). The precise molecular function of the GW182 silencing domain is not fully understood, yet it is known that the domain is not required for GW182 proteins to interact with Argonaute proteins or to localize to P bodies (3, 14, 22). Furthermore, when the silencing domains of GW182 proteins are artificially tethered to mRNAs, their expression is silenced; therefore, tethering bypasses the requirement for Argonaute proteins and miRNAs (5, 22, 33). These observations suggest that the silencing domains of GW182 proteins exhibit intrinsic silencing activity and therefore likely play a role at the effector step of silencing (13, 14, 22, 33).Here we investigate what role the Drosophila melanogaster GW182 silencing domain plays in the miRNA pathway. Overall, our results reveal that the very C-terminal region of this domain is required for the release of GW182 from silenced mRNPs. Indeed, we unexpectedly found that we could detect D. melanogaster GW182 bound to miRNA targets only in cells depleted of components of the deadenylase complex. These results suggest that GW182 dissociates from Argonaute-1 (AGO1) and miRNA targets at a step of silencing downstream of deadenylation. In contrast, GW182 mutants lacking the C-terminal region remain stably bound to miRNA targets, even in wild-type cells, indicating that this region plays a role in the dissociation of GW182 from effector complexes. We further show that the bipartite silencing domain of GW182 interacts with PABPC1 and interferes with the binding of PABPC1 to eIF4G. The interaction of GW182 with PABPC1 is also required for the degradation of miRNA targets, most likely because the interaction facilitates the recruitment of the CCR4-NOT deadenylase complex. Accordingly, overexpressing PABPC1 suppresses the silencing of miRNA targets. Our findings uncover an unexpected role for PABPC1 in the miRNA pathway.