Occurrence and Molecular Characteristics of Methicillin-Resistant Staphylococcus aureus and Methicillin-Resistant Staphylococcus pseudintermedius in an Academic Veterinary Hospital

Recently, methicillin-resistant Staphylococcus aureus (MRSA) and methicillin-resistant Staphylococcus pseudintermedius (MRSP) have been increasingly isolated from veterinarians and companion animals. With a view to preventing the spread of MRSA and MRSP, we evaluated the occurrence and molecular characteristics of each in a veterinary college. MRSA and MRSP were isolated from nasal samples from veterinarians, staff members, and veterinary students affiliated with a veterinary hospital. Using stepwise logistic regression, we identified two factors associated with MRSA carriage: (i) contact with an identified animal MRSA case (odds ratio [OR], 6.9; 95% confidence interval [95% CI], 2.2 to 21.6) and (ii) being an employee (OR, 6.2; 95% CI, 2.0 to 19.4). The majority of MRSA isolates obtained from individuals affiliated with the veterinary hospital and dog patients harbored spa type t002 and a type II staphylococcal cassette chromosome mec (SCCmec), similar to the hospital-acquired MRSA isolates in Japan. MRSA isolates harboring spa type t008 and a type IV SCCmec were obtained from one veterinarian on three different sampling occasions and also from dog patients. MRSA carriers can also be a source of MRSA infection in animals. The majority of MRSP isolates (85.2%) carried hybrid SCCmec type II-III, and almost all the remaining MRSP isolates (11.1%) carried SCCmec type V. MRSA and MRSP were also isolated from environmental samples collected from the veterinary hospital (5.1% and 6.4%, respectively). The application of certain disinfection procedures is important for the prevention of nosocomial infection, and MRSA and MRSP infection control strategies should be adopted in veterinary medical practice.Methicillin-resistant Staphylococcus aureus (MRSA) is an important cause of nosocomial infections in human hospitals. The prevalence of hospital-acquired MRSA (HA-MRSA) infection among inpatients in intensive care units (ICUs) continues to increase steadily in Japan. Recently, cases of community-acquired MRSA (CA-MRSA) have been documented in persons without an established risk factor for HA-MRSA infection (14, 32, 36, 49).There has also been an increase in the number of reports of the isolation of MRSA from veterinarians and companion animals (5, 21, 23-26, 28, 31, 34, 38, 44, 50, 51, 53). Values reported for the prevalence of MRSA among veterinary staff include 17.9% in the United Kingdom (21), 10% in Japan (38), 3.9% in Scotland (13), and 3.0% in Denmark (28). Loeffler et al. reported that the prevalence of MRSA among dog patients and healthy dogs owned by veterinary staff members was 8.9% (21). In Japan, an MRSA isolate was detected in only one inpatient dog (3.8%) and could not be detected in any of 31 outpatient dogs (38). In the United States, MRSA isolates were detected in both dog (0.1%) and cat (0.1%) patients (31). The prevalence of MRSA among healthy dogs has been reported to be 0.7% (5). Hanselman et al. suggested that MRSA colonization may be an occupational risk for large-animal veterinarians (12). Recently, Burstiner et al. reported that the frequency of MRSA colonization among companion-animal veterinary personnel was equal to the frequency among large-animal veterinary personnel (6).In addition, other methicillin-resistant coagulase-positive staphylococci (MRCPS), such as methicillin-resistant Staphylococcus pseudintermedius (MRSP) and methicillin-resistant Staphylococcus schleiferi (MRSS), isolated from dogs, cats, and a veterinarian have been reported (11, 31, 38, 40, 52). MRSP isolates have also been detected among inpatient dogs (46.2%) and outpatient dogs (19.4%) in a Japanese veterinary teaching hospital (38). In Canada, however, MRSP and MRSS isolates were detected in only 2.1% and 0.5% of dog patients, respectively (11).Methicillin-resistant staphylococci produce penicillin-binding protein 2′, which reduces their affinity for β-lactam antibiotics. This protein is encoded by the mecA gene (48), which is carried on the staphylococcal cassette chromosome mec (SCCmec). SCCmec is a mobile genetic element characterized by the combination of the mec and ccr complexes (16), and it is classified into subtypes according to differences in the junkyard regions (43). SCCmec typing can be used as a molecular tool (22, 27, 30, 33, 36, 55) for examining the molecular epidemiology of methicillin-resistant staphylococci.In this study, we investigated the occurrence and characteristics of MRCPS isolates in a veterinary hospital in order to establish the transmission route of MRCPS in a veterinary hospital and with a view to preventing the spread of MRCPS infection. In addition, we evaluated the factors associated with MRCPS. Further, as Heller et al. have reported the distribution of MRSA within veterinary hospital environments and suggested the necessity to review cleaning protocols of hospital environments (13), we also attempted to isolate MRCPS from environmental samples collected in a veterinary hospital for an evaluation of MRSA transmission cycle though environmental surfaces in the veterinary hospital.     

Generation of Electricity and Analysis of Microbial Communities in Wheat Straw Biomass-Powered Microbial Fuel Cells

Electricity generation from wheat straw hydrolysate and the microbial ecology of electricity-producing microbial communities developed in two-chamber microbial fuel cells (MFCs) were investigated. The power density reached 123 mW/m² with an initial hydrolysate concentration of 1,000 mg chemical oxygen demand (COD)/liter, while coulombic efficiencies ranged from 37.1 to 15.5%, corresponding to the initial hydrolysate concentrations of 250 to 2,000 mg COD/liter. The suspended bacteria found were different from the bacteria immobilized in the biofilm, and they played different roles in electricity generation from the hydrolysate. The bacteria in the biofilm were consortia with sequences similar to those of Bacteroidetes (40% of sequences), Alphaproteobacteria (20%), Bacillus (20%), Deltaproteobacteria (10%), and Gammaproteobacteria (10%), while the suspended consortia were predominately Bacillus (22.2%). The results of this study can contribute to improving understanding of and optimizing electricity generation in microbial fuel cells.Wheat straw is one of the most abundant renewable resources. According to the Food and Agriculture Organization of the United Nations, approximately 1.9 × 10⁹ tons of wheat straw annually are produced worldwide, accompanied by 6.2 × 10⁸ tons of wheat production. Wheat straw is composed of 35 to 45% cellulose and 20 to 30% hemicelluloses with a relatively low lignin content (<20%) (42). The hemicellulose fraction of the straw is easily hydrolyzed to its constituent sugars by a hydrothermal treatment process, forming a carbohydrate-enriched liquid hydrolysate (46). Chemical and biological approaches to sustainable energy production from the liquefied hydrolysates to energy carriers, such as methane, ethanol, and H₂, have been developed. However, many of these approaches encounter technical and economical hurdles (10, 12, 15, 16). An alternative strategy is direct conversion of wheat straw biomass to electrical energy in microbial fuel cells (MFCs).MFCs are bioelectrochemical reactors in which microorganisms mediate the direct conversion of chemical energy stored in organic matter or bulk biomass into electrical energy (12, 15, 16, 40). Various substrates, such as simple carbohydrates, low-molecular-weight organic acids, starch, amino acids, chitin, cellulose, domestic wastewater, food-processing wastewater, recycled paper wastewater, and marine sediment organic matter, have been successfully utilized for power generation in MFCs (16-18, 27, 30, 33). To understand the microbial constraints on various fuel-powered MFCs, microbial communities have been characterized by several groups. Microbial communities from various systems are very different and often diverse, ranging from well-known metal- and anode-reducing bacteria to unknown exoelectrogens (1, 20, 21). It has been found that parameters such as the substrates used as fuels and the inocula used for starting up the MFCs can influence the anode bacterial communities in an MFC, which subsequently influence the efficiency of the MFCs (3, 14, 22, 38, 44). Different pure substrates, such as acetate, glucose, and lactate, were used as fuel to compare the microbial communities that developed in the MFCs. Regardless of the different substrates, all anode communities contained sequences closely affiliated with Geobacter sulfurreducens (>99% similarity) and an uncultured bacterium clone belonging to the family Bacteroidaceae (99% similarity). Firmicutes were only found in glucose-fed MFCs (20). Microbial-community analyses of MFCs powered with complex substrates have also been performed by several researchers, and their results were very diverse. The microbial community in starch wastewater-powered MFC was dominated by unidentified bacteria (35.9%), followed by Betaproteobacteria (25.0%), Alphaproteobacteria (20.1%), and the Cytophaga/Flexibacter/Bacteroides group (19.0%) (21). The anode-attached consortia in a cellulose-powered MFC were related to Clostridium spp., while Comamonas spp. were abundant in the suspended consortia (13). Although many studies have reported the microbial compositions of MFCs, it is still unclear which microbial communities develop as a function of the external parameters.Wheat straw biomass constitutes a large source for bioenergy production and shows promising prospects for electricity generation in MFCs. Therefore, wheat straw biomass was used to study the microbial communities that develop during the operation of an MFC in order to better understand the microbial electrochemical roles and potentially improve MFC performance.The objectives of this study were to (i) test wheat straw hydrolysate as a potential fuel in an MFC for electricity generation and (ii) study the microbial composition and evolution of electricity-producing communities in a two-chamber MFC system. Phylogenetic-diversity analysis of the enriched consortia was conducted to verify the presence of hydrolytic and respiratory anaerobes that could couple hydrolysate oxidation with proton reduction in the anode chamber. This is the first report of exploiting microbial communities for direct conversion of wheat straw hydrolysate to electrical energy in an MFC.     

Quantitative Approach to Determining the Contribution of Viable-but-Nonculturable Subpopulations to Malolactic Fermentation Processes

Different sizes of viable-but-nonculturable cell subpopulations of a lactic acid bacterium strain were induced by adding increasing amounts of SO₂. The experimental data obtained here were fitted to a segregated kinetic model developed previously. This procedure allowed us to determine in quantitative terms the contribution of this physiological state to malolactic fermentation.The persistence of stressed, damaged, or viable-but-nonculturable (VBNC) cells during microbial fermentation underlines the requirement of alternative methods for detecting and characterizing these emergent states not otherwise detectable by traditional culture-based methods (13). Flow cytometry (FC) has evolved as an outstanding tool in bioprocesses due to its usefulness in cell physiology monitoring (5, 12). The persistence of nonculturable cells during microbial fermentation has been attributed to changes in water activity, acidity, redox potential, nutrient availability, and starvation (14, 17, 18, 24, 25) or to the use of preserved starter cultures (20). Additionally, the quantification of catalytic activity is critical to bioprocess optimization, as it measures the individual contributions of different cell subpopulations to the global process (2, 13). Despite the loss of culturability under standard conditions, it is strongly suspected that VBNC cells remain alive, maintain the transport system and biosynthesis, and are able to metabolize substrates (16, 26). Gene expression has also been demonstrated previously (9, 23). However, although the physiology, biochemistry, and genetics of the VBNC state have been studied over the years, its functionality and biological implication are still issues under intense debate (1, 21, 22).In this work, cider malolactic fermentation (MLF) was selected as a model system to clarify the role played by VBNC cells in bioprocesses. MLF was carried out under different SO₂ concentrations (0, 30, and 60 ppm total) for inducing VBNC states. The fermentation medium was sterile apple must or “green” cider (obtained just after alcoholic fermentation and containing 5.6% [vol/vol] ethanol), obtained as previously described (11). Sodium bisulfite was used for SO₂ treatments. MLF was carried out in duplicate at 22°C statically in 250-ml bottles. An indigenous strain of Lactobacillus hilgardii was inoculated at an optical density at 600 nm of ∼0.1 to start MLF. Flasks were shaken just before sampling in order to homogenize the biomass content. Samples were taken aseptically at time intervals until malic acid was consumed (≤0.5 g liter⁻¹), and cells were collected and processed for further analysis as described previously (20). Supernatants were filtered (0.45 μm pore size) and frozen (−20°C) until chemical analysis. The amount of malic acid was determined by high-pressure liquid chromatography (Alliance 2690; Waters) with a photodiode array detector (Waters 996), as reported previously (19).     

Engineering of Clostridium phytofermentans Endoglucanase Cel5A for Improved Thermostability

A family 5 glycoside hydrolase from Clostridium phytofermentans was cloned and engineered through a cellulase cell surface display system in Escherichia coli. The presence of cell surface anchoring, a cellulose binding module, or a His tag greatly influenced the activities of wild-type and mutant enzymes on soluble and solid cellulosic substrates, suggesting the high complexity of cellulase engineering. The best mutant had 92%, 36%, and 46% longer half-lives at 60°C on carboxymethyl cellulose, regenerated amorphous cellulose, and Avicel, respectively.The production of biofuels from nonfood cellulosic biomass would benefit the economy, the environment, and national energy security (17, 32). The largest technological and economical obstacle is the release of soluble fermentable sugars at prices competitive with those from sugarcane or corn kernels (17, 31). One of the approaches is discovering new cellulases from cellulolytic microorganisms, followed by cellulase engineering for enhanced performance on pretreated solid substrates. However, cellulase engineering remains challenging because enzymatic cellulose hydrolysis is complicated, involving heterogeneous substrates (33, 37), different action mode cellulase components (18), synergy and/or competition among cellulase components (36, 37), and declining substrate reactivity over the course of conversion (11, 26). Directed enzyme evolution, independent of knowledge of the protein structure and the enzyme-substrate interactions (6, 34), has been conducted to generate endoglucanase mutants, such as enhanced activities on soluble substrates (14, 16, 22), prolonged thermostability (20), changed optimum pH (24, 28), or improved expression levels (21). Here, we cloned and characterized a family 5 glycoside hydrolase (Cel5A) from a cellulolytic bacterium, Clostridium phytofermentans ISDg (ATCC 700394) (29, 30), and engineered it for enhanced thermostability.     

Poly(3-Hydroxybutyrate) Production from Glycerol by Zobellella denitrificans MW1 via High-Cell-Density Fed-Batch Fermentation and Simplified Solvent Extraction

Industrial production of biodegradable polyesters such as polyhydroxyalkanoates is hampered by high production costs, among which the costs for substrates and for downstream processing represent the main obstacles. Inexpensive fermentable raw materials such as crude glycerol, an abundant by-product of the biodiesel industry, have emerged to be promising carbon sources for industrial fermentations. In this study, Zobellella denitrificans MW1, a recently isolated bacterium, was used for the production of poly(3-hydroxybutyrate) (PHB) from glycerol as the sole carbon source. Pilot-scale fermentations (42-liter scale) were conducted to scale up the high PHB accumulation capability of this strain. By fed-batch cultivation, at first a relatively high cell density (29.9 ± 1.3 g/liter) was obtained during only a short fermentation period (24 h). However, the PHB content was relatively low (31.0% ± 4.2% [wt/wt]). Afterwards, much higher concentrations of PHB (up to 54.3 ± 7.9 g/liter) and higher cell densities (up to 81.2 ± 2.5 g/liter) were obtained by further fed-batch optimization in the presence of 20 g/liter NaCl, with optimized feeding of glycerol and ammonia to support both cell growth and polymer accumulation over a period of 50 h. A high specific growth rate (0.422/h) and a short doubling time (1.64 h) were attained. The maximum PHB content obtained was 66.9% ± 7.6% of cell dry weight, and the maximum polymer productivity and substrate yield coefficient were 1.09 ± 0.16 g/liter/h and 0.25 ± 0.04 g PHB/g glycerol, respectively. Furthermore, a simple organic solvent extraction process was employed for PHB recovery during downstream processing: self-flotation of cell debris after extraction of PHB with chloroform allowed a convenient separation of a clear PHB-solvent solution from the cells. Maximum PHB recovery (85.0% ± 0.10% [wt/wt]) was reached after 72 h of extraction with chloroform at 30°C, with a polymer purity of 98.3% ± 1.3%.Polyhydroxybutyrate (PHB) is the best-studied example of biodegradable polyesters belonging to the group of polyhydroxyalkanoates (PHAs), which are synthesized by many bacteria and archaea as intracellular carbon and energy reserves (1, 40, 43). In the last decades, these biopolymers have received great attention due to their properties which resemble those of conventional petrochemical-based polymers (49). For instance, PHB is very similar to thermoplastic polypropylene (17). Their production from renewable resources and their complete biodegradability give PHAs promising advantages from an environmental point of view (6). In addition to their special physical traits, such as the elasticity of medium-chain-length PHAs and the high crystallization rate of PHB, PHAs are biocompatible, water resistant, oxygen impermeable, and enantiomerically pure; all of these characteristics broaden the scope of their applications in industry and medicine.So far, higher production costs than those of petrochemical plastics have hindered the successful commercialization of PHB (9). Many efforts have been devoted to reducing the production costs by developing superior microbial strains capable of utilizing cheap substrates and also by applying more efficient fermentation strategies and economical recovery processes (10).Fed-batch fermentation regimens are usually applied to achieve a high cell density, which is necessary for a high productivity and yield, in particular in cases of intracellular products, by frequent or continuous feeding of nutrients when growth proceeds (46). Several fed-batch fermentation processes have been reported for PHA production (21, 28). There are two prevalent cultivation modes for PHB production that are imposed on the microorganisms being used. The more frequently used mode is realized by a complex two-stage cultivation process. In this mode, all nutrients needed for growth to a high cell density are provided during the first phase of the process. In the second phase, imbalanced growth conditions are enforced by providing growth-limiting amounts of nutrients such as nitrogen, phosphate, or oxygen to trigger PHA biosynthesis and accumulation. The model organism for this mode is Ralstonia eutropha (formerly known as Alcaligenes eutrophus and recently reclassified as Cupriavidus necator) (26, 27). In the other cultivation mode, PHB is accumulated concurrently with growth, and therefore a single-stage process is applicable. A well-known example of this mode is PHB production by Alcaligenes latus (18, 47).Although several new downstream processes for the extraction of PHA have been reported as being economically effective, such as the application of surfactants and hypochlorite (9, 38), dispersions of hypochlorite solution and chloroform (14, 15), and the selective dissolution of cell mass by proteolytic enzymes (25) or by sulfuric acid and hypochlorite (48), solvent extraction methods are still regarded as an adequate way to gain intact polymers with a high purity and recovery yield (39). However, there is still a need to develop and improve these extraction methods further to make the entire process much simpler and cheaper (22).In addition to increased prices for crude oil, the abundance of inexpensive raw materials from agriculture and industry as cheap substrates for microbial fermentations, such as crude glycerol from the biodiesel industry, could make the production of PHA from renewable resources more competitive with common plastics (32). Due to increased glycerol production by the growing biodiesel industry, the prices for glycerol became low enough to make this residual compound a cheap carbon source for several industrial fermentation processes, especially for the production of microbial polyesters (11, 34). However, the various amounts of actual fermentable substrates and the presence of other nonfermentable components in feedstock, such as the various concentrations of glycerol and salts in biodiesel coproducts, hinder their use (42). Therefore, tolerant bioprocesses and/or strains tolerant to such variable factors are required.The production of PHA from glycerol has been investigated in only a few studies (4, 12, 24, 33, 42). In a recent study (32), crude glycerol from different biodiesel manufacturers was examined for suitability as a substrate for PHB production. However, significant decreases in PHB productivity and product yields were recorded when NaCl-contaminated crude glycerol was used.Recently, a newly isolated bacterium, Zobellella denitrificans MW1, was characterized as producing large amounts of PHB from glycerol, with enhanced growth and polymer productivity in the presence of NaCl (20). The present study aimed at developing a strategy to improve the volumetric production of PHB by Z. denitrificans MW1, using glycerol as the sole carbon source. For this purpose, several fed-batch cultivations were set up to steadily improve the nutrient supply to attain a high cell density and high PHB productivity. Moreover, the conventional organic solvent extraction method was modified with regard to an economically more feasible large-scale PHB extraction, achieving a high purity and recovery of the polymer.     

Algal Lipid Bodies: Stress Induction,Purification, and Biochemical Characterization in Wild-Type and Starchless Chlamydomonas reinhardtii

When the unicellular green soil alga Chlamydomonas reinhardtii is deprived of nitrogen after entering stationary phase in liquid culture, the cells produce abundant cytoplasmic lipid bodies (LBs), as well as abundant starch, via a pathway that accompanies a regulated autophagy program. After 48 h of N starvation in the presence of acetate, the wild-type LB content has increased 15-fold. When starch biosynthesis is blocked in the sta6 mutant, the LB content increases 30-fold, demonstrating that genetic manipulation can enhance LB production. The use of cell wall-less strains permitted development of a rapid “popped-cell” microscopic assay to quantitate the LB content per cell and permitted gentle cell breakage and LB isolation. The highly purified LBs contain 90% triacylglycerol (TAG) and 10% free fatty acids (FFA). The fatty acids associated with the TAGs are ∼50% saturated (C₁₆ and C₁₈) fatty acids and ∼50% unsaturated fatty acids, half of which are in the form of oleic acid (C_18:1). The FFA are ∼50% C₁₆ and ∼50% C₁₈. The LB-derived TAG yield from a liter of sta6 cells at 10⁷ cells/ml after starvation for 48 h is calculated to approach 400 mg. The LB fraction also contains low levels of charged glycerolipids, with the same profile as whole-cell charged glycerolipids, that presumably form LB membranes; chloroplast-specific neutral glycerolipids (galactolipids) are absent. Very low levels of protein are also present, but all matrix-assisted laser desorption ionization-identified species are apparent contaminants. Nitrogen stress-induced LB production in C. reinhardtii has the hallmarks of a discrete pathway that should be amenable to additional genetic and culture condition manipulation.There is keen interest in the development of technologies that harvest lipids from microalgae and convert them into diesel fuel (7, 11, 24, 43). A widely adopted approach is to identify algal species that are ascertained to be oleaginous (e.g., Neochloris, Nannochloropsis, and Dunaliella species) and focus on extracting and processing their oils (43). We have adopted a complementary approach, which is to start with the unicellular green soil alga Chlamydomonas reinhardtii, widely regarded as nonoleaginous (48), and utilize the highly developed molecular and genetic tools available for this organism (22) to investigate how its oil production might be enhanced. Such information could then, in the future, be applied to any algae that may prove promising for industrial application.Algal oil production is commonly quantitated by extracting cells with organic solvents, characterizing the lipid fraction, and expressing the lipid yield as the percent dry weight of the starting material (24, 19, 43). Many cellular components (e.g., pigments, cell walls, and starch) contribute to dry weight, and these may change in quantity and/or composition during the cell cycle and/or during fluctuations in growth conditions for a given alga; they are also likely to differ among different algal lineages. Therefore, this convention provides an ambiguous metric for assessing how much oil a given cell produces when genetic background and/or culture conditions are manipulated and may yield misleading between-species comparisons.A related difficulty with this convention is that the extract is expected to contain lipids from numerous sources, e.g., plasma membranes, endomembranes, chloroplasts, and lipid bodies (LBs) dedicated to the storage of triacylglycerides (TAG) and fatty acids (FA). Although all of these sources are of potential value for fuel production, it is problematic to evaluate the output of a particular pathway when the outputs from multiple pathways are being pooled.We have therefore elected to focus on the biosynthesis of LBs (also referred to as lipid droplets or oil bodies), since this process has the hallmark of a discrete and inducible pathway amenable to genetic and culture condition manipulation (37), and we have developed a simple and direct microscopic assay for quantitating LB production per cell that is independent of dry weight.The assay was used to study two parameters. (i) Increases in extractable TAG in numerous algal species, including C. reinhardtii (65), when cells are starved for nitrogen (N) have been reported previously (3, 4, 25, 26, 33, 43, 44, 49, 53, 57, 59). We demonstrate that, in C. reinhardtii, this increase correlates with a robust increase in LB production. (ii) N starvation has also been shown to stimulate a pronounced increase in the biosynthesis of starch granules in C. reinhardtii (31, 35, 45), prompting us to ask whether LB production might be enhanced if starch production was eliminated. We report that the cw15 sta6 starch null strain (66) deleted in ADP glucose phosphorylase (an essential enzyme in the starch biosynthetic pathway) produces twice as much LB-associated TAG as its parental cw15 strain under nitrogen stress, suggesting that carbon skeletons normally converted into starch are instead able to flow into the starvation-induced TAG biosynthetic pathway when the starch option is unavailable.We have also developed a simple LB purification procedure that has permitted analysis of LB composition. The bodies contain ∼90% TAG, ∼10% free FA (FFA), and minor levels of charged glycerolipids (CGLs). Protein levels are also minor, and no proteins with the expected features of “dedicated” LB proteins, like the oleosins or caleosins of plant seeds, were identified.     

Quantitative Detection of Human Adenoviruses in Wastewater and Combined Sewer Overflows Influencing a Michigan River

Enteric viruses are important pathogens found in contaminated surface waters and have previously been detected in waters of the Great Lakes. Human adenoviruses were monitored because of their high prevalence and persistence in aquatic environments. In this study, we quantified adenoviruses in wastewater, surface water, and combined sewer overflows (CSOs) by real-time PCR. Between August 2005 and August 2006, adenovirus concentrations in raw sewage, primary-treated effluent, secondary-treated effluent, and chlorinated effluent from a wastewater treatment plant in Michigan were examined. CSO samples (n = 6) were collected from a CSO retention basin in Grand Rapids, MI. Adenoviruses were detected in 100% of wastewater and CSO discharge samples. Average adenovirus DNA concentrations in sewage and CSOs were 1.15 × 10⁶ viruses/liter and 5.35 × 10⁵ viruses/liter, respectively. Adenovirus removal was <2 log₁₀ (99%) at the wastewater treatment plant. Adenovirus type 41 (60% of clones), type 12 (29%), type 40 (3%), type 2 (3%), and type 3 (3%) were isolated from raw sewage and primary effluents (n = 28). Six of 20 surface water samples from recreational parks at the lower Grand River showed virus concentrations above the real-time PCR detection limit (average, 7.8 × 10³ viruses/liter). This research demonstrates that wastewater effluents and wastewater-impacted surface waters in the lower Grand River in Michigan contain high levels of viruses and may not be suitable for full-body recreational activities. High concentrations of adenovirus in these waters may be due to inefficient removal during wastewater treatment and to the high persistence of these viruses in the environment.Enteric viruses are important waterborne pathogens. They are frequently isolated from feces-contaminated water and have been linked to numerous waterborne outbreaks (9, 34, 42, 61). This group of pathogens includes adenoviruses, enteroviruses, hepatitis A virus, noroviruses, and rotavirus. In the Great Lakes region, enteric viruses were isolated from recreational beaches and groundwater for municipal usage, indicating an elevated public health risk in consuming or coming into contact with these waters (15, 69). Although recent developments in molecular detection assays substantially increase the detection of viruses from waters, from a management standpoint it is impractical to test all viruses when determining the microbial quality of water. Here we propose that adenovirus monitoring can be used to examine wastewater impacts on surface water quality.Adenoviruses, which have a high prevalence in water, have been suggested as preferred candidates as index organisms for viral pathogens because they fit most criteria for an ideal indicator (19, 33, 38, 54). It is estimated that more than 90% of the human population is seropositive for one or more serotypes of adenoviruses (11, 68). Human adenoviruses (HAdVs) are present at a higher frequency in sewage than are other enteric viruses (54) and are excreted in high concentrations from infected patients (up to 10¹¹ viral particles per gram of feces) (68).Adenoviruses were first isolated from humans and identified as the causative agent of epidemic febrile respiratory disease among military recruits in the 1950s (30, 55). Human adenoviruses are the second most important viral pathogen of infantile gastroenteritis, after rotavirus (3, 10, 44, 51, 58, 62, 65). Serotypes of adenoviruses have been found to cause symptomatic infections in several organ systems, including the respiratory system (pharyngitis, acute respiratory disease, and pneumonia), eye (conjunctivitis), gastrointestinal tract (gastroenteritis), central nervous system (meningoencephalitis), and genitalia (urethritis and cervicitis) (8, 37). Human adenovirus types 40 and 41 have been associated with gastroenteritis in children, while human adenovirus type 4 is linked to persistent epidemics of acute respiratory disease in the United States (10, 49). It was estimated that 2 to 7% of all lower respiratory tract illnesses in children may be caused by adenoviruses (5, 17).Transmission routes of adenoviruses include the fecal-oral route and inhalation of aerosols. Adenoviruses have been associated with outbreaks in different settings, including military camps (7, 36, 40), hospitals (6, 28, 32), day care centers (1, 38), and schools (27). Waterborne outbreaks due to adenoviruses have also involved swimming pools (53, 64).It is hypothesized that combined sewer overflows (CSOs; where storm water and untreated sewage are combined) may contribute high concentrations of waterborne pathogens, especially viruses, which in turn may pose an adverse risk to human health. In older cities of Michigan, such as Detroit, East Lansing, and Grand Rapids, major contributors to microbial contamination of surface water during high-rainfall events include discharges from sanitary sewer systems and combined sewer systems. The federal government''s effort to control CSOs started in 1994, when the U.S. EPA published the CSO Control Policy as the national framework. In Michigan, the first CSO policy was drafted by the Department of Environmental Quality in 1983. However, the first noncontested permit requiring a long-term CSO correction program was issued to the Grand Rapids wastewater treatment plant (WWTP) only in Fall 1988, following a large CSO event in the city that affected water quality downstream, in Grand Haven (50). To date, Michigan communities have eliminated 75% of the 613 untreated CSO outfalls that existed in the year 1988, and the remaining 25% are scheduled for correction/elimination through implementation of long-term control plans. However, water quality after CSO or any sewage spill remains a public health concern to individuals via recreational water exposure at recreational parks and beaches downstream of discharge sites.The aim of this study was to evaluate the presence and concentration of adenoviruses in sewage and in the Grand River in the state of Michigan. Raw sewage, wastewater effluent, CSO discharges, and surface water in the lower Grand River were surveyed for the occurrence and concentration of human adenoviruses. Real-time PCR was used for quantification. Predominant adenovirus genotypes in sewage were determined, and the efficiency of virus removal during wastewater treatment was evaluated.     

New Electropositive Filter for Concentrating Enteroviruses and Noroviruses from Large Volumes of Water

The U.S. Environmental Protection Agency''s information collection rule requires the use of 1MDS electropositive filters for concentrating enteric viruses from water, but unfortunately, these filters are not cost-effective for routine viral monitoring. In this study, an inexpensive electropositive cartridge filter, the NanoCeram filter, was evaluated for its ability to concentrate enteroviruses and noroviruses from large volumes of water. Seeded viruses were concentrated using the adsorption-elution procedure. The mean percent retention of seeded polioviruses by NanoCeram filters was 84%. To optimize the elution procedure, six protocols, each comprising two successive elutions with various lengths of filter immersion, were evaluated. The highest virus recovery (77%) was obtained by immersing the filters in beef extract for 1 minute during the first elution and for 15 min during the second elution. The recovery efficiencies of poliovirus, coxsackievirus B5, and echovirus 7 from 100-liter samples of seeded tap water were 54%, 27%, and 32%, respectively. There was no significant difference in virus recovery from tap water with a pH range of 6 to 9.5 and a water flow rate range of 5.5 liters/min to 20 liters/min. Finally, poliovirus and Norwalk virus recoveries by NanoCeram filters were compared to those by 1MDS filters, using tap water and Ohio River water. Poliovirus and Norwalk virus recoveries by NanoCeram filters from tap and river water were similar to or higher than those by the 1MDS filters. These data suggest that NanoCeram filters can be used as an inexpensive alternative to 1MDS filters for routine viral monitoring of water.Viruses that primarily infect and replicate in the gastrointestinal tract are known as enteric viruses. More than 140 different enteric viruses are known to infect humans. These include the enteroviruses, rotaviruses, hepatitis A virus, noroviruses, adenoviruses, and reoviruses, among others. Enteric viruses are capable of causing a wide range of illnesses, including gastroenteritis, paralysis, aseptic meningitis, herpangina, respiratory illness, fevers, myocarditis, etc. Given the potential public health impact of the enteric viruses, enteroviruses (echovirus and coxsackievirus), adenoviruses, and caliciviruses are on the U.S. Environmental Protection Agency''s contaminant candidate list 2 for regulatory consideration for drinking water (11). Within the Caliciviridae family, noroviruses are the primary viruses of concern for drinking water.Contaminated drinking water is considered to be a potential transmission route, and an infectious dose in humans may consist of only a small number of virus particles. Enteric viruses are introduced in aquatic environments through natural or human activities, such as leaking sewage and septic systems, urban runoff, landfills, injection of treated wastewater into aquifers, wastewater discharge, sewage outfall, etc. These viruses have been found in surface water, groundwater, and drinking water (1, 6, 13, 22, 26). Between 1971 and 2004, 789 drinking water outbreaks and 575,207 cases of illness were reported in the United States, and 8% of the reported outbreaks were due to enteric viruses (2, 5, 28, 29, 30, 46).The levels of enteric viruses in natural waters are often low, and as such, typical virus sampling involves a primary concentration of viruses from large volumes of water (hundreds to thousands of liters). Unlike other waterborne pathogens (such as bacteria and parasites), viruses are smaller, and thus, size exclusion filtration is often not practical, especially for turbid waters. In addition, viruses are negatively charged in natural environments and can be adsorbed onto a number of different matrices by electrostatic and hydrophobic interactions (16). Consequently, different types of matrices have been used to isolate enteric viruses from water. These include negatively and positively charged membranes or cartridge filters (10, 17, 32, 34, 35, 39), gauze pad (31), and glass powder or glass wool (14, 27). Of all of these methods, electronegative and electropositive filters are most commonly used. In the case of electronegative filters, the acidification of the water and addition of multivalent cations are required for optimal virus adsorption. Because of this need to condition the water to attain acceptable recoveries, it is difficult to use electronegative filters for field sampling. In contrast, electropositive filters do not require conditioning of the water. Among all the filters, 1MDS electropositive filters (Cuno, Meriden, CT) are the most commonly used filter for fresh and drinking water sampling; however, they are not cost-effective for routine viral monitoring of water and require pH adjustment for waters with pH values exceeding 8.0 (12).Viruses adsorbed on the filter are usually eluted and recovered using 1 to 1.6 liters of eluting solution (6, 12). Many different procedures are described in the literature to elute viruses from filters. These procedures include the use of different eluting solutions, such as 0.3%, 1.5% or 3% beef extract, urea-arginine phosphate buffer, glycine buffer, etc. (10, 12, 24, 37). There are also different elution processes, such as single elution, recirculation of eluents, or successive elution of filters (6, 8, 15, 43). Sobsey and Hickey (40) used only one elution with 0.3% beef extract in 50 mM glycine. Sobsey et al. (43) suggested that 1 liter of 1.5% beef extract be recirculated through the filters for 5 min. Dahling and Wright (8) reported that the highest virus recoveries were obtained by three elutions, each using 1.6 liters of 3% beef extract. Dahling (6) reported that the highest virus recoveries were obtained with two separate beef extract elutions, one being an overnight filter immersion in beef extract.Although methods for concentration of many enteric viruses have been developed, limited studies have been conducted for concentrating noroviruses from water. Huang et al. (21) described a norovirus concentration method using porcine calicivirus (Pan-1) as a surrogate. Pan-1 was sensitive to the high pH (9.5) of the eluting solution, which is commonly used. Myrmel et al. (33) described a method of norovirus concentration using feline calicivirus as a surrogate organism. The method used electronegative filters, and the recovery of virus was 5 to 10%. Many other studies reported detection of human noroviruses in environmental waters (18, 19, 25); however, none of these studies evaluated the recovery efficiencies of human noroviruses from large volumes of water.The objective of this study was to evaluate the NanoCeram (Argonide, Sanford, FL) cartridge filter for the concentration of enteroviruses and noroviruses from large volumes of water. NanoCeram filters have an active component of nano alumina (AlOOH) fibers, which give them a naturally occurring electropositive charge.     

Distribution of Legionella Species from Environmental Water Sources of Public Facilities and Genetic Diversity of L. pneumophila Serogroup 1 in South Korea

A total of 560 Legionella species were isolated from environmental water sources from public facilities from June to September 2008 throughout South Korea. The distribution of Legionella isolates was investigated according to geographical region, facility type, and sample type. The genetic diversity of 104 isolates of Legionella pneumophila serogroup 1 (sg 1) was analyzed by sequence-based typing (SBT). L. pneumophila was distributed broadly throughout Korea, accounting for 85.0% of the isolates, and L. pneumophila sg 1 predominated in all of the public facilities except for the springs. Legionella anisa and Legionella bozemanii predominated among non-L. pneumophila species (48.1% and 21.0%, respectively). The second most dominant strain differed depending on the facility type: L. anisa was the second most dominant strain in the buildings (10.8%), L. pneumophila sg 5 in public baths (21.6%), L. pneumophila sg 6 in factories (12.0%), and L. pneumophila sg 7 in hospitals (13.1%). In the SBT analysis, 104 L. pneumophila sg 1 isolates were differentiated into 26 sequence types (STs) and categorized into 3 clonal groups (CGs) and 10 singleton STs via the eBURST V3 program. ST1, a potential founder of major CG1, was commonly distributed (48.1%). The dominant ST in hot water was ST-K1 (7, 12, 17, 3, 35, 11, 11), which was designated in this study (36.1%). The second most dominant strain differed depending on the type of facility from which the samples were obtained. The unique allelic profile of ST-K1, obtained from hot water, was not found in the European Working Group for Legionella Infections (EWGLI) SBT database.Legionella species, ubiquitous Gram-negative bacteria, are found in a variety of artificial water systems, natural freshwaters, and soils. Currently, the Legionella genus includes 52 species and more than 70 different serogroups, and more than 20 species have been proven to be causative agents of Legionnaires'' disease (LD). The species Legionella pneumophila accounts for approximately 90% of confirmed cases of legionellosis, and L. pneumophila serogroup 1 (sg 1) has been recognized as the most important agent in this regard, as that specific strain was initially implicated as the pathogen causative of LD in 1977 (15; http://www.bacterio.cict.fr/l/legionellaceae.html). The other non-L. pneumophila sg 1 strains, sg 2 to 15, accounted for 7.4% of cases, and Legionella longbeachae (3.9%) and Legionella bozemanii (2.4%) have also been associated with the pathogen of LD. In particular, L. longbeachae has been recognized as accounting for 30.4% of community-acquired Legionella isolates in Australia and New Zealand (53).The most common transmission mechanism of legionellosis is the inhalation of aerosols from the water systems of artificial facilities, including large buildings, hotels, hospitals, public baths, spas, or decorative fountains contaminated by Legionella species (1). Therefore, hot water and water from cooling towers have been perceived as sources of infection in cases of community-acquired, nosocomially acquired, or travel-associated LD (15, 26, 31, 37, 38, 39, 41, 43). Thus, it is important from a public health perspective to continually survey environmental water systems for the presence of Legionella species (2, 34, 35). In particular, hot-water systems used as public baths, such as springs, spas, or tubs, have become a popular means of recreation in a lot of countries, including South Korea. The contamination of hot-water systems has gradually become recognized as an important risk factor all over the world (4, 12, 18, 23, 42, 50), as sources of legionellosis have been detected increasingly since 1982 (52) and many cases of nosocomially acquired (32, 51) and community-acquired (6, 7, 48) LD have been detected in Legionella-contaminated hot-water systems or hot springs.In South Korea, several cases of nosocomial infection and community-acquired pneumonia have occasionally been reported (9, 45) since the first recognized outbreak in South Korea in 1984, which was associated with Legionella gormanii (27). Since 2006, the Korean National Infectious Disease Surveillance (NIDS) program (http://dis.cdc.go.kr/) has reported an average of 20 cases of LD per year (29). In South Korea, surveys of Legionella acquired from environmental water in public facilities such as hot springs and public baths has been gradually enhanced since 2007. An annual training program for the detection of Legionella species from environmental water systems and clinical specimens is currently conducted for the personnel of 16 Provincial Institute of Health and Environment locations (PIHEs) throughout South Korea. Recently, the rate of detection of environmental Legionella bacteria has been gradually increasing (8.1% in 2006, 9.4% in 2007, and 10.3% in 2008).The principal objectives of this study were to assess the current distribution of Legionella species from environmental water sources from public facilities such as buildings, hotels, public baths, springs, hospitals, or factories throughout South Korea. Additionally, the molecular typing of L. pneumophila sg 1 isolates was conducted using sequence-based typing (SBT) to assess the genetic diversity among the isolates.     

Abundance of Novel and Diverse tfdA-Like Genes,Encoding Putative Phenoxyalkanoic Acid Herbicide-Degrading Dioxygenases,in Soil

Phenoxyalkanoic acid (PAA) herbicides are widely used in agriculture. Biotic degradation of such herbicides occurs in soils and is initiated by α-ketoglutarate- and Fe²⁺-dependent dioxygenases encoded by tfdA-like genes (i.e., tfdA and tfdAα). Novel primers and quantitative kinetic PCR (qPCR) assays were developed to analyze the diversity and abundance of tfdA-like genes in soil. Five primer sets targeting tfdA-like genes were designed and evaluated. Primer sets 3 to 5 specifically amplified tfdA-like genes from soil, and a total of 437 sequences were retrieved. Coverages of gene libraries were 62 to 100%, up to 122 genotypes were detected, and up to 389 genotypes were predicted to occur in the gene libraries as indicated by the richness estimator Chao1. Phylogenetic analysis of in silico-translated tfdA-like genes indicated that soil tfdA-like genes were related to those of group 2 and 3 Bradyrhizobium spp., Sphingomonas spp., and uncultured soil bacteria. Soil-derived tfdA-like genes were assigned to 11 clusters, 4 of which were composed of novel sequences from this study, indicating that soil harbors novel and diverse tfdA-like genes. Correlation analysis of 16S rRNA and tfdA-like gene similarity indicated that any two bacteria with D > 20% of group 2 tfdA-like gene-derived protein sequences belong to different species. Thus, data indicate that the soil analyzed harbors at least 48 novel bacterial species containing group 2 tfdA-like genes. Novel qPCR assays were established to quantify such new tfdA-like genes. Copy numbers of tfdA-like genes were 1.0 × 10⁶ to 65 × 10⁶ per gram (dry weight) soil in four different soils, indicating that hitherto-unknown, diverse tfdA-like genes are abundant in soils.Phenoxyalkanoic acid (PAA) herbicides such as MCPA (4-chloro-2-methyl-phenoxyacetic acid) and 2,4-D (2,4-dichlorophenoxyacetic acid) are widely used to control broad-leaf weeds in agricultural as well as nonagricultural areas (19, 77). Degradation occurs primarily under oxic conditions in soil, and microorganisms play a key role in the degradation of such herbicides in soil (62, 64). Although relatively rapidly degraded in soil (32, 45), both MCPA and 2,4-D are potential groundwater contaminants (10, 56, 70), accentuating the importance of bacterial PAA herbicide-degrading bacteria in soils (e.g., references 3, 5, 6, 20, 41, 59, and 78).Degradation can occur cometabolically or be associated with energy conservation (15, 54). The first step in the degradation of 2,4-D and MCPA is initiated by the product of cadAB or tfdA-like genes (29, 30, 35, 67), which constitutes an α-ketoglutarate (α-KG)- and Fe²⁺-dependent dioxygenase. TfdA removes the acetate side chain of 2,4-D and MCPA to produce 2,4-dichlorophenol and 4-chloro-2-methylphenol, respectively, and glyoxylate while oxidizing α-ketoglutarate to CO₂ and succinate (16, 17).Organisms capable of PAA herbicide degradation are phylogenetically diverse and belong to the Alpha-, Beta-, and Gammproteobacteria and the Bacteroidetes/Chlorobi group (e.g., references 2, 14, 29-34, 39, 60, 68, and 71). These bacteria harbor tfdA-like genes (i.e., tfdA or tfdAα) and are categorized into three groups on an evolutionary and physiological basis (34). The first group consists of beta- and gammaproteobacteria and can be further divided into three distinct classes based on their tfdA genes (30, 46). Class I tfdA genes are closely related to those of Cupriavidus necator JMP134 (formerly Ralstonia eutropha). Class II tfdA genes consist of those of Burkholderia sp. strain RASC and a few strains that are 76% identical to class I tfdA genes. Class III tfdA genes are 77% identical to class I and 80% identical to class II tfdA genes and linked to MCPA degradation in soil (3). The second group consists of alphaproteobacteria, which are closely related to Bradyrhizobium spp. with tfdAα genes having 60% identity to tfdA of group 1 (18, 29, 34). The third group also harbors the tfdAα genes and consists of Sphingomonas spp. within the alphaproteobacteria (30).Diverse PAA herbicide degraders of all three groups were identified in soil by cultivation-dependent studies (32, 34, 41, 78). Besides CadAB, TfdA and certain TfdAα proteins catalyze the conversion of PAA herbicides (29, 30, 35). All groups of tfdA-like genes are potentially linked to the degradation of PAA herbicides, although alternative primary functions of group 2 and 3 TfdAs have been proposed (30, 35). However, recent cultivation-independent studies focused on 16S rRNA genes or solely on group 1 tfdA sequences in soil (e.g., references 3-5, 13, and 41). Whether group 2 and 3 tfdA-like genes are also quantitatively linked to the degradation of PAA herbicides in soils is unknown. Thus, tools to target a broad range of tfdA-like genes are needed to resolve such an issue. Primers used to assess the diversity of tfdA-like sequences used in previous studies were based on the alignment of approximately 50% or less of available sequences to date (3, 20, 29, 32, 39, 47, 58, 73). Primers specifically targeting all major groups of tfdA-like genes to assess and quantify a broad diversity of potential PAA degraders in soil are unavailable. Thus, the objectives of this study were (i) to develop primers specific for all three groups of tfdA-like genes, (ii) to establish quantitative kinetic PCR (qPCR) assays based on such primers for different soil samples, and (iii) to assess the diversity and abundance of tfdA-like genes in soil.     

Identification of a Novel Alkaliphilic Esterase Active at Low Temperatures by Screening a Metagenomic Library from Antarctic Desert Soil

A novel esterase was identified through functional screening of a metagenomic library in Escherichia coli obtained from Antarctic desert soil. The 297-amino-acid sequence had only low (<29%) similarity to a putative esterase from Burkholderia xenovorans. The enzyme was active over a temperature range of 7 to 54°C and at alkaline pH levels and is a potential candidate for industrial application.The cold deserts of the McMurdo Dry Valleys, South Victoria Land, Eastern Antarctica, are widely acknowledged as having the harshest soil environments on Earth (6, 8, 26). Despite the apparent hostility of the environment, we and others have reported both unexpectedly high biomass (9) and phylogenetic diversity (1, 19, 24, 29) in Antarctic soils. The presence of numerous novel taxa suggests that these soils might prove to be valuable sources of genetic material for mining novel industrial enzymes active at low temperatures (9, 23).Esterases (EC 3.1.1.1) and lipases (EC 3.1.1.3) catalyze the hydrolysis and synthesis of ester compounds. Their applications in industry cover a broad spectrum, including as detergent additives, in food processing, in environmental bioremediation, and in biomass and plant waste degradation for the production of useful organocompounds (3, 16).In this study, a novel esterase was isolated from a metagenomic fosmid library obtained from Antarctic soil. The enzyme displays activity over a wide temperature range and has very low similarity (<29% amino acid identity) to esterases in the GenBank database. The study demonstrates the value of Antarctic metagenomes as a source of novel industrial products.     

Community Structure and Dynamics of Small Eukaryotes Targeted by New Oligonucleotide Probes: New Insight into the Lacustrine Microbial Food Web

The seasonal dynamics of the small eukaryotic fraction (cell diameter, 0.2 to 5 μm) was investigated in a mesotrophic lake by tyramide signal amplification-fluorescence in situ hybridization targeting seven different phylogenetic groups: Chlorophyceae, Chrysophyceae, Cryptophyceae, Cercozoa, LKM11, Perkinsozoa (two clades), and Fungi. The abundance of small eukaryotes ranged from 1,692 to 10,782 cells ml⁻¹. The dominant groups were the Chrysophyceae and the Chlorophyceae, which represented 19.6% and 17.9% of small eukaryotes, respectively. The results also confirmed the quantitative importance of putative parasites, Fungi and Perkinsozoa, in the small heterotrophic eukaryotic assemblage. The relative abundances recorded for the Perkinsozoa group reached as much as 31.6% of total targeted eukaryotes during the summer. The dynamics of Perkinsozoa clade 1 coincided with abundance variations in Peridinium and Ceratium spp. (Dinoflagellates), while the dynamics of Perkinsozoa clade 2 was linked to the presence of Dinobryon spp. (Chrysophyceae). Fungi, represented by chytrids, reached maximal abundance in December (569 cells ml⁻¹) and were mainly correlated with the dynamics of diatoms, especially Melosira varians. A further new finding of this study is the recurrent presence of Cercozoa (6.2%) and LKM11 (4.5%) cells. This quantitative approach based on newly designed probes offers a promising means of in-depth analysis of microbial food webs in lakes, especially by revealing the phylogenetic composition of the small heterotrophic flagellate assemblage, for which an important fraction of cells are generally unidentified by classical microscopy (on average, 96.8% of the small heterotrophic flagellates were identified by the specific probes we used in this study).Recently developed molecular methods based on the amplification and sequencing of rRNA genes have made it possible to investigate picoeukaryote assemblage composition (pigmented or nonpigmented unicellular eukaryotes with cell diameters of <2 μm or <5 μm according to the studies) in various aquatic systems, independently of morphological identification and cultivation (14, 23, 27, 28, 29, 39). The essential role of picoplankton (both eukaryotic and prokaryotic) as a contributor to plankton biomass and to carbon and nutrient cycling has long been established (9), but the unexpected diversity among the smallest eukaryotes (cell diameters, <5 μm) was only recently revealed. Most of these data were obtained in oceanic systems, but a few recent studies conducted in lakes have also highlighted the broad diversity of 18S rRNA sequences affiliated with numerous phylogenetic groups: Chlorophyceae, Chrysophyceae, Cryptophyceae, Cercozoa, Fungi, Choanoflagellida, Bicosoecida, Ciliophora, Haptophyceae, Perkinsozoa, LKM11, Hyphochytridiomycota, Katablepharidaceae, Dinophyceae, and Eustigmatophyceae (22, 23, 24, 34). Thus, it has been possible to observe clear seasonal changes in small-eukaryote structure in an oligomesotrophic lake (23), and the lake-based studies generally report a dominance of heterotrophic cells within the lacustrine small-eukaryote assemblage. Moreover, the recurrent presence of sequences affiliated with parasitic groups has been highlighted in lakes of various trophic statuses (22, 23). Lepère et al. (25) reported the unexpected importance of two groups: first, fungi affiliated with two clades of chytrids known as parasites of various groups of microalgae; and second, members of the phylum Perkinsozoa belonging to two clades closely related to Perkinsus marinus and Parvilucifera infectans, which are parasites of bivalves and dinoflagellates, respectively (30), and whose systematic position has been controversial, since they are phylogenetically related to the Apicomplexa or the Dinoflagellata (6, 13).Although these data brought new insight into the structural diversity of lacustrine small eukaryotes, the relative importance, dynamics, and functional roles of these microorganisms from various phylogenetic groups are still largely unknown. We now need to research specific in situ abundances of previously undetected taxa. In this study, specially developed oligonucleotide probes, designed on the basis of molecular data obtained from sequencing (20, 21, 22, 23, 24, 25, 34), were used for fluorescence in situ hybridization (FISH) coupled with tyramide signal amplification (TSA) to investigate the composition, abundance, and dynamics of lacustrine small eukaryotes (<5 μm) in the mesotrophic Lake Bourget over 1 year. Special attention was paid to the dynamics of putative parasitic groups (Perkinsozoa, Fungi, Cercozoa).     

Subcellular Localization of the Barley Stripe Mosaic Virus Triple Gene Block Proteins

Barley stripe mosaic virus (BSMV) spreads from cell to cell through the coordinated actions of three triple gene block (TGB) proteins (TGB1, TGB2, and TGB3) arranged in overlapping open reading frames (ORFs). Our previous studies (D. M. Lawrence and A. O. Jackson, J. Virol. 75:8712-8723, 2001; D. M. Lawrence and A. O. Jackson, Mol. Plant Pathol. 2:65-75, 2001) have shown that each of these proteins is required for cell-to-cell movement in monocot and dicot hosts. We recently found (H.-S. Lim, J. N. Bragg, U. Ganesan, D. M. Lawrence, J. Yu, M. Isogai, J. Hammond, and A. O. Jackson, J. Virol. 82:4991-5006, 2008) that TGB1 engages in homologous interactions leading to the formation of a ribonucleoprotein complex containing viral genomic and messenger RNAs, and we have also demonstrated that TGB3 functions in heterologous interactions with TGB1 and TGB2. We have now used Agrobacterium tumefaciens-mediated protein expression in Nicotiana benthamiana leaf cells and site-specific mutagenesis to determine how TGB protein interactions influence their subcellular localization and virus spread. Confocal microscopy revealed that the TGB3 protein localizes at the cell wall (CW) in close association with plasmodesmata and that the deletion or mutagenesis of a single amino acid at the immediate C terminus can affect CW targeting. TGB3 also directed the localization of TGB2 from the endoplasmic reticulum to the CW, and this targeting was shown to be dependent on interactions between the TGB2 and TGB3 proteins. The optimal localization of the TGB1 protein at the CW also required TGB2 and TGB3 interactions, but in this context, site-specific TGB1 helicase motif mutants varied in their localization patterns. The results suggest that the ability of TGB1 to engage in homologous binding interactions is not essential for targeting to the CW. However, the relative expression levels of TGB2 and TGB3 influenced the cytosolic and CW distributions of TGB1 and TGB2. Moreover, in both cases, localization at the CW was optimal at the 10:1 TGB2-to-TGB3 ratios occurring in virus infections, and mutations reducing CW localization had corresponding effects on BSMV movement phenotypes. These data support a model whereby TGB protein interactions function in the subcellular targeting of movement protein complexes and the ability of BSMV to move from cell to cell.Plants use macromolecular trafficking pathways through plasmodesmata (PD) as a means to regulate developmental processes and physiological functions, and they also rely on these channels as avenues to communicate and mount defense responses to pathogen challenge (2, 37, 55). Local and systemic plant virus invasion depends on the abilities of viruses to use these pathways to spread from initially infected cells to the vascular tissue and distal regions of the plant. To this end, viruses infecting plants have evolved movement proteins (MPs) that coopt host trafficking pathways to target virus genomes to the PD and to facilitate the cell-to-cell transit of infectious entities (4, 13, 36, 48, 55). Virus MPs vary in size, number, and genome organization, but they share a number of functional characteristics including localization to PD, an ability to increase the size exclusion limits of PD, and RNA binding activities (3, 7, 8, 24, 27, 58).Viruses containing triple gene block (TGB) MPs have been the subjects of a number of investigations (4, 6, 39, 53, 54). Interestingly, viruses with a range of diverse genome structures encode MPs in a TGB, but these proteins fall into two major TGB classes that have substantial differences in protein structure and variations in their physical, functional, and cellular interactions (19, 30, 39, 45, 48). For example, the hordeivirus-like TGB1 proteins contain substantial N-terminal extensions that are lacking in the potexvirus-like TGB1 proteins, but the two classes of proteins share a conserved helicase domain at their C termini (39). The available evidence also indicates that hordeivirus-like and potexvirus-like TGB1 proteins share common biochemical features, including RNA binding abilities (3, 13, 23, 35, 44, 56), RNA helicase activities (22), associated NTPase activities (3, 13, 23, 33, 35, 44), and the capacity to form homologous interactions (29, 30, 45). However, the potexvirus-like TGB1 proteins localize at the CW when expressed autonomously and also facilitate increases in PD size exclusion limits, whereas the hordeivirus-like TGB1 proteins lack both these activities (39, 53). Major differences are also evident in the organizations of the potexvirus-like and hordeivirus-like TGB3 proteins, which share no discernible relatedness, differ in the numbers of their transmembrane domains, and indeed appear to have a polyphyletic origin (39).In both TGB classes, the movement strategy employs the coordinated actions of all three proteins. However, the coat protein is dispensable for one or more phases of movement of benyvirus, hordeivirus, pecluvirus, and pomovirus, encoding hordeivirus-like (class I) MPs, but is absolutely required for cell-to-cell movement of potexvirus-like (class II) MPs encoded by allexivirus, carlavirus, foveavirus, and potexvirus (6, 19, 39, 54). These variations clearly demonstrate that the two classes of TGB proteins have profound differences in their functional properties and in their associations with other virus and host proteins. Hence, comparative analyses of the functional and biological properties of the two classes of proteins in their common hosts may reveal important activities relevant to viral pathogenesis. To provide more information about the hordeivirus-like movement mechanisms, we are investigating the TGB interactions of Barley stripe mosaic virus (BSMV).BSMV is the type member of the genus Hordeivirus, which includes Poa semilatent virus (PSLV), Lychnis ringspot virus, and Anthoxanthum latent blanching virus (6, 19). Hordeiviruses have positive-sense, single-stranded RNA genomes consisting of three segments, designated α, β, and γ. The RNAβ segment encodes the coat protein, which is translated directly from genomic RNAβ (gRNAβ), and the TGB proteins, which are expressed from two subgenomic RNAs (sgRNAs), designated sgRNAβ1 and sgRNAβ2 (60). The coat protein is dispensable for the systemic movement of BSMV (41), and mutational analyses indicate that the TGB1, TGB2, and TGB3 proteins are each essential for cell-to-cell movement in monocot and dicot hosts (28). The BSMV TGB1 (58-kDa) protein is expressed from sgRNAβ1 at higher levels than the smaller hydrophobic TGB2 (14-kDa) and TGB3 (17-kDa) proteins, which are coexpressed from the bicistronic sgRNAβ2 during replication (14, 60). BSMV TGB1 has binding activity for both single-stranded and double-stranded RNAs (13) and forms nucleoprotein complexes with each of the BSMV gRNAs and sgRNAs (30). The hordeivirus-like TGB1 proteins differ from the potexvirus-like TGB1 proteins in having longer N-terminal domains with positively charged amino acids, but both classes of proteins have conserved C-terminal NTPase/helicase domains (13, 39, 49). In BSMV, mutations of conserved amino acids within the TGB1 helicase motif abrogate cell-to-cell movement and alter subcellular localization in infected protoplasts (27). Plants infected with a BSMV β-green fluorescent protein-TGB1 (β-GFP-TGB1) reporter virus also exhibited paired foci on both sides of the CW, and the plasma membranes of infected protoplasts developed punctate foci (27). TGB1 and TGB2 are also essential for plasma membrane targeting because β-GFP-TGB1 reporter derivatives that were unable to express TGB2 or TGB3 fluoresce at perinuclear membranes of protoplasts (27). Particle bombardment studies with the related hordeivirus PSLV also suggested that the expression of TGB3 is required to shift the localization of TGB2 from the endoplasmic reticulum (ER) to the peripheral membranes (50), and transgenically expressed PSLV TGB3 appears to be associated with PD due to its colocalization with callose markers (17).We have recently shown that TGB2 and TGB3 interact physically and have identified single amino acids in each protein that are required for these interactions (19, 30). TGB3 also interacts with TGB1, and we have proposed that these interactions facilitate the transport of ribonucleoprotein (RNP) complexes to the PD (30). However, the effects of TGB protein interactions on subcellular localization have not been defined. Moreover, because of possible convergent evolution of the hordeivirus-like and potexvirus-like TGB-containing viruses (39), the mechanisms of action resulting in transport may differ among different genera or even among different virus species within a genus. To obtain more refined information about these processes, we have now expressed fluorescent TGB fusion proteins transiently in Nicotiana benthamiana leaf cells by Agrobacterium tumefaciens infiltration and have assessed the subcellular localization patterns of BSMV wild-type (wt) and mutant TGB derivatives that differ in their interactions. We also have carried out reverse genetic experiments with selected BSMV TGB mutants to provide a biological context for the localization patterns appearing during ectopic Agrobacterium expression. These findings are elaborated in a model for TGB interactions required for the cell-to-cell movement of BSMV.     

Widespread Infection with Homologues of Human Parvoviruses B19, PARV4, and Human Bocavirus of Chimpanzees and Gorillas in the Wild

Infections with human parvoviruses B19 and recently discovered human bocaviruses (HBoVs) are widespread, while PARV4 infections are transmitted parenterally and prevalent specifically in injecting drug users and hemophiliacs. To investigate the exposure and circulation of parvoviruses related to B19 virus, PARV4, and HBoV in nonhuman primates, plasma samples collected from 73 Cameroonian wild-caught chimpanzees and gorillas and 91 Old World monkey (OWM) species were screened for antibodies to recombinant B19 virus, PARV4, and HBoV VP2 antigens by enzyme-linked immunosorbent assay (ELISA). Moderate to high frequencies of seroreactivity to PARV4 (63% and 18% in chimpanzees and gorillas, respectively), HBoV (73% and 36%), and B19 virus (8% and 27%) were recorded for apes, while OWMs were uniformly negative (for PARV4 and B19 virus) or infrequently reactive (3% for HBoV). For genetic characterization, plasma samples and 54 fecal samples from chimpanzees and gorillas collected from Cameroonian forest floors were screened by PCR with primers conserved within Erythrovirus, Bocavirus, and PARV4 genera. Two plasma samples (chimpanzee and baboon) were positive for PARV4, while four fecal samples were positive for HBoV-like viruses. The chimpanzee PARV4 variant showed 18% and 15% nucleotide sequence divergence in NS and VP1/2, respectively, from human variants (9% and 7% amino acid, respectively), while the baboon variant was substantially more divergent, mirroring host phylogeny. Ape HBoV variants showed complex sequence relationships with human viruses, comprising separate divergent homologues of HBoV1 and the recombinant HBoV3 species in chimpanzees and a novel recombinant species in gorillas. This study provides the first evidence for widespread circulation of parvoviruses in primates and enables future investigations of their epidemiology, host specificity, and (co)evolutionary histories.Autonomous parvoviruses known to infect humans comprise parvovirus B19 (18) and the recently discovered PARV4 (22) and human bocavirus (HBoV) (3). Members of the family Parvoviridae are genetically and biologically diverse and are classified into several genera or groups, showing marked differences in host range, pathology, and tissue/cellular tropisms (18). Human parvovirus B19, a member of the Erythrovirus genus, is transmitted primarily by the respiratory route but causes systemic infections. Erythroid progenitor cells are specifically targeted through expression of globoside P antigen, which acts as the B19 virus receptor for entry (5). In common with infections by most parvoviruses, B19 virus infections are acute; a period of intense viremia is followed by seroconversion for antibody to B19 virus and lifelong immunity from reinfection (29). Despite the clearance of viremia and seroconversion for antibody, lifelong persistence of viral DNA in tissues has been shown to occur (12, 20, 26, 28, 43, 58). Three genotypes of B19 virus have been described, differing in nucleotide sequence by approximately 13 to 14% (7, 21, 41, 53); genotypes 1 and 2 have been found in Europe, the United States, and other Western countries, while genotype 3 is restricted to sub-Saharan Africa and South America (7, 47, 49). B19 virus widely circulates in human populations worldwide; in Western countries, several studies have documented increasing frequencies of B19 virus seropositivity with age, rising to approximately 60 to 70% by adulthood (15, 39, 48, 61).Another human parvovirus, PARV4, shows markedly different epidemiology and transmission routes. It was originally detected in plasma from an individual with an “acute infection syndrome” resembling that of primary human immunodeficiency virus (HIV) infection (22). While this clinical presentation has not been observed again, infection with PARV4 is known to be widespread specifically in individuals with a history of parenteral exposure (injecting drug users [IDUs], hemophiliacs, polytransfused individuals), with a strikingly higher incidence in those infected with HIV-1 (13, 14, 30, 35, 54). These observations suggest that PARV4 is primarily transmitted though parenteral routes in Western countries (54, 56). In common with infection with the better-characterized human parvovirus B19, infection with PARV4 is associated with a period of acute viremia, followed by seroconversion for antibody and long-term persistence of viral DNA sequences in lymphoid and other tissue (33, 37, 52). Circulating variants of PARV4 have been classified into three distinct genotypes exhibiting approximately 8% nucleotide sequence divergence from each other. Genotypes 1 and 2 circulate in Western countries, while genotype 3 has to date been recorded only in sub-Saharan Africa (45, 55).The third human parvovirus, HBoV (3), shows a number of epidemiological and clinical attributes different from those of both B19 virus and PARV4. HBoV was originally found in the respiratory tract of young children and has been the subject of intense investigation as a potential cause of human respiratory disease (reviewed in references 1, 51, and 62). Although it is frequently detected by PCR in the nasopharynx of viremic individuals with primary infections with lower respiratory tract disease, other coinfecting respiratory viruses are frequently detected (19). HBoV additionally shows long-term, low-level carriage in the respiratory tract after primary infection, which further complicates PCR-based etiological studies (2, 38) and warrants the use of other diagnostic strategies, such as serology (30, 32, 59). In contrast to the rather minimal genetic diversity of B19 virus and PARV4 genotypes, bocaviruses infecting humans are now known to comprise three to four major genetic variants (termed types or species 1 to 4) (23, 24). HBoV1 and HBoV2 show 22%, 33%, and 20% amino acid sequence divergence from each other in the encoded viral nonstructural (NS), NP-1, and structural VP1/VP2 proteins, respectively, the latter potentially leading to antigenic diversity and some loss of antigenic cross-reactivity. A third type/species of HBoV is a chimeric form with a nonstructural gene region (NS, NP1) most similar to HBoV1, a recombination breakpoint in the intergenic region between NP1 and VP1, and structural genes related to those of HBoV2 (4, 23). Current data suggest that only HBoV1 is capable of infecting the respiratory tract; most published large-scale screening studies have failed to detect HBoV2 (or HBoV3) in respiratory samples (10, 11, 60), while all three types/species are detectable in fecal samples, indicating the existence of an alternative or additional site of virus replication (23). Despite extensive inquiry, the exact role of HBoV1 in respiratory disease remains unclear, as is the proposed etiological role of HBoV2 (and possibly HBoV3) in gastroenteritis (4, 11, 23, 50). Very recently, a fourth species/type, HBoV4, has been detected in fecal samples; genetically it also shows evidence for past recombination, with NS and NP1 region sequences grouping with HBoV2, while VP1/VP2 is more closely related to HBoV3 (23).We have little understanding of the past epidemiology, evolution, and origins of human parvoviruses. For both B19 virus and PARV4, evidence has been obtained for a temporal succession of genotypes over time (37, 43); in Europe, B19 virus genotype 1 largely replaced type 2 in the 1960 and 1970s (43), while current data indicate that a similar replacement of PARV4 genotypes occurred within the last 20 years (37). The highly restricted sequence diversity of currently circulating variants of PARV4 and B19 virus and of HBoV1 variants supports the hypothesis of a relatively recent emergence and spread of these viruses in human populations (36, 42, 64).The existence and evolution of parvoviruses on a much longer time scale is suggested by the observations that members of the Erythrovirus and Parvovirus genera both contain viruses that are highly host species specific and that the molecular phylogenies of both genera are largely congruent with those of their hosts (34). This has led to the hypothesis of long-term coevolution of parvoviruses with their host over the 90 million years of mammalian evolution and perhaps beyond. Among erythroviruses, simian homologues of B19 virus have been found in cynomolgus monkeys (44) and rhesus and pig-tailed macaques (16) and more genetically distant viruses have been characterized in chipmunks and cows (9, 63). Divergent homologues of PARV4 in pigs and cows have been described (31), while the bovine and canine parvoviruses distantly related to HBoV are the originally described members of the Bocavirus genus. However, the process of virus-host codivergence is known to be punctuated by occasional cross-species transmissions, including the well-documented spread of feline parvovirus to dogs (46). Based on serological evidence, the possible transmission of simian erythroviruses to animal handlers has been proposed (6).To gain further insights into the origins and evolution of human parvoviruses, we have performed large-scale serological and PCR-based screening of nonhuman primates (chimpanzees and gorillas) and of several species of Old World monkeys (OWMs) for evidence of infection with parvoviruses that are antigenically related to the human B19, PARV4, and HBoV viruses. By PCR, we have sought to genetically characterize homologues of the three autonomous human parvoviruses in apes and Old World monkey species and to analyze their evolutionary relationship to human and other mammalian homologues of these viruses.     

Detection of Adenoviruses and Rotaviruses in Drinking Water Sources Used In Rural Areas of Benin,West Africa

Diseases associated with viruses also found in environmental samples cause major health problems in developing countries. Little is known about the frequency and pattern of viral contamination of drinking water sources in these resource-poor settings. We established a method to analyze 10 liters of water from drinking water sources in a rural area of Benin for the presence of adenoviruses and rotaviruses. Overall, 541 samples from 287 drinking water sources were tested. A total of 12.9% of the sources were positive for adenoviruses and 2.1% of the sources were positive for rotaviruses at least once. Due to the temporary nature of viral contamination in drinking water sources, the probability of virus detection increased with the number of samples taken at one test site over time. No seasonal pattern for viral contaminations was found after samples obtained during the dry and wet seasons were compared. Overall, 3 of 15 surface water samples (20%) and 35 of 247 wells (14.2%) but also 2 of 25 pumps (8%) tested positive for adenoviruses or rotaviruses. The presence of latrines within a radius of 50 m in the vicinity of pumps or wells was identified as being a risk factor for virus detection. In summary, viral contamination was correlated with the presence of latrines in the vicinity of drinking water sources, indicating the importance of appropriate decision support systems in these socioeconomic prospering regions.Although access to safe drinking water is considered a human right, many people suffer from inadequate water supply. Especially in developing countries, improper water quality causes major public health problems affecting mortality rates in highly susceptible people (small children and immunocompromised patients) as well as economic income problems due to disease-related nonproductive time. Only 37.4% of households have access to piped water sources in Benin, West Africa, and in rural areas, even fewer have access (3). Many diseases like diarrhea, gastroenteritis, keratoconjunctivitis, respiratory infections, and hepatitis are associated with viruses, often found in environmental samples like groundwater, surface water, sewage, costal water, shellfish, and tap water (5, 6, 10, 13, 23, 38). Virus concentrations in environmental samples are low both due to the inability to replicate without a host cell and because of continuous degradation and dilution effects. On the other hand and in contrast to most bacterial infections, even small amounts of viruses (as few as 10 PCR-detectable units) are sufficient to establish an infection in the new host (24). Bacterial indicators seem to be inappropriate for analyzing viral contamination, since viruses are more resistant to environmental conditions (2) and spread over a longer distance than bacteria (9). Therefore, viruses are often found without any bacterial indicator for fecal contamination (2, 6). In North America, 15 to 30% of all gastrointestinal diseases were suspected of being related to water (30), whereas worldwide, over 88% of diarrheal diseases are waterborne or water related (18).Routine screening of environmental samples for viral contamination is controversially being discussed at the moment. Furthermore, no standard procedure for the detection of viruses in environmental samples currently exists. In numerous studies, virus concentration from water was achieved by filtration using electropositive filters (1MDS) (12, 15, 25, 26, 33). Further methods using ultrafiltration, glass wool filters (7, 22), or immunomagnetic separation (16, 28) were used to detect small amounts of viruses independently of matrix effects. However, the U.S. Environmental Protection Agency listed adenovirus as one of nine microorganisms on the contamination candidate list for drinking water as a potential indicator virus due to an outstanding resistance to UV disinfection. The 51 presently recognized adenovirus serotypes are responsible for a great variety of human diseases like diarrhea, keratoconjunctivitis, and respiratory infections. However, severe diarrhea, especially in small children and immunocompromised patients, is often caused by rotaviruses. The fatal outcome of infant diarrhea substantially contributes to the high mortality rate of children under the age of 5 years in developing countries (8). In Benin, the probability of dying per 1,000 live births under 5 years of age (under-5 mortality rate) was 152 in 2004, and 17.1% of these deaths were caused by diarrheal diseases (37). To address the frequency and pattern of viral contamination in drinking water sources in rural areas of West Africa, we analyzed water samples during the dry and wet seasons in Benin for contamination with adenoviruses as indicators and rotaviruses as important pathogens in developing countries.     

Molecular Detection of Hepatitis E Virus in Sewage Samples

Human hepatitis E virus (HEV) is considered an emerging pathogen in industrialized countries. In Italy, the true burden of HEV infection is unknown. Molecular HEV screening of raw sewage samples from 11 wastewater treatment plants yielded 19 positives (16%; 18 genotype I, 1 genotype III) evenly distributed throughout Italy. Evidence that HEV could be establishing itself in our region is accumulating and may justify more active surveillance to monitor its spread.Hepatitis E is a self-limited, enterically transmitted acute viral hepatitis that occurs most frequently in epidemic outbreaks and often spreads by way of fecally contaminated drinking water (5, 20). Hepatitis E virus (HEV) infections are caused by a positive-sense, nonenveloped RNA virus of the Hepevirus genus. The four major genotypes (GI to GIV), all belonging to a single serotype, are known to infect humans. While GI and GII are restricted to humans, GIII and GIV are zoonotic and may infect animals (swine, chickens, deer, mongooses, and rabbits), as well as humans, in both industrialized and nonindustrialized countries (18, 19). GI consists of epidemic strains circulating in Africa and Asia. GII is found in Mexico and Africa. GIII is widely distributed, mainly—but not exclusively—in the United States, Europe, and Japan. GIV is present in Asia (16). An HEV strain belonging to a fifth genotype has been identified in birds (12).HEV is transmitted by the fecal-oral route. Large waterborne outbreaks with high attack rates among young adults have been described in regions characterized by poor sanitary conditions (22). Hepatitis E is responsible for over 50% of cases of acute viral hepatitis in countries where the disease is endemic (Central and Southeast Asia, North and West Africa, and Mexico), where seroprevalence rates range from 15% to 60% (8). North America and Europe have traditionally been considered areas where HEV is not endemic, with acute infection diagnosed rarely and largely confined to travelers returning from areas where the disease is endemic. The high rates of HEV IgG positivity reported in different studies, however, suggest that unrecognized or subclinical infection is common (8). In Europe, increasing numbers of HEV infections not associated with travel have been recently reported (15).HEV infection may vary in severity from asymptomatic to fulminant. Case fatality rates range between 0.5% and 4% overall but may reach 25% among pregnant women (1). In industrialized countries, the case fatality rate seems to be higher than in areas where the disease is endemic, since infection occurs more frequently in elderly people with chronic liver disease, a subgroup of patients with a case fatality rate approaching 70% (26).HEV, which is shed in the feces of infected individuals, has been detected in sewage samples, suggesting that HEV contamination of aquatic environments may also be present (2, 6, 7, 23). In Italy, the true burden of HEV infection is still unknown and there are no available studies on the presence of this virus in sewage. The prevalence of anti-HEV antibodies among healthy individuals has been found to be approximately 1% in the northern regions and up to 5% in the southern regions, including Sicily and Sardinia. Higher prevalence rates have been found among drug users (especially HIV-infected individuals), hemodialysis patients, and patients with chronic hepatitis C, suggesting that HEV may be transmitted not only by the fecal-oral route (the main mode of transmission) but also parenterally (27).The objective of the present study was to investigate the occurrence of HEV through the molecular screening of raw sewage samples collected from urban wastewater treatment plants (WTPs) in different regions of Italy.     

Genome-Derived Criteria for Assigning Environmental narG and nosZ Sequences to Operational Taxonomic Units of Nitrate Reducers

Ninety percent of cultured bacterial nitrate reducers with a 16S rRNA gene similarity of ≥97% had a narG or nosZ similarity of ≥67% or ≥80%, respectively, suggesting that 67% and 80% could be used as standardized, conservative threshold similarity values for narG and nosZ, respectively (i.e., any two sequences that are less similar than the threshold similarity value have a very high probability of belonging to different species), for estimating species-level operational taxonomic units. Genus-level tree topologies of narG and nosZ were generally similar to those of the corresponding 16S rRNA genes. Although some genomes contained multiple copies of narG, recent horizontal gene transfer of narG was not apparent.Nitrate reducers (i.e., both dissimilatory nitrate reducers and denitrifiers) reduce nitrate to nitrite, which can then be reduced to ammonium by dissimilatory nitrate reducers or sequentially reduced to nitric oxide, nitrous oxide, and dinitrogen by denitrifiers (29). narG codes for the alpha subunit of the dissimilatory nitrate reductase, which reduces nitrate to nitrite and is thus common to both dissimilatory nitrate reducers and denitrifiers (29). nosZ codes for nitrous oxide reductase, which reduces nitrous oxide to dinitrogen and is common to denitrifiers but not dissimilatory nitrate reducers (29). Both narG and nosZ are commonly used as gene markers for community level analysis of nitrate reducers (2, 8, 9, 16, 18, 19, 20, 25). However, standardized criteria for assigning environmental narG and nosZ sequences to operational taxonomic units (OTUs) are required so that diverse data sets on nitrate-reducing communities can be normalized. The widespread ability of bacteria and archaea to denitrify (29) complicates the development of such criteria for genes involved in denitrification. Some closely related narG and closely related nosZ genes occur in distantly related taxa, and narG or nosZ phylogenies do not always reflect 16S rRNA phylogenies (17). However, nosZ-based phylogenies in general have a high degree of congruency with 16S rRNA gene-based phylogenies (3, 10, 30), and recent horizontal gene transfer of nosZ seems unlikely (10), indicating that denitrifier structural genes might be used for estimating the species-level novelty, as well as species-level diversity, of denitrifiers in environmental samples. The limited amount of data on horizontal gene transfer of narG (4, 24) identifies a need to extend such an approach to this gene. The limited number of studies that have compared 16S rRNA with narG or nosZ phylogenies accentuates the need for a more thorough analysis of the phylogenetic relatedness of these three genes (3, 4, 7). Thus, the main objectives of this study were to (i) resolve criteria for standardizing OTU assignment of environmental narG and nosZ sequences, (ii) determine whether those criteria can be used as indicators of novel species, and (iii) investigate the impact of horizontal gene transfer on narG.