Genetic Diversity and Histo-Blood Group Antigen Interactions of Rhesus Enteric Caliciviruses

Recently, we reported the discovery and characterization of Tulane virus (TV), a novel rhesus calicivirus (CV) (T. Farkas, K. Sestak, C. Wei, and X. Jiang, J. Virol. 82:5408-5416, 2008). TV grows well in tissue culture, and it represents a new genus within Caliciviridae, with the proposed name of Recovirus. We also reported a high prevalence of CV antibodies in macaques of the Tulane National Primate Research Center (TNPRC) colony, including anti-norovirus (NoV), anti-sapovirus (SaV), and anti-TV (T. Farkas, J. Dufour, X. Jiang, and K. Sestak, J. Gen. Virol. 91:734-738, 2010). To broaden our knowledge about CV infections in captive nonhuman primates (NHP), 500 rhesus macaque stool samples collected from breeding colony TNPRC macaques were tested for CVs. Fifty-seven (11%) samples contained recovirus isolates. In addition, one NoV was detected. Phylogenetic analysis classified the recovirus isolates into two genogroups and at least four genetic types. The rhesus NoV isolate was closely related to GII human NoVs. TV-neutralizing antibodies were detected in 88% of serum samples obtained from primate caretakers. Binding and plaque reduction assays revealed the involvement of type A and B histo-blood group antigens (HBGA) in TV infection. Taken together, these findings indicate the zoonotic potential of primate CVs. The discovery of a genetically diverse and prevalent group of primate CVs and remarkable similarities between rhesus enteric CVs and human NoVs opens new possibilities for research involving in vitro and in vivo models of human NoV gastroenteritis.Caliciviruses (CV) are important human and animal pathogens, causing a wide variety of diseases in their respective hosts. The family Caliciviridae consists of five established genera (Norovirus, Sapovirus, Lagovirus, Vesivirus, and Nebovirus). Recently, two new calicivirus genera have been proposed, represented by the Tulane virus (Recovirus) and the St. Valerien-like viruses (Valovirus) (11-13, 24, 36, 37, 39).NoVs are recognized as the leading cause of epidemics of gastroenteritis (GE), causing 80 to 90% of nonbacterial GE outbreaks and more than 50% of all food-related GE outbreaks (7, 8, 29). They are also an important cause of sporadic GE in both children and adults. Based on phylogenetic analysis, NoVs are divided into five genogroups and more than 30 genetic clusters or genotypes (9, 46). This high genetic and, likely, antigenic variation, combined with the lack of a tissue culture or animal model, represent major obstacles for NoV research.NoVs with close genetic and antigenic relatedness to human NoVs have been isolated from various animal species (6, 28, 33, 41). This not only provided opportunities for using some of these viruses as surrogates for human NoV research (44) but also raised the concern of the possible zoonotic nature of CV gastroenteritis.Based on results of in vitro binding assays, volunteer challenge studies, and the analysis of NoV outbreaks, it was proposed that histo-blood group antigens (HBGA), including the ABO, Lewis, and secretor-type HBGAs, function as the NoV receptors (17, 19, 20, 27, 32). The involvement of other host factors in NoV replication and susceptibility to infection also has been implicated (14, 43).Previously, we reported the isolation and characterization of a novel CV (Tulane virus; TV) from stool samples of juvenile rhesus macaques (11). TV represents a newly proposed genus (Recovirus) within Caliciviridae that phylogenetically shares a common origin with NoVs; however, TV can be grown in tissue culture (11). We also reported a high prevalence of anti-NoV, anti-SaV binding, and anti-TV-neutralizing (VN) antibodies in colony macaques, suggesting that CV infections are frequent in captive nonhuman primates (NHP) (10). The few NoV challenge studies conducted also suggest that NHPs are susceptible to NoV infection. Chimpanzees inoculated with the Norwalk virus developed seroresponses and virus shedding but without the manifestation of clinical disease (45). Subekti et al. reported the development of clinical illness characterized by diarrhea, dehydration, vomiting, and virus shedding in newborn pigtail macaques inoculated with the Toronto virus (40). In a study conducted by Rockx et al., one of the three rhesus macaques infected with Norwalk virus developed virus-specific IgM and IgG responses and shed the virus for 19 days postinoculation (38). To date, however, direct evidence of natural NoV or SaV infection in NHPs is missing. Moreover, the prevalence and genetic diversity of recoviruses have yet to be studied.In this study, we undertook the molecular detection and genetic analysis of CVs circulating in colony macaques and examined the role of HBGAs in recovirus infection.     

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.     

Divergent Evolution of Norovirus GII/4 by Genome Recombination from May 2006 to February 2009 in Japan

Norovirus GII/4 is a leading cause of acute viral gastroenteritis in humans. We examined here how the GII/4 virus evolves to generate and sustain new epidemics in humans, using 199 near-full-length GII/4 genome sequences and 11 genome segment clones from human stool specimens collected at 19 sites in Japan between May 2006 and February 2009. Phylogenetic studies demonstrated outbreaks of 7 monophyletic GII/4 subtypes, among which a single subtype, termed 2006b, had continually predominated. Phylogenetic-tree, bootscanning-plot, and informative-site analyses revealed that 4 of the 7 GII/4 subtypes were mosaics of recently prevalent GII/4 subtypes and 1 was made up of the GII/4 and GII/12 genotypes. Notably, single putative recombination breakpoints with the highest statistical significance were constantly located around the border of open reading frame 1 (ORF1) and ORF2 (P ≤ 0.000001), suggesting outgrowth of specific recombinant viruses in the outbreaks. The GII/4 subtypes had many unique amino acids at the time of their outbreaks, especially in the N-term, 3A-like, and capsid proteins. Unique amino acids in the capsids were preferentially positioned on the outer surface loops of the protruding P2 domain and more abundant in the dominant subtypes. These findings suggest that intersubtype genome recombination at the ORF1/2 boundary region is a common mechanism that realizes independent and concurrent changes on the virion surface and in viral replication proteins for the persistence of norovirus GII/4 in human populations.Norovirus (NoV) is a nonenveloped RNA virus that belongs to the family Caliciviridae and can cause acute gastroenteritis in humans. The NoV genome is a single-stranded, positive-sense, polyadenylated RNA that encodes three open reading frames, ORF1, ORF2, and ORF3 (68). ORF1 encodes a long polypeptide (∼200 kDa) that is cleaved in the cells by the viral proteinase (3C^pro) into six proteins (4). These proteins function in NoV replication in host cells (19). ORF2 encodes a viral capsid protein, VP1. The capsid gene evolved at a rate of 4.3 × 10⁻³ nucleotide substitutions/site/year (7), which is comparable to the substitution rates of the envelope and capsid genes of human immunodeficiency virus (30). The capsid protein of NoV consists of a shell (S) and two protruding (P) domains: P1 and P2 (47). The S domain is relatively conserved within the same genetic lineages of NoVs (38) and is responsible for the assembly of VP1 (6). The P1 subdomain is also relatively conserved (38) and has a role in enhancing the stability of virus particles (6). The P2 domain is positioned at the most exposed surface of the virus particle (47) and forms binding clefts for putative infection receptors, such as human histo-blood group antigens (HBGA) (8, 13, 14, 60). The P2 domain also contains epitopes for neutralizing antibodies (27, 33) and is consistently highly variable even within the same genetic lineage of NoVs (38). ORF3 encodes a VP2 protein that is suggested to be a minor structural component of virus particles (18) and to be responsible for the expression and stabilization of VP1 (5).Thus far, the NoVs found in nature are classified into five genogroups (GI to GV) and multiple genotypes on the basis of the phylogeny of capsid sequences (71). Among them, genogroup II genotype 4 (GII/4), which was present in humans in the mid-1970s (7), is now the leading cause of NoV-associated acute gastroenteritis in humans (54). The GII/4 is further subclassifiable into phylogenetically distinct subtypes (32, 38, 53). Notably, the emergence and spread of a new GII/4 subtype with multiple amino acid substitutions on the capsid surface are often associated with greater magnitudes of NoV epidemics (53, 54). In 2006 and 2007, a GII/4 subtype, termed 2006b, prevailed globally over preexisting GII/4 subtypes in association with increased numbers of nonbacterial acute gastroenteritis cases in many countries, including Japan (32, 38, 53). The 2006b subtype has multiple unique amino acid substitutions that occur most preferentially in the protruding subdomain of the capsid, the P2 subdomain (32, 38, 53). Together with information on human population immunity against NoV GII/4 subtypes (12, 32), it has been postulated that the accumulation of P2 mutations gives rise to antigenic drift and plays a key role in new epidemics of NoV GII/4 in humans (32, 38, 53).Genetic recombination is common in RNA viruses (67). In NoV, recombination was first suggested by the phylogenetic analysis of an NoV genome segment clone: a discordant branching order was noted with the trees of the 3D^pol and capsid coding regions (21). Subsequently, many studies have reported the phylogenetic discordance using sequences from various epidemic sites in different study periods (1, 10, 11, 16, 17, 22, 25, 40, 41, 44-46, 49, 51, 57, 63, 64, 66). These results suggest that genome recombination frequently occurs among distinct lineages of NoV variants in vivo. However, the studies were done primarily with direct sequencing data of the short genome portion, and information on the cloned genome segment or full-length genome sequences is very limited (21, 25). Therefore, we lack an overview of the structural and temporal dynamics of viral genomes during NoV epidemics, and it remains unclear whether NoV mosaicism plays a role in these events.To clarify these issues, we collected 199 near-full-length genome sequences of GII/4 from NoV outbreaks over three recent years in Japan, divided them into monophyletic subtypes, analyzed the temporal and geographical distribution of the subtypes, collected phylogenetic evidence for the viral genome mosaicism of the subtypes, identified putative recombination breakpoints in the genomes, and isolated mosaic genome segments from the stool specimens. We also performed computer-assisted sequence and structural analyses with the identified subtypes to address the relationship between the numbers of P2 domain mutations at the times of the outbreaks and the magnitudes of the epidemics. The obtained data suggest that intersubtype genome recombination at the ORF1/2 boundary region is common in the new GII/4 outbreaks and promotes the effective acquisition of mutation sets of heterogeneous capsid surface and viral replication proteins.     

Bovine Norovirus: Carbohydrate Ligand,Environmental Contamination,and Potential Cross-Species Transmission via Oysters

Noroviruses (NoV) are major agents of acute gastroenteritis in humans and the primary pathogens of shellfish-related outbreaks. Previous studies showed that some human strains bind to oyster tissues through carbohydrate ligands that are similar to their human receptors. Thus, based on presentation of shared norovirus carbohydrate ligands, oysters could selectively concentrate animal strains with increased ability to overcome species barriers. In comparison with human GI and GII strains, bovine GIII NoV strains, although frequently detected in bovine feces and waters of two estuaries of Brittany, were seldom detected in oysters grown in these estuaries. Characterization of the carbohydrate ligand from a new GIII strain indicated recognition of the alpha-galactosidase (α-Gal) epitope not expressed by humans, similar to the GIII.2 Newbury2 strain. This ligand was not detectable on oyster tissues, suggesting that oysters may not be able to accumulate substantial amounts of GIII strains due to the lack of shared carbohydrate ligand and that they should be unable to contribute to select GIII strains with an increased ability to recognize humans.Environmental sources of animal pathogens and, most specifically, of RNA viruses may constitute substantial risk factors for cross-species transmission to humans (14). In this context, noroviruses (NoVs) infecting cattle could be of importance owing to the high densities of cows bred in areas of human activities. The ability of shellfish to concentrate pathogens released in seawater raises questions about the transmission of animal NoVs to humans through oyster consumption, but so far very few studies have compared water and shellfish contamination. One of the first such studies, conducted more than 30 years ago, comparing the presence of enterovirus by cell culture in water and oysters yielded about the same frequency of positive water (59%) and shellfish samples (35%) (12). More recently, phages of Bacteroides fragilis and Salmonella detected in sewage effluents were also detected in receiving waters and oysters (6). Human NoVs were detected in 75% of river water samples and in 60% of oyster beds (38). Only one study reported the detection of porcine norovirus in 15% of shellfish collected from the U.S. market but no information from the surrounding water was available (8).NoVs are small nonenveloped viruses approximately 30 nm in diameter with a positive-sense, single-stranded RNA genome. They belong to the Caliciviridae family, and in humans they are the most frequent cause of diarrhea outbreaks in all age groups (11, 28). They are classified in five genogroups, with human strains belonging to genogroups I, II, and IV, GIII strains infecting cattle, and murine strains classified in GV (45). Recently, two new genogroups (VI and VII) infecting animals have been proposed (29). Based on analysis of the open reading frame 2 (ORF2) sequence encoding the capsid protein, high diversity has been observed, with the result that genogroups have been subdivided into clusters, including up to 19 for GII strains. Porcine NoVs have been classified into three clusters of GII (GII.11, GII.18, and GII.19) while all bovine strains of NoV described so far belong to GIII (25, 29, 41, 45). The first bovine strain, Bo/Newbury2/1976/UK (NB2), was isolated in the United Kingdom from calves with diarrhea (43). Later, another distinct genotype of bovine NoV, Bo/Jena/1978/GER, was identified in Germany (21). These two strains represent the prototypes of the GIII.2 and GIII.1 genotypes, respectively.Although many gaps persist in our understanding of human NoV infections and pathogenesis, recent advances demonstrated a genetically determined host susceptibility based on histo-blood group antigen diversity. Various human NoV strains attach to distinct carbohydrates of the ABH and Lewis histo-blood group family, and evidence accumulated from volunteer studies and outbreaks indicates that binding to these carbohydrates is required for infection (19, 35). In addition, it was recently shown that the prototype bovine GIII.2 strain binds to a related carbohydrate structure which is absent from human tissues (44). Similarly, it was also demonstrated that some strains of either GI or GII specifically attach to oysters tissues through recognition of histo-blood group antigens (HBGAs) (17, 22, 36). This finding could help explain other observations, such as the rapid contamination of oysters, long persistence of viral particles, and, consequently, shellfish-borne outbreaks (3, 16). It additionally suggests that oysters may not merely act as passive filters randomly accumulating virus particles but, instead, may also act as selective filters specifically concentrating strains by recognition of carbohydrate epitopes shared with humans. As shellfish are grown in coastal waters frequently exposed to contamination from bovine in neighboring fields, they may be contaminated by these animal strains. This raises the issue of the potential role of oysters in the emergence of bovine NoVs into the human population.The aim of our study is to provide quantitative data on the presence of GIII NoV strains in comparison with GI and GII strains in bovine feces, rivers, or estuarine waters as well as shellfish from an area of both high cattle density and high-density oyster breeding. The possibility of GIII strain-specific binding to carbohydrate ligands of oyster tissues that may be shared with cows and humans is additionally examined. The results are discussed in the context of the environmental data in order to provide a first appreciation of the risk of GIII NoV transmission to humans through oyster consumption.     

Eukaryotic Viruses in Wastewater Samples from the United States

Human fecal matter contains a large number of viruses, and current bacterial indicators used for monitoring water quality do not correlate with the presence of pathogenic viruses. Adenoviruses and enteroviruses have often been used to identify fecal pollution in the environment; however, other viruses shed in fecal matter may more accurately detect fecal pollution. The purpose of this study was to develop a baseline understanding of the types of viruses found in raw sewage. PCR was used to detect adenoviruses, enteroviruses, hepatitis B viruses, herpesviruses, morbilliviruses, noroviruses, papillomaviruses, picobirnaviruses, reoviruses, and rotaviruses in raw sewage collected throughout the United States. Adenoviruses and picobirnaviruses were detected in 100% of raw sewage samples and 25% and 33% of final effluent samples, respectively. Enteroviruses and noroviruses were detected in 75% and 58% of raw sewage samples, respectively, and both viral groups were found in 8% of final effluent samples. This study showed that adenoviruses, enteroviruses, noroviruses, and picobirnaviruses are widespread in raw sewage. Since adenoviruses and picobirnaviruses were detected in 100% of raw sewage samples, they are potential markers of fecal contamination. Additionally, this research uncovered previously unknown sequence diversity in human picobirnaviruses. This baseline understanding of viruses in raw sewage will enable educated decisions to be made regarding the use of different viruses in water quality assessments.Millions of viruses and bacteria are excreted in human fecal matter (5, 17, 82), and current methods of sewage treatment do not always effectively remove these organisms (74, 76-78). The majority of treated wastewater, as well as untreated sewage, drains into the marine environment (1) and has the potential to threaten environmental (e.g., nutrients and chemicals) (45) and public (e.g., pathogen exposure via swimming and seafood consumption) (1, 24, 28, 29, 33, 44, 57, 63) health. Currently, the U.S. Environmental Protection Agency (EPA) mandates the use of bacterial indicators such as fecal coliforms and enterococci to assess water quality (75). Although monitoring of these bacteria is simple and inexpensive, it has been shown that fecal-associated bacteria are not ideal indicators of fecal pollution.Since fecal-associated bacteria are able to live in sediments in the absence of fecal pollution (18, 32, 55), their resuspension into the water column can result in false-positive results and mask correlations between their concentrations and the extent of recent fecal pollution. Another unfavorable characteristic of current bacterial indicators is their inability to predict or correlate with the presence of pathogenic viruses (25, 40, 41, 64, 80). Human-pathogenic viruses associated with feces are generally more robust than enteric bacteria and are not as easily eliminated by current methods of wastewater treatment (43, 80). For example, adenoviruses are more resilient to tertiary wastewater treatment and UV disinfection than are bacterial indicators of fecal pollution (74). Since bacterial indicators cannot accurately depict the risks to human health from fecal pollution, several studies have proposed the use of a viral indicator of wastewater contamination (35, 41, 61).While it is impractical to monitor the presence of all viral pathogens related to wastewater pollution, the development of an accurate viral indicator of sewage contamination is needed for enhanced water quality monitoring. Enteric viruses (including viruses belonging to the families Adenoviridae, Caliciviridae, Picornaviridae, and Reoviridae) are transmitted via the fecal-oral route and are known to be abundant in raw sewage. These viruses have been used to identify fecal pollution in coastal environments throughout the world (27, 35, 39, 40, 48, 50, 56, 57, 63, 64, 67-69, 71, 80). To determine which viruses are effective indicators of fecal pollution, it is first necessary to establish a broad, baseline understanding of the many diverse groups of eukaryotic viruses in raw sewage. Several studies have identified adenoviruses, noroviruses, reoviruses, rotaviruses, and other enteroviruses (e.g., polioviruses, coxsackie viruses, and echoviruses) in raw sewage in Australia, Europe, and South Africa (30, 47, 58, 76-78). However, no broad baseline data on the presence of eukaryotic viruses in raw sewage in the United States currently exist.This study determined the presence of 10 viral groups (adenoviruses, enteroviruses, hepatitis B viruses, herpesviruses, morbilliviruses, noroviruses, papillomaviruses, picobirnaviruses, reoviruses, and rotaviruses) in raw sewage samples collected throughout the United States. All viral groups that were detected in raw sewage were then examined further to determine if they were also present in final treated wastewater effluent. These 10 viral groups were chosen because of their potential to be transmitted via the fecal-oral route, suggesting that they might be found in raw sewage. Many of these viruses (excluding adenoviruses, enteroviruses, noroviruses, reoviruses, and rotaviruses) have not been studied in sewage despite their likely presence. Picobirnaviruses have been detected in individual fecal samples (12, 70, 79, 82); however, their presence has never been analyzed in collective waste, nor have they been proposed to be potential markers of fecal pollution. This study identified potential viral indicators of fecal pollution and will have important applications to water quality monitoring programs throughout the country.     

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.     

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 Ecology of Listeria monocytogenes: Evidence for a Reservoir in Milking Equipment on a Dairy Farm

A longitudinal study aimed to detect Listeria monocytogenes on a New York State dairy farm was conducted between February 2004 and July 2007. Fecal samples were collected every 6 months from all lactating cows. Approximately 20 environmental samples were obtained every 3 months. Bulk tank milk samples and in-line milk filter samples were obtained weekly. Samples from milking equipment and the milking parlor environment were obtained in May 2007. Fifty-one of 715 fecal samples (7.1%) and 22 of 303 environmental samples (7.3%) were positive for L. monocytogenes. A total of 73 of 108 in-line milk filter samples (67.6%) and 34 of 172 bulk tank milk samples (19.7%) were positive for L. monocytogenes. Listeria monocytogenes was isolated from 6 of 40 (15%) sampling sites in the milking parlor and milking equipment. In-line milk filter samples had a greater proportion of L. monocytogenes than did bulk tank milk samples (P < 0.05) and samples from other sources (P < 0.05). The proportion of L. monocytogenes-positive samples was greater among bulk tank milk samples than among fecal or environmental samples (P < 0.05). Analysis of 60 isolates by pulsed-field gel electrophoresis (PFGE) yielded 23 PFGE types after digestion with AscI and ApaI endonucleases. Three PFGE types of L. monocytogenes were repeatedly found in longitudinally collected samples from bulk tank milk and in-line milk filters.Listeria monocytogenes can cause listeriosis in humans. This illness, despite being underreported, is an important public health concern in the United States (23) and worldwide. According to provisional incidence data provided by the Centers for Disease Control and Prevention (CDC), 762 cases of listeriosis were reported in the United States in 2007. In previous years (2003 to 2006), the number of reported annual listeriosis cases in the United States ranged between 696 and 896 cases per year (5).Exposure to food-borne L. monocytogenes may cause fever, muscle aches, and gastroenteritis (30), but does not usually cause septicemic illness in healthy nonpregnant individuals (7, 30). Elderly and immunocompromised people, however, are susceptible to listeriosis (22, 10), and they may develop more-severe symptoms (10). Listeriosis in pregnant women may cause abortion (22, 30) or neonatal death (22).Dairy products have been identified as the source of several human listeriosis outbreaks (4, 7, 10, 22). Listeria is ubiquitous on dairy farms (26), and it has been isolated from cows'' feces, feed (3, 26), and milk (21, 35). In ruminants, L. monocytogenes infections may be asymptomatic or clinical. Clinical cases typically present with encephalitis and uterine infections, often resulting in abortion (26, 39). Both clinically infected and healthy animals have been reported to excrete L. monocytogenes in their feces (20), which could eventually cause contamination of the bulk tank milk or milk-processing premises (39).On-farm epidemiologic research provides science-based information to improve farming and management practices. The Regional Dairy Quality Management Alliance (RDQMA) launched a combined United States Department of Agriculture (USDA)-RDQMA pilot project in January 2004 to scientifically validate intervention strategies in support of recommended best management practices among northeast dairy farms. The primary goal of the project was to track dynamics of infectious microorganisms on well-characterized dairy farms. Target species included Salmonella spp. (6, 36, 37), Mycobacterium avium subsp. paratuberculosis (13, 24), and L. monocytogenes.The objectives of this study were to describe the presence of L. monocytogenes on a dairy farm over time and to perform molecular subtyping by pulsed-field gel electrophoresis (PFGE) on L. monocytogenes isolates obtained from bulk tank milk, milk filters, milking equipment, feces, and the environmental samples to identify diversity among L. monocytogenes strains, persistence, and potential sources of bulk tank milk contamination.     

Failure To Detect Helicobacter pylori DNA in Drinking and Environmental Water in Dhaka,Bangladesh, Using Highly Sensitive Real-Time PCR Assays

The main transmission pathway of Helicobacter pylori has not been determined, but several reports have described detection of H. pylori DNA in drinking and environmental water, suggesting that H. pylori may be waterborne. To address this possibility, we developed, tested, and optimized two complementary H. pylori-specific real-time PCR assays for quantification of H. pylori DNA in water. The minimum detection level of the assays including collection procedures and DNA extraction was shown to be approximately 250 H. pylori genomes per water sample. Using our assays, we then analyzed samples of drinking and environmental water (n = 75) and natural water biofilms (n = 21) from a high-endemicity area in Bangladesh. We could not identify H. pylori DNA in any of the samples, even though other pathogenic bacteria have been found previously in the same water samples by using the same methodology. A series of control experiments were performed to ensure that the negative results were not falsely caused by PCR inhibition, nonspecific assays, degradation of template DNA, or low detection sensitivity. Our results suggest that it is unlikely that the predominant transmission route of H. pylori in this area is waterborne.Helicobacter pylori is the most common human bacterial pathogen in the world (15), and it has been estimated that 50% of the world''s population is infected. The prevalence of H. pylori infection varies greatly worldwide, with infection rates of more than 80% in some developing countries and below 20% in some developed countries (29). H. pylori causes peptic ulcers in 10 to 15% and stomach cancer in another 1 to 2% of those infected (29).H. pylori naturally resides in the human stomach, and except for some primate species, no other host has been identified. Outside its host, H. pylori is fastidious and can grow only under microaerophilic conditions at 34 to 40°C in nutrient-rich media (29). Under suboptimal conditions, H. pylori transforms into nonculturable spherical or coccoid forms. To date, it is not clear if this process is reversible or if the coccoid form is infectious or even viable, but it has been reported to retain some metabolic activity, its genome, and an intact membrane (1, 6, 12, 28, 38, 47).Transmission of H. pylori has been proposed to occur via gastric-oral, oral-oral, or fecal-oral routes, with studies suggesting transmission through saliva and dental plaque (14, 23), normal and diarrheal stools (18, 23, 41, 43), and vomitus (30, 41). Infected mothers or older siblings, low standards of living, and crowded households have been shown to be major risk factors for contracting H. pylori (25, 35, 50). Other studies have shown a relation between infection, water sanitation, and drinking water sources (24, 26, 39), further supported by reports of H. pylori DNA in drinking, river, lake, or seawater (3, 7, 16, 19-22, 25, 33, 34, 37, 40, 43, 49).Since none of the latter group of studies have shown a causative relation between traces of H. pylori in water and new infections, our original aim was to perform a 2-year prospective study tracing H. pylori in water in a high-endemicity area and relate the findings with new infections in children. For this purpose, we developed highly sensitive and specific quantitative real-time PCR assays for detecting H. pylori DNA in water or human samples while allowing analysis of clonal relatedness between samples of different origins by sequencing of recovered DNA. Using these assays, we conducted a study in a slum area in Dhaka, Bangladesh, where we have recently shown a very high rate of H. pylori infections, i.e., that 60% of the children were infected by the age of 2 years (4). Drinking, waste, and environmental water samples and natural drinking water biofilm samples were collected and analyzed, with rigorous controls for falsely positive or negative results.     

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.     

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.     

Proteorhodopsin-Bearing Bacteria in Antarctic Sea Ice

Proteorhodopsins (PRs) are widespread bacterial integral membrane proteins that function as light-driven proton pumps. Antarctic sea ice supports a complex community of autotrophic algae, heterotrophic bacteria, viruses, and protists that are an important food source for higher trophic levels in ice-covered regions of the Southern Ocean. Here, we present the first report of PR-bearing bacteria, both dormant and active, in Antarctic sea ice from a series of sites in the Ross Sea using gene-specific primers. Positive PR sequences were generated from genomic DNA at all depths in sea ice, and these sequences aligned with the classes Alphaproteobacteria, Gammaproteobacteria, and Flavobacteria. The sequences showed some similarity to previously reported PR sequences, although most of the sequences were generally distinct. Positive PR sequences were also observed from cDNA reverse transcribed from RNA isolated from sea ice samples. This finding indicates that these sequences were generated from metabolically active cells and suggests that the PR gene is functional within sea ice. Both blue-absorbing and green-absorbing forms of PRs were detected, and only a limited number of blue-absorbing forms were found and were in the midsection of the sea ice profile in this study. Questions still remain regarding the protein''s ecological functions, and ultimately, field experiments will be needed to establish the ecological and functional role of PRs in the sea ice ecosystem.Proteorhodopsins (PRs) are retinal binding bacterial integral membrane proteins that function as light-driven proton pumps (9, 10) and belong to the microbial rhodopsin superfamily of proteins (54). Since the first reported PR sequence from members of SAR86 clade marine (class Gammaproteobacteria) in 2000 (9), many other PR-bearing bacteria have been identified in a range of marine habitats (5, 18, 20, 24, 25, 46, 62). In the recent Global Ocean Sampling (GOS) expedition, almost 4,000 PR sequences from 41 distinct surface marine environments were acquired, demonstrating that these PR genes are extremely abundant in the genomes of ocean bacterioplankton (46). In fact, PR-containing bacteria account for 13% of the community in the Mediterranean Sea and Red Sea and 70% of the community in the Sargasso Sea (18, 46, 49, 60). These light-harvesting bacteria are present in three major marine classes of bacteria: the Alphaproteobacteria, Gammaproteobacteria, and Flavobacteria. In addition, two distinct PR genes encode pigments with “blue-absorbing” and “green-absorbing” properties, which is achieved by a substitution at a single amino acid position, which thereby functions as a spectral tuning switch (10, 37, 48).Sea ice represents a complex physicochemical environment in polar regions and covers up to 13% of the Earth''s surface (59). Although extreme gradients of temperature, salinity, nutrient availability, and light stratify the ice matrix from the surface to the ice-water interface (41), the sea ice habitat nevertheless supports a diverse microbial community of phytoplankton, Bacteria, Archaea, viruses, and protists that grow in liquid brine channels within the ice (14, 35, 56). This sea ice microbial community (SIMCO) is highly metabolically active despite being unable to avoid the extreme environmental conditions that they experience (39). In fact, very-high-standing stocks of the SIMCO exist in many regions of the Southern Ocean. For example, the concentration of chlorophyll a, a proxy for microalgal biomass, typically reaches 200 mg m⁻² in the Ross Sea, while the concentration of chlorophyll a in the water column below is approximately 2 orders of magnitude less (47), and the percentage of metabolically active bacteria (32% [39]) is significantly higher than the 10% observed for temperate marine systems (36). The SIMCO is thus a major source of biomass in ice-covered regions of the Southern Ocean (59), providing a critical food source for grazing zooplankton (and, consequently, also for higher trophic levels) for much of the year (3, 59). This biomass is of particular importance during the darkness of the polar winter, where the bottom-ice community is the only available food source for juvenile krill. These grazers absolutely rely on the sea ice microbial community to survive, as the water lacks other food sources (6, 28).In the past decade, reports of the widespread occurrence of bacteriochlorophyll and PR pigments in planktonic marine bacteria have challenged the assumption that chlorophyll a is the only principal light-capturing pigment in ocean surface waters. These alternative pigments may in fact play a critical role in light energy harvesting for microbial metabolism in various aquatic ecosystems (5, 10, 25, 40, 49). It has been proposed that energy, rather than nutrient conservation, is important for the regulation of productivity (7). PR-containing phototrophic eubacteria could play a significant role in the energy budget of cells in the photic zone in marine environments (15). PR sequences have been detected in the Southern Ocean (9), but to our knowledge, there have been no reports of PR-bearing bacteria within the sea ice matrix.The majority of the microbial rhodopsin genes found in oceanic samples have been detected by environmental sequencing (30, 46, 48, 60). We have used degenerate PR gene primers (5) in this study to positively identify PR-bearing operational taxonomic units (OTUs) from sea ice. Also, specific bacterial mRNA can now be detected from extracted nucleic acids and used to examine gene expression and, thus, infer metabolic activity (8). With this in mind, we have generated cDNA from RNA extracted from sea ice samples. From these observations, we deduce that PR-bearing bacteria are present in sea ice and may be actively contributing to the ecosystem within this extreme microenvironment.     

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).     

Multiplex PCR for Detection of Botulinum Neurotoxin-Producing Clostridia in Clinical,Food, and Environmental Samples

Botulinum neurotoxin (BoNT), the most toxic substance known, is produced by the spore-forming bacterium Clostridium botulinum and, in rare cases, also by some strains of Clostridium butyricum and Clostridium baratii. The standard procedure for definitive detection of BoNT-producing clostridia is a culture method combined with neurotoxin detection using a standard mouse bioassay (SMB). The SMB is highly sensitive and specific, but it is expensive and time-consuming and there are ethical concerns due to use of laboratory animals. PCR provides a rapid alternative for initial screening for BoNT-producing clostridia. In this study, a previously described multiplex PCR assay was modified to detect all type A, B, E, and F neurotoxin genes in isolated strains and in clinical, food, environmental samples. This assay includes an internal amplification control. The effectiveness of the multiplex PCR method for detecting clostridia possessing type A, B, E, and F neurotoxin genes was evaluated by direct comparison with the SMB. This method showed 100% inclusivity and 100% exclusivity when 182 BoNT-producing clostridia and 21 other bacterial strains were used. The relative accuracy of the multiplex PCR and SMB was evaluated using 532 clinical, food, and environmental samples and was estimated to be 99.2%. The multiplex PCR was also used to investigate 110 freshly collected food and environmental samples, and 4 of the 110 samples (3.6%) were positive for BoNT-encoding genes.Botulinum neurotoxins (BoNTs) are the most toxic agents known, and as little as 30 ng neurotoxin is potentially lethal to humans (36). These toxins are responsible for botulism, a disease characterized by flaccid paralysis. Seven antigenically distinct BoNTs are known (types A to G), and BoNT types A, B, E, and F are the principal types associated with human botulism (37). Significant sequence diversity and antigenically variable subtypes have recently been reported for the type A, B, and E neurotoxin genes (14, 22, 23, 42).Apart from the species Clostridium botulinum, which itself consists of four phylogenetically distinct groups of organisms, some strains of other clostridia, namely Clostridium butyricum and Clostridium baratii, are also known to produce BoNTs (2, 4, 7, 13, 20, 26, 34, 44). Also, strains that produce two toxins and strains carrying silent toxin genes have been reported (8, 22, 24, 39). Due to the great physiological variation of the BoNT-producing clostridia, their isolation and identification cannot depend solely on biochemical characteristics (32). Indeed, the standard culture methods take into consideration only C. botulinum and not C. baratii and C. butyricum, and identification and confirmation require detection of BoNT by a standard mouse bioassay (SMB) (12). The SMB is highly sensitive and specific but also expensive, time-consuming, and undesirable because of the use of experimental animals. Detection of neurotoxin gene fragments by PCR is a rapid alternative method for detection and typing of BoNT-producing clostridia (3). Different PCR methods have been described for detecting neurotoxin type A-, B-, E-, and F-producing clostridia (9, 15-18, 21, 40, 41).A previously described multiplex PCR method able to simultaneously detect type A, B, E, and F neurotoxin genes is a useful tool for rapid detection of the BoNT-producing clostridia (31). While this method generally has a high level of inclusivity for detection of type B, E, and F neurotoxin genes, limitations for detection of the recently described subtype A2, A3, and A4 strains have been identified (6, 28). To increase the efficiency of this multiplex PCR method, new primers were designed to detect genes for all identified type A neurotoxin subtypes (19). Additionally, an internal amplification control (IAC) was added according to ISO 22174/2005. The specificity and selectivity of this multiplex PCR method were evaluated in comparison with an SMB (12) using target and nontarget strains, and the robustness was assessed using clinical, food, and environmental samples. Moreover, to evaluate the applicability of this multiplex PCR method, a survey with food and environmental samples was performed in a German food control laboratory.     

Continuous Presence of Noroviruses and Sapoviruses in Raw Sewage Reflects Infections among Inhabitants of Toyama,Japan (2006 to 2008)

Various genotypes of norovirus (NoV) (genogroup I genotype 1 [GI.1], -2, -4, -5, -8, -11, -12, and -14; GII.3, -4, -6, -7, -10, -13, -14, and -15), and sapovirus (SaV) (GI.1 and GI.2, GII.1, and GIV.1) were detected from raw sewage from April 2006 to March 2008, while limited numbers of genotypes of NoV (GI.8, GII.4, GII.6, and GII.13) and SaV (GII.3 and GIV.1) and of NoV (GII.4, GII.7, and GII.13) were detected from clinical cases and healthy children, respectively. During the winter 2006 to 2008, a large number of sporadic gastroenteritis outbreaks and many outbreaks caused by NoV GII.4 occurred among inhabitants in Toyama, Japan. The copy number of genomes of NoV GII detected from raw sewage changed in relation to the number of outbreaks. NoV strains of the same genotypes observed in both raw sewage and human specimens belonged to the same cluster by phylogenetic analysis and had almost identical nucleotide sequences among each genotype. These data suggest that NoVs and SaVs detected from raw sewage reflect the viruses circulating in the community, irrespective of symptoms, and that subclinical infections of NoV are common in Japan. Combined surveys of raw sewage with those of clinical cases help us to understand the relationship between infection of these viruses and gastroenteritis.Norovirus (NoV) and sapovirus (SaV), members of the Caliciviridae family, are considered to be a major cause of acute gastroenteritis in humans. Both NoV and SaV infect humans via the fecal-oral route and cause family or community-wide outbreaks, mainly in the winter season. NoVs are shed in feces at a level of 10⁵ to 10⁹ virus particles per gram during the symptomatic phase (32, 37), and viruses are continuously shed from patients after cessation of the symptoms (28, 37, 40). In addition, recent reports showed relatively high levels of shedding of the viruses from asymptomatic individuals (7, 8, 32, 37).NoVs and SaVs show high diversity in their genomes (5, 9). According to such a genetic diversity, they are classified into several genogroups (genogroup I [GI], GII, and GIV for human NoV and GI, GII, GIV, GV for human SaV) and further divided into many genotypes (NoV GI genotypes 1 to 14 [GI.1-14] and GII.1-17 and SaV GI.1-5, GII.1-6, GIV.1, and GV.1) (10, 17, 18). In 2006 to 2007, NoV GII.4 caused a large number of outbreaks of acute gastroenteritis worldwide (1, 11, 35, 43, 45). However, the other genotypes of NoV and SaV may infect humans asymptomatically and persist in the environment.Raw sewage could contain enteric viruses shed from affected people, and therefore, detectable viruses in raw sewage would reflect the actual state of the circulating viruses in the area. We previously reported that polioviruses in raw sewage and river water were isolated at the same time as oral vaccination in babies, and these isolates were derived from vaccine strains (13, 30). We also showed that the nucleotide sequences of echovirus type 13 isolated from river water were closely related to those from patients with aseptic meningitis during the outbreak in 2002 (14). For NoVs and SaVs, many epidemiological surveys have been conducted to determine the prevalence and virological properties of these viruses (42). Previous reports have shown that the nucleotide sequences of NoV strains from stools of outbreaks in nursing homes and from sewage were identical for an individual outbreak (26), and NoVs detected from gastroenteritis patients, domestic sewage, river water, and cultivated oysters in the area were related to each other (44). However, less is known about infection of the viruses with minor genotypes that are silently circulating in the population.In this study, we investigated NoVs and SaVs in raw sewage from 2006 to 2008 in Japan and compared the results with the viruses detected from clinical cases as well as healthy individuals to show the comprehensive prevalence of these viruses in the community.