A biomarker for the identification of cattle fecal pollution in water using the LTIIa toxin gene from enterotoxigenic Escherichia coli

This research describes a method based on PCR to identify cattle fecal pollution in water using a portion of the heat labile toxin IIA (LTIIa) gene from enterotoxigenic Escherichia coli (ETEC). We describe the development of the primers and target. DNA extracts (221) from different animal fecal and human sewage samples were screened and showed no cross-reactivity. Minimum detection limits using centrifugation and filtration methods to concentrate E. coli seeded into stream, ocean, and secondary effluent waters were found to be at femtogram and attogram levels, respectively. Stability of the biomarker in stream, ocean, and secondary effluent waters was 2-4 weeks for all water types. Finally, 33 farm lagoon and waste samples were collected and 31 tested to validate the method; 93% were positive for the LTIIa trait when >1,000 E. coli were screened and 100% positive when >10(5) E. coli were screened. Prevalence of the toxin gene in the E. coli population affected the outcome of the analyses. The cow biomarker can be used in watershed studies to identify cattle waste with great accuracy if the appropriate numbers of E. coli are screened.     

Identifying Host Sources of Fecal Pollution: Diversity of Escherichia coli in Confined Dairy and Swine Production Systems

Repetitive extragenic palindromic PCR fingerprinting of Escherichia coli is one microbial source tracking approach for identifying the host source origin of fecal pollution in aquatic systems. The construction of robust known-source libraries is expensive and requires an informed sampling strategy. In many types of farming systems, waste is stored for several months before being released into the environment. In this study we analyzed, by means of repetitive extragenic palindromic PCR using the enterobacterial repetitive intergenic consensus primers and comparative analysis using the Bionumerics software, collections of E. coli obtained from a dairy farm and from a swine farm, both of which stored their waste as a slurry in holding tanks. In all fecal samples, obtained from either barns or holding tanks, the diversity of the E. coli populations was underrepresented by collections of 500 isolates. In both the dairy and the swine farms, the diversity of the E.coli community was greater in the manure holding tank than in the barn, when they were sampled on the same date. In both farms, a comparison of stored manure samples collected several months apart suggested that the community composition changed substantially in terms of the detected number, absolute identity, and relative abundance of genotypes. Comparison of E. coli populations obtained from 10 different locations in either holding tank suggested that spatial variability in the E. coli community should be accounted for when sampling. Overall, the diversity in E. coli populations in manure slurry storage facilities is significant and likely is problematic with respect to library construction for microbial source tracking applications.     

Distribution of ten antibiotic resistance genes in <Emphasis Type="Italic">E. coli</Emphasis> isolates from swine manure,lagoon effluent and soil collected from a lagoon waste application field

The prevalence of ten antibiotic resistance genes (ARGs) was evaluated in a total of 616 Escherichia coli isolates from swine manure, swine lagoon effluent, and from soils that received lagoon effluent on a commercial swine farm site in Sampson County, North Carolina (USA). Isolates with ARGs coding for streptomycin/spectinomycin (aadA/strA and strB), tetracycline (tetA and tetB), and sulfonamide (sul1) occurred most frequently (60.6–91.3%). The occurrence of E. coli isolates that carried aadA, tetA, tetB, and tetC genes was significantly more frequent in soil samples (34.0–97.2%) than in isolates from lagoon samples (20.9–90.6%). Furthermore, the frequency of isolates that contain genes coding for aadA and tetB was significantly greater in soil samples (82.6–97.2%) when compared to swine manure (16.8–86.1%). Isolates from the lagoon that carried tetA, tetC, and sul3 genes were significantly more prevalent during spring (63.3–96.7%) than during winter (13.1–67.8%). The prevalence of isolates from the lagoon that possessed the strA, strB, and sul1 resistance genes was significantly more frequent during the summer (90.0–100%) than during spring (66.6–80.0%). The data suggest that conditions in the lagoon, soil, and manure may have an impact on the occurrence of E. coli isolates with specific ARGs. Seasonal variables seem to impact the recovery isolates with ARGs; however, ARG distribution may be associated with mobile genetic elements or a reflection of the initial numbers of resistant isolates shed by the animals.     

Development of a Swine-Specific Fecal Pollution Marker Based on Host Differences in Methanogen mcrA Genes

The goal of this study was to evaluate methanogen diversity in animal hosts to develop a swine-specific archaeal molecular marker for fecal source tracking in surface waters. Phylogenetic analysis of swine mcrA sequences compared to mcrA sequences from the feces of five animals (cow, deer, sheep, horse, and chicken) and sewage showed four distinct swine clusters, with three swine-specific clades. From this analysis, six sequences were chosen for molecular marker development and initial testing. Only one mcrA sequence (P23-2) showed specificity for swine and therefore was used for environmental testing. PCR primers for the P23-2 clone mcrA sequence were developed and evaluated for swine specificity. The P23-2 primers amplified products in P23-2 plasmid DNA (100%), pig feces (84%), and swine waste lagoon surface water samples (100%) but did not amplify a product in 47 bacterial and archaeal stock cultures and 477 environmental bacterial isolates and sewage and water samples from a bovine waste lagoon and a polluted creek. Amplification was observed in only one sheep sample out of 260 human and nonswine animal fecal samples. Sequencing of PCR products from pig feces demonstrated 100% similarity to pig mcrA sequence from clone P23-2. The minimal amount of DNA required for the detection was 1 pg for P23-2 plasmid, 1 ng for pig feces, 50 ng for swine waste lagoon surface water, 1 ng for sow waste influent, and 10 ng for lagoon sludge samples. Lower detection limits of 10⁻⁶ g of wet pig feces in 500 ml of phosphate-buffered saline and 10⁻⁴ g of lagoon waste in estuarine water were established for the P23-2 marker. This study was the first to utilize methanogens for the development of a swine-specific fecal contamination marker.     

Distribution and Diversity of Escherichia coli Populations in the South Nation River Drainage Basin,Eastern Ontario,Canada

We investigated the prevalence and diversity of Escherichia coli strains isolated from surface waters from multiple watersheds within the South Nation River basin in eastern Ontario, Canada. The basin is composed of mixed but primarily agricultural land uses. From March 2004 to November 2007, a total of 2,004 surface water samples were collected from 24 sampling sites. E. coli densities ranged from undetectable to 1.64 × 10⁵ CFU 100 ml⁻¹ and were correlated with stream order and proximity to livestock production systems. The diversity of 21,307 E. coli isolates was characterized using repetitive extragenic palindromic PCR (rep-PCR), allowing for the identification of as many as 7,325 distinct genotypes, without capturing all of the diversity. The community was temporally and spatially dominated by a few dominant genotypes (clusters of more than 500 isolates) and several genotypes of intermediary abundance (clustering between 10 and 499 isolates). Simpson diversity indices, assessed on a normalized number of isolates per sample, ranged from 0.050 to 0.668. Simpson indices could be statistically discriminated on the basis of year and stream order, but land use, discharge, weather, and water physical-chemical properties were not statistically important discriminators. The detection of Campylobacter species was associated with statistically lower Simpson indices (greater diversity; P < 0.05). Waterborne E. coli isolates from genotypes of dominant and intermediary abundance were clustered with isolates obtained from fecal samples collected in the study area over the same period, and 90% of the isolates tested proved to share genotypes with fecal isolates. Overall, our data indicated that the densities and distribution of E. coli in these mixed-use watersheds were linked to stream order and livestock-based land uses. Waterborne E. coli populations that were distinct from fecal isolates were detected and, on this basis, were possibly naturalized E. coli strains.Escherichia coli is ubiquitously distributed in fecal material from humans and warm-blooded animals (38). The detection of E. coli in water is an implicit indicator of recent fecal contamination and therefore of the risk of cooccurrence of enteric pathogens that can cause illness in susceptible populations (62). Many jurisdictions evaluate and mandate compliance with drinking and recreational water quality standards on the basis of the presence and abundance of E. coli (14, 44). For example, Canadian recreational water quality standards stipulate that E. coli densities in excess of a geometric mean of 200 CFU per 100 ml indicate that the water is unsuitable for swimming and bathing (23).In a background of increasing occurrence of microbial contamination of surface water, a variety of methods for elucidating the sources of fecal contamination have been developed, and these microbial source tracking (MST) methods are recommended components of fecal pollution abatement strategies (16, 57). So-called library-dependent MST methods compare environmental isolates to collections of isolates obtained from likely sources of fecal pollution in the area of investigation. The host source is distinguished on the basis of the similarity of environmental isolates to reference fecal isolates. Comparison can be undertaken on the basis of genomic fingerprinting methods, including repetitive extragenic palindromic PCR (rep-PCR), ribotyping, or pulsed-field gel electrophoresis (PFGE) (13, 17, 31, 54, 57). A variety of studies using these methods have revealed enormous diversity in the fecal and environmental E. coli populations. For example, 461 distinct PFGE genotypes and 175 distinct enterobacterial repetitive intergenic consensus (ERIC)-PCR genotypes were detected in a collection of 555 E. coli strains isolated from river water in Texas (10). As many as 291 and 94 rep-PCR genotypes were distinguished in collections of 643 river isolates and 353 beach water E. coli isolates, respectively (43). Significant diversity was also revealed using multilocus enzyme electrophoresis (MLEE) and multilocus sequence typing (MLST) on 185 E. coli isolates from freshwater beaches, where an average of 40 alleles per locus were detected (59). Almost 60% of 657 E. coli isolates in a fecal reference collection had unique (i.e., detected in only one individual) fingerprints determined by rep-PCR (32). Extensive diversity of E. coli was also observed in soils in temperate climates, where the growth and persistence of “naturalized” populations without any known fecal input have been found (7, 28, 30). Naturalized populations have been dominated by the B1 phylogroup and may have adapted in ways that enhance their survival in temperate secondary habitats (59). The temporal and spatial diversity of E. coli may not be a significant factor in coarse-source (e.g., human versus animal) classification of E. coli by means of ribotyping procedures (48). Ultimately, the characterization and understanding of the diversity of populations of selected microorganisms in surface watercourses affected by multiple sources of fecal pollution (as in agricultural watershed settings, for example) may be more critical for assessing the specific impacts of contamination-mitigating measures than previously thought. For instance, restricting the access of cattle on pasture to adjacent water by implementing vegetative buffering along watercourses creates habitat for varied wildlife, which then contribute to fecal pollution. In this context, the diversity in populations of indicator bacteria could be useful for better understanding how changes in landscape use influence fecal source inputs.As part of a research program evaluating the impact of agriculture on water quality and the efficacy of better agricultural management practices to mitigate agricultural pollution, we have conducted a multiyear study of the microbiological water quality for a suite of different-sized watersheds in the South Nation River basin in eastern Ontario, Canada (41, 46, 61). Land use in this river basin is mixed, consisting primarily of agricultural activities, light urban development, and interspersed wildlife habitat. Surface water systems in the study region differ widely in their contributing areas and therefore in their discharges (61).In the work undertaken here, we sought to determine the spatial and seasonal variability in the density and the structure of populations of E. coli in surface waters within the South Nation River basin. The specific objectives of the study were (i) to characterize the seasonal distribution and abundance of E. coli in different watershed settings within the river basin, (ii) to evaluate the spatial distribution of E. coli densities and diversity with respect to upstream land use activities, (iii) to use rep-PCR to elucidate the dominant E. coli genotypes and the diversity of E. coli populations and to explore linkages to pathogen presence, season, and environmental and land use variables, and (iv) using rep-PCR, to evaluate the concordance between waterborne isolates and fecal isolates obtained from within the study area. The study is distinguished by an intensive 4-year sampling of numerous (n = 24) sites that differed in their stream order and proximal land use activity; the number of E. coli isolates (≈21,000) included in the analysis; and the use of two distinct rep-PCR fingerprinting methods (ERIC and BOXA1R) to characterize the isolates. Furthermore, we used classification and Regression Tree (CART) analysis to evaluate relationships between the abundance and diversity of E. coli in water samples and environmental and land use variables.     

Development of a swine-specific fecal pollution marker based on host differences in methanogen mcrA genes

The goal of this study was to evaluate methanogen diversity in animal hosts to develop a swine-specific archaeal molecular marker for fecal source tracking in surface waters. Phylogenetic analysis of swine mcrA sequences compared to mcrA sequences from the feces of five animals (cow, deer, sheep, horse, and chicken) and sewage showed four distinct swine clusters, with three swine-specific clades. From this analysis, six sequences were chosen for molecular marker development and initial testing. Only one mcrA sequence (P23-2) showed specificity for swine and therefore was used for environmental testing. PCR primers for the P23-2 clone mcrA sequence were developed and evaluated for swine specificity. The P23-2 primers amplified products in P23-2 plasmid DNA (100%), pig feces (84%), and swine waste lagoon surface water samples (100%) but did not amplify a product in 47 bacterial and archaeal stock cultures and 477 environmental bacterial isolates and sewage and water samples from a bovine waste lagoon and a polluted creek. Amplification was observed in only one sheep sample out of 260 human and nonswine animal fecal samples. Sequencing of PCR products from pig feces demonstrated 100% similarity to pig mcrA sequence from clone P23-2. The minimal amount of DNA required for the detection was 1 pg for P23-2 plasmid, 1 ng for pig feces, 50 ng for swine waste lagoon surface water, 1 ng for sow waste influent, and 10 ng for lagoon sludge samples. Lower detection limits of 10(-6) g of wet pig feces in 500 ml of phosphate-buffered saline and 10(-4) g of lagoon waste in estuarine water were established for the P23-2 marker. This study was the first to utilize methanogens for the development of a swine-specific fecal contamination marker.     

Evaluation of Swine-Specific PCR Assays Used for Fecal Source Tracking and Analysis of Molecular Diversity of Swine-Specific “Bacteroidales” Populations

In this study, we evaluated the specificity, distribution, and sensitivity of Prevotella strain-based (PF163 and PigBac1) and methanogen-based (P23-2) PCR assays proposed to detect swine fecal pollution in environmental waters. The assays were tested against 222 fecal DNA extracts derived from target and nontarget animal hosts and against 34 groundwater and 15 surface water samples from five different sites. We also investigated the phylogenetic diversity of 1,340 “Bacteroidales” 16S rRNA gene sequences derived from swine feces, swine waste lagoons, swine manure pits, and waters adjacent to swine operations. Most swine fecal samples were positive for the host-specific Prevotella-based PCR assays (80 to 87%), while fewer were positive with the methanogen-targeted PCR assay (53%). Similarly, the Prevotella markers were detected more frequently than the methanogen-targeted assay markers in waters historically impacted with swine fecal contamination. However, the PF163 PCR assay cross-reacted with 23% of nontarget fecal DNA extracts, although Bayesian statistics suggested that it yielded the highest probability of detecting pig fecal contamination in a given water sample. Phylogenetic analyses revealed previously unknown swine-associated clades comprised of clones from geographically diverse swine sources and from water samples adjacent to swine operations that are not targeted by the Prevotella assays. While deeper sequencing coverage might be necessary to better understand the molecular diversity of fecal Bacteroidales species, results of sequence analyses supported the presence of swine fecal pollution in the studied watersheds. Overall, due to nontarget cross amplification and poor geographic stability of currently available host-specific PCR assays, development of additional assays is necessary to accurately detect sources of swine fecal pollution.The size of swine farming operations has increased significantly during the last few decades as a result of the high demand for pork products. In fact, pork is now considered the most popular meat worldwide (15). In the United States, the number of large confined swine animal units increased by 3 orders of magnitude from 1982 to 1997 (18), making the swine industry among the top three producers of domesticated animal feces. A direct consequence of this trend is the increase in swine fecal waste, which in turn has raised environmental concerns. When introduced to water, swine fecal waste can present a risk to human health because this waste can harbor a variety of human pathogens (5, 13, 15, 21, 36). The diversity and relatively high frequency of human pathogens in swine feces make swine important reservoirs of zoonotic pathogens. Moreover, the marked increase in the number of large operations has resulted in increased manure production and application in small geographic areas, creating an imbalance between the assimilative capacity of manure-treated farmland and the amount of manure nutrients produced on each farm. This imbalance is evidenced by the 20% increase (from 1982 to 1997) in nitrogen and phosphorus produced in swine operations, thus potentially contributing to the detrimental eutrophication of aquatic ecosystems (18). Swine manure spills and leaks are commonplace in the top hog production states, such as Iowa and North Carolina, due to failure or overflow of manure storage, uncontrolled runoff from open feedlots, improper manure application on cropland, deliberate pumping of manure onto the ground, and intentional breaches in storage lagoons (28, 37).Recently, swine-associated PCR-based methods targeting members of the “Bacteroidales” order (i.e., Prevotella species) and methanogen populations (12, 29, 35) have been proposed to discriminate swine fecal pollution events from other potential fecal contributions (i.e., human, bovine, and wildlife) to environmental waters. Nevertheless, the value of these assays in reliably detecting fecal pollution sources in watershed-based studies has not been thoroughly investigated. The main goals of this study were to determine host specificity, frequency of detection, and detection limits of currently available swine-associated PCR-based, microbial source tracking assays. To achieve these objectives, assays were tested against swine and nontarget fecal samples, samples from swine manure pits and swine waste lagoons, and water samples presumed to be impacted by swine fecal sources. Furthermore, we investigated the phylogenetic diversity of Bacteroidales 16S rRNA gene sequences derived from some of the aforementioned samples to resolve the level of specificity, relative abundance, and environmental occurrence of Bacteroidales-specific 16S rRNA gene sequences.     

Occurrence of Genes Associated with Enterotoxigenic and Enterohemorrhagic Escherichia coli in Agricultural Waste Lagoons

The prevalence among all Escherichia coli bacteria of the LTIIa toxin gene and STII toxin gene, both associated with enterotoxigenic E. coli, and of three genes (stxI, stxII, and eaeA) associated with enterohemorrhagic E. coli was determined in farm waste disposal systems seasonally for 1 year. Single- and nested-PCR results for the number of E. coli isolates carrying each toxin gene trait were compared with a five-replicate most-probable-number (MPN) method. The STII and LTIIa toxin genes were present continuously at all farms and downstream waters that were tested. Nested-MPN-PCR manifested sensitivity increased over that of single-MPN-PCR by a factor of 32 for LTIIa, 10 for STII, and 2 for the stxI, stxII, and eaeA genes. The geometric mean prevalence of each toxin gene within the E. coli community in waste disposal site waters after nested MPN-PCR was 1:8.5 E. coli isolates (1:8.5 E. coli) for the LTIIa toxin gene and 1:4 E. coli for the STII toxin gene. The geometric mean prevalence for the simultaneous occurrence of toxin genes stxI, stxII, and eaeA, was 1:182 E. coli. These findings based on total population analysis suggest that prevalence rates for these genes are higher than previously reported in studies based on surveys of single isolates. With a population-based approach, the frequency of each toxin gene at the corresponding disposal sites and the endemic nature of diseases on farms can be easily assessed, allowing farmers and public health officials to evaluate the risk of infection to animals or humans.     

Development and use of a multiplex PCR system for the rapid screening of heat labile toxin I, heat stable toxin II and shiga-like toxin I and II genes of Escherichia coli in water

Enterotoxigenic Escherichia coli (ETEC) may produce heat-labile toxin (LT) I and LTII and heat-stable toxin (ST) I and STII, while shiga toxin producing E. coli (STEC) strains, including enterohaemorrhagic E. coli (EHEC), may produce shiga-like toxin (SLT) I and/or SLTII. Both ETEC and STEC are pathogenic to humans, pigs and cattle. As contamination of environmental water by any of these pathogenic E. coli cells is possible, a multiplex polymerase chain reaction (PCR) system for the rapid screening of LTI, STII, and SLTI and SLTII genes of E. coli was developed. The PCR primers used were the SLTI and SLTII genes specific primers developed by the present authors and the LTI and STII genes specific primers reported by other laboratories. The detection specificity of this multiplex PCR system was confirmed by PCR assay of ETEC, STEC and other E. coli cells as well as non- E. coli bacteria. Its detection limit was 10²–10³ cfu each of the target cells per assay. When this multiplex PCR system was used for the rapid screening of LTI, STII ETEC and STEC in water samples such as tap, underground and lake waters, it was found that after the enrichment step, as few as 10⁰ cells 100 ml⁻¹ of the water sample could be detected. Therefore, this PCR system could be used for the rapid monitoring of ETEC and/or STEC cells contaminating water samples.     

Comparison of the in situ survival and activity ofKlebsiella pneumoniae andEscherichia coli in tropical marine environments

A near-shore coastal mangrove island receiving untreated sewage and a coastal cove receiving rum distillery effluent in Puerto Rico were examined for their ability to support survival and activity ofKlebsiella pneumoniae andEscherichia coli. Pure cultures of both bacteria were monitored for 96 hours in situ at both locations using membrane diffusion chambers.K. pneumoniae survived at all sites as measured by AODC and Coulter Counter direct counts. However, at the mangrove island less than 20% of theK. pneumoniae population was active (AODC) after the first 3 hours and less than 10% of this population was respiring (INT). In contrast, the coastal area which was receiving rum distillery effluent was able to maintain 40% of theK. pneumoniae population in an active state with 90% respiring. TheE. coli population declined by two orders of magnitude at the mangrove island, but remained unchanged at the rum distillery outfall. TheE. coli population had a higher proportion of active cells and respiring cells thanK. pneumoniae at all sites. At the rum distillery site, theE. coli population was remarkable in that 95% remained active and 99% were respiring. This study suggests that, when sufficient organic loading exists,E. coli, a nonsurvivor, can overcome the bactericidal effects of tropical marine waters.K. pneumoniae, a survivor, could survive under all conditions but could not maintain the activity or respiration that theE. coli population could, even when high organic loads were present. Morphological changes related to nutrient stress in the tropical marine environment were apparent inE. coli, but not inK. pneumoniae. Based on physiological activityE. coli is just as much a survivor asK. pneumoniae in tropical marine waters.     

Identification and Mutational Analysis of <Emphasis Type="Italic">Escherichia coli</Emphasis> Sorbitol-Enhanced Glucose-Repressed <Emphasis Type="Italic">srlA</Emphasis> Promoter Expressed in LB Medium by Using Homologous Recombination and One-Round PCR Products

Escherichia coli has been used for recombinant protein production for many years. However, no native E. coli promoters have been found for constitutive expression in LB medium. To obtain high-expression E. coli promoters active in LB medium, we inserted various promoter regions upstream of eEmRFP that encodes a red fluorescent protein. Among the selected promoters, only colonies of srlA promoter transformants turned red on LB plate. srlA is a gene that regulates sorbitol utilization. The addition of sorbitol enhanced eEmRFP expression but glucose and other sugars repressed, indicating that srlAp is a sorbitol-enhanced glucose-repressed promoter. To analyze the srlAp sequence, a novel site-directed mutagenesis method was developed. Since we demonstrated that homologous recombination in E. coli could occur between 12-bp sequences, 12-bp overlapping sequences were attached to the set of primers that were designed to produce a full-length plasmid, denoted “one-round PCR product.” Using this method, we identified that the srlA promoter region was 100 bp. Further, the sequence adjacent to the start codon was found to be essential for high expression, suggesting that the traditionally used restriction enzyme sites for cloning in the promoter region have hindered expression. The srlA-driven expression system and DNA manipulation with one-round PCR products are useful tools in E. coli genetic engineering.     

Evaluation of Selected Membrane Filtration and Most Probable Number Methods for the Enumeration of Faecal Coliforms,Escherichia coli and Enterococci in Environmental Waters

Selected methods recommended in national and international water quality guidelines were compared in tests on environmental waters with different levels of faecal pollution. The following methods yielded no statistically significant differences in counts of faecal coliforms and Escherichia coli in raw sewage, semi-treated effluent, polluted urban run-off and stored potable water: Membrane filtration (MF) using MFc Agar or Chromocult Coliform Agar containing X-glucuronide, or a miniaturised microtitre-plate Most Probable Number (MPN) assay using a liquid growth medium containing chromogenic 4-methyl-umbelliferyl--D-glucuronide. Significant differences were, however, found between the Chromocult and the other methods for unpolluted river water. Counts of faecal enterococci in raw sewage, semi-treated effluent and polluted urban run-off, obtained by the following methods did not differ significantly: MF using M-Enterococcus Agar, Bile-Esculin Agar or Enterococcus Selective Agar, or a microtitre-plate MPN method with a liquid growth medium containing chromogenic 4-methyl-umbelliferyl--D-glucoside. Significant differences were, however, found between the MPN and the other methods for unpolluted river water and stored potable water. MF using Chromocult Coliform Agar had useful benefits for the simultaneous enumeration of coliforms and E coli. However, in view of cost and practical considerations, MF using MFc Agar or M-Enterococcus Agar proved the methods of choice for respectively enumerating faecal coliforms and E coli, or faecal enterococci, in analyses for general water quality surveillance purposes.     

Estimation of Pig Fecal Contamination in a River Catchment by Real-Time PCR Using Two Pig-Specific Bacteroidales 16S rRNA Genetic Markers

The microbiological quality of coastal or river water can be affected by fecal contamination from human or animal sources. To discriminate pig fecal pollution from other pollution, a library-independent microbial source tracking method targeting Bacteroidales host-specific 16S rRNA gene markers by real-time PCR was designed. Two pig-specific Bacteroidales markers (Pig-1-Bac and Pig-2-Bac) were designed using 16S rRNA gene Bacteroidales clone libraries from pig feces and slurry. For these two pig markers, 98 to 100% sensitivity and 100% specificity were obtained when tested by TaqMan real-time PCR. A decrease in the concentrations of Pig-1-Bac and Pig-2-Bac markers was observed throughout the slurry treatment chain. The two newly designed pig-specific Bacteroidales markers, plus the human-specific (HF183) and ruminant-specific (BacR) Bacteroidales markers, were then applied to river water samples (n = 24) representing 14 different sites from the French Daoulas River catchment (Brittany, France). Pig-1-Bac and Pig-2-Bac were quantified in 25% and 62.5%, respectively, of samples collected around pig farms, with concentrations ranging from 3.6 to 4.1 log₁₀ copies per 100 ml of water. They were detected in water samples collected downstream from pig farms but never detected near cattle farms. HF183 was quantified in 90% of water samples collected downstream near Daoulas town, with concentrations ranging between 3.6 and 4.4 log₁₀ copies per 100 ml of water, and BacR in all water samples collected around cattle farms, with concentrations ranging between 4.6 and 6.0 log₁₀ copies per 100 ml of water. The results of this study highlight that pig fecal contamination was not as frequent as human or bovine fecal contamination and that fecal pollution generally came from multiple origins. The two pig-specific Bacteroidales markers can be applied to environmental water samples to detect pig fecal pollution.Human and animal fecal pollution of coastal environments affects shellfish and recreational water quality and safety, in addition to causing economic losses from the closure of shellfish harvesting areas and from bathing restrictions (13, 19, 33). Human feces are known to contain human-specific enteric pathogens (3, 18, 28), but animals can also be reservoirs for numerous enteric human pathogens, such as Escherichia coli O157:H17, Salmonella spp., Mycobacterium spp., or Listeria spp., that may persist in the soil or surface waters (6, 8, 22, 24). Among animals, pigs are known to carry human pathogens that are excreted with fecal wastes. There are approximately 125 million pigs in the European Union (EU) and 114 million in North America (12, 36, 48), generating an estimated 100 and 91 million tons of pig slurry per year, respectively (4). France, the third largest pig producer in the EU, with about 23,000 farms, generates 8 to 10 million tons of pig slurry per year. Brittany accounts for 56.1% of the total national pig production on only 6% (27,200 km²) of the French territory, though it has 40% (2,700 km) of the coastline. This production could contaminate the environment when tanks on farms overflow, when slurry or compost is spread onto soils, or to a lesser extent, when lagoon surface waters are used for irrigation (38, 47, 52).Fecal contamination in shellfish harvesting and bathing areas is currently evaluated by the detection and enumeration of culturable facultative-anaerobic bacteria, such as E. coli, enterococci, or fecal coliforms (11), in shellfish and bathing waters (European Directives 2006/113/CE and 2006/7/CE). Pigs are among the potential sources of E. coli inputs to the environment; a pig produces approximately 1 × 10⁷ E. coli bacteria per gram of feces, which corresponds to an E. coli flow rate per day that is 28 times higher than that for one human (16, 34, 55).E. coli is not a good indicator of fecal sources of pollution in water because of its presence in both human and animal feces; therefore, alternative fecal indicators must be used. Microbial source tracking methods (44) are being developed to discriminate between human and nonhuman sources of fecal contamination and to distinguish contamination from different animal species (17, 46, 54). Many of these methods are library dependent, requiring a large number of isolates to be cultured and tested, which is time consuming and labor intensive. For these reasons, library-independent methods are preferred for the detection of host-specific markers.The detection of host-specific Bacteroidales markers is a promising library-independent method and has been used for identifying contamination from human and bovine origins (25, 29, 39, 40, 45). In this study, we selected Bacteroidales 16S rRNA gene markers and real-time PCR to focus on fecal contamination from pigs. To date, only one pig-specific Bacteroidales 16S rRNA gene marker has been developed and used on water samples for the identification of pig fecal contamination by real-time PCR assay (SYBR green) (37). When this pig-specific Bacteroidales marker was tested on a small number of fecal samples (n = 16), it showed some cross-reaction with human and cow feces.The present study investigated pig fecal contamination in a French catchment, the Daoulas estuary (Brittany), which has commercial and recreational shellfish harvesting areas and which is potentially subject to fecal contamination. The aims of the present study were (i) to design new primers for the detection and quantification of pig-specific Bacteroidales 16S rRNA genes by TaqMan analysis; (ii) to validate the sensitivity and specificity of the new primers and TaqMan assay using target (feces, slurry, compost, and lagoon water samples) and nontarget (human and other animal sources) DNA, respectively; and (iii) to evaluate the TaqMan assay for proper detection and quantitative estimation of pig-associated fecal pollution. The study represents the first application of pig-specific Bacteroidales markers using a TaqMan assay in Europe and included a monitoring study of marker levels throughout the various stages of slurry treatment.     

Evaluation of Lactobacillus sobrius/L. amylovorus as a New Microbial Marker of Pig Manure

Based on a comparison of the dominant microbial populations in 17 pig manure samples and using a molecular typing method, we identified a species, Lactobacillus sobrius and Lactobacillus amylovorus (which now are considered a single species and are designated L. sobrius/amylovorus here), that was consistently found in manure. The aim of the present study was to confirm by real-time PCR the relevance of this species as a marker of pig fecal contamination. The specificity of L. sobrius/amylovorus was evaluated in human and animal DNA extracted from feces. The real-time PCR assay then was applied to water samples, including effluents from urban wastewater treatment plants, runoff water, and rivers. L. sobrius/amylovorus was consistently present in all samples of swine origin: 48 fecal samples, 18 from raw manure and 10 from biologically treated manure at mean concentrations of 7.2, 5.9, and 5.0 log₁₀ cells/g, respectively. The species was not detected in any of the other livestock feces (38 samples from cattle and 16 from sheep), in the 27 human fecal samples, or in the 13 effluent samples from urban wastewater treatment plants. Finally, L. sobrius/amylovorus was not detected in runoff water contaminated by cattle slurry, but it was quantified at concentrations ranging from 3.7 to 6.5 log₁₀ cells/100 ml in runoff water collected after pig manure was spread on soil. Among the stream water samples in which cultured Escherichia coli was detected, 23% tested positive for L. sobrius/amylovorus. The results of this study indicate that the quantification of L. sobrius/amylovorus using real-time PCR will be useful for identifying pig fecal contamination in surface waters.Pig manure may contain pathogenic microorganisms that are harmful to humans and animals (11). These pathogens, which include bacteria, viruses, and protozoans, can survive for several weeks during the storage of manure and in the soil after manure is spread on the land (30). As a consequence, the large amount of manure that is produced and applied on land in many agricultural areas may impact water quality. It contributes to non-point source pollution, which is due partially to runoff from manured soil, especially when manure is spread just before rainfall. It is difficult to determine the origin of diffuse pollution, as it cannot be traced to a specific spot. Fecal indicators (Escherichia coli, fecal coliforms, and enterococci), which are commonly used to quantify fecal pollution, are present in the intestinal tracts of both humans and warm-blooded animals and thus cannot be used to distinguish contamination by pig manure from other sources of pollution. For this reason, alternative microbial indicators have been proposed for the identification of specific pollution sources.During the past 10 years, a few library-independent methods have been developed for the identification of pig fecal contamination. They are based mostly on the PCR amplification of specific genes or sequences, such as the STII toxin gene from enterotoxigenic E. coli (16), the internal transcribed spacer (ITS) sequence from Bifidobacterium thermacidophilum subsp. porcinum (26), the 16S rRNA gene of Bacteroides-Prevotella (5, 27, 31), and the methyl coenzyme M reductase gene from a methanogenic Archaea member (41). However, some of these methods are only qualitative, like the detection of B. thermacidophilum subsp. porcinum or of the mcrA and STII toxin genes, and do not allow the level of contamination to be quantified. Furthermore, it is noteworthy that the archaeal mcrA gene was not detected in 16% of the pig feces analyzed (41), and that the presence of the STII toxin gene depends on the level of E. coli in the sample, which needs to be greater than 100 cells to avoid false positives (16). Okabe et al. (31) quantified a Bacteroides-Prevotella pig-specific marker (Pig-Bac2) in water samples using real-time PCR. However, this marker lacks specificity, as the Pig-Bac2 marker also was present in human and cow feces at a concentration of 7 and 8 log₁₀ copies per g, respectively (31). Only one pig-specific Bacteroidales 16S rRNA gene marker (Pig-2-Bac), which was developed recently by Mieszkin et al. (27) using real-time PCR, appears to be suitable to quantify pig fecal contamination. However, one limit of targeting the Bacteroidales group could be their strictly anaerobic metabolism, which may influence their persistence in well-oxygenated water. Savichtcheva et al. (36) thus have reported that oxygen has a negative effect on the survival rate of Bacteroides fragilis. We thus consider it important to study biomarkers that are less sensitive to oxygen in order to extend the choice of tools for tracking sources of pollution by manure. Moreover, in the case of the downgrading of bathing or shellfish areas, when health and economic risks are involved, it could be useful to combine multiple markers to identify the source of pollution with certainty.In the search for potential pig manure markers, we recently analyzed the dominant bacterial groups of 17 raw pig manure samples using 16S rRNA-targeted PCR and the CE-SSCP (capillary electrophoresis-single-strand conformation polymorphism) molecular typing method (26). Among the dominant bacterial groups (Bacteroidales, Bifidobacterium, Eubacterium-Clostridiaceae, and Bacillus-Streptococcus-Lactobacillus), we highlighted the presence of a microaerophilic species, Lactobacillus sobrius, which was isolated from piglet feces previously (19). Lactobacilli are known to establish a stable population in the intestinal tract of piglets soon after birth (28, 39) and to rapidly become a dominant population of their intestinal flora, at least in the first days after weaning (2, 14, 34). Their concentration in pig feces has been estimated at about 3 × 10⁸ bacteria/g (9). Because of their protective effect against diarrhea, some species of Lactobacillus, including L. sobrius, particularly have been studied (20, 35). Konstantinov et al. (21) therefore designed a primer pair that specifically amplifies a fragment of the L. sobrius genome using real-time PCR. Finally, Jakava-Viljanen et al. (13) recently demonstrated very high similarity between the L. sobrius and L. amylovorus type and reference strains and representative porcine isolates based on their 16S rRNA gene sequence analysis. According to these results, L. sobrius and L. amylovorus constitute a single species and consequently are referred to as L. sobrius/amylovorus in this paper.Given the abundance of L. sobrius/amylovorus in piglet feces (19, 37) and its systematic presence in raw manure (26), we tested this species as a new marker of pig fecal contamination. The aims of our study were (i) to confirm the specificity of L. sobrius/amylovorus to pig feces by analyzing five host groups (human, pig, cattle, poultry, and sheep), manure and by-products of manure treatment, runoff water, and urban wastewaters, and (ii) to estimate the suitability of this marker to identify pig fecal contamination found in surface waters. The concentrations of L. sobrius/amylovorus were estimated by real-time PCR using the primers designed by Konstantinov et al. (21). They were compared to the levels of E. coli, total lactobacilli, and, for river water samples, to the concentrations of the pig-specific Bacteroidales 16S rRNA genetic marker (Pig-2-Bac) developed by Mieszkin et al. (27).     

Enumeration and Characterization of Antimicrobial-Resistant Escherichia coli Bacteria in Effluent from Municipal,Hospital, and Secondary Treatment Facility Sources

We describe a modification of the most probable number (MPN) method for rapid enumeration of antimicrobial-resistant Escherichia coli bacteria in aqueous environmental samples. E. coli (total and antimicrobial-resistant) bacteria were enumerated in effluent samples from a hospital (n = 17) and municipal sewers upstream (n = 5) and downstream (n = 5) from the hospital, effluent samples from throughout the treatment process (n = 4), and treated effluent samples (n = 13). Effluent downstream from the hospital contained a higher proportion of antimicrobial-resistant E. coli than that upstream from the hospital. Wastewater treatment reduced the numbers of E. coli bacteria (total and antimicrobial resistant); however, antimicrobial-resistant E. coli was not eliminated, and E. coli resistant to cefotaxime (including extended-spectrum beta-lactamase [ESBL] producers), ciprofloxacin, and cefoxitin was present in treated effluent samples.The emergence and dissemination of antimicrobial resistance are well established as clinical problems that affect human and animal health. Escherichia coli is an important element of the flora of the human and animal intestine and a significant pathogen associated with gastrointestinal infection, urinary tract infections, and a variety of other extraintestinal infections (4). E. coli shed into the environment can survive for significant periods (7, 14, 23). Detection of E. coli in water and food is widely used as a microbiological indication of fecal contamination.Data on the significance of environmental contamination with antimicrobial-resistant E. coli for human health are limited. Previous reports have shown that antimicrobial-resistant strains of bacteria are present in various effluents, such as hospital effluent discharge (8, 10, 16, 21), inflow effluent to a wastewater treatment plant (WWTP) (15), and outflow-treated effluent from a wastewater treatment plant (2, 12, 13, 18, 27). A wastewater treatment plant treating effluent from hospitals may be associated with discharge of relatively high levels of antimicrobial-resistant E. coli compared with those of a plant treating municipal effluent that does not include hospital effluent discharge (22). There are few reports of quantitative data on antimicrobial-resistant E. coli bacteria in effluent, reflecting the lack of a convenient method for their enumeration (12, 15, 22). Previous methods available for the detection of antimicrobial-resistant E. coli in a water sample have generally involved the isolation of E. coli and the selection of some isolates for susceptibility testing. In such cases, the proportions of antimicrobial-resistant organisms are based only on those isolates selected and are therefore not representative of the entire population. By adding the antimicrobial agent of interest to the water sample before testing, we have adapted a commercial most probable number (MPN) method (the Colilert system) for enumerating the total number of E. coli isolates resistant to that agent in a sample.     

Differentiation of Fecal <Emphasis Type="Italic">Escherichia coli</Emphasis> from Human,Livestock, and Poultry Sources by rep-PCR DNA Fingerprinting on the Shellfish Culture Area of East China Sea

The rep-PCR DNA fingerprinting performed with REP, BOX A1R, and (GTG)₅ primers was investigated as a way to differentiate between human, livestock, and poultry sources of fecal pollution on the area of Xiangshan Bay, East China Sea. Of the three methods, the BOX-PCR DNA fingerprints analyzed by jack-knife algorithm were revealed high rate of correct classification (RCC) with 91.30, 80.39, 89.39, 86.14, 93.24, 87.72, and 89.28% of human, cattle, swine, chicken, duck, sheep, and goose E. coli isolates classified into the correct host source, respectively. The average rate of correct classification (ARCC) of REP-, BOX-, and (GTG)₅-PCR patterns was 79.88, 88.21, and 86.39%, respectively. Although the highest amount of bands in (GTG)₅-PCR fingerprints could be observed, the discriminatory efficacy of BOX-PCR was superior to both REP- and (GTG)₅-PCR. Moreover, the similarity of 459 isolates originated from shellfish and growing water was compared with fecal-obtained strains. The results showed that 92.4 and 96.2% E. coli strains isolated from midstream and downstream shellfish samples, respectively, had a ≥80% similarity with corresponding strains isolated from fecal samples. It was indicated that E. coli in feces could spread from human sewage or domestic farms to the surrounding shellfish culture water, and potentially affect the quality of shellfish. This work suggests that rep-PCR fingerprinting can be a promising genotypic tool applied in the shellfish growing water management on East China Sea for source identification of fecal pollution.     

Identification and Characterization of Heat-Stable Enterotoxin II-Producing Escherichia coli from Patients with Diarrhea

Stock strains of Eschericia coli isolated from patients with traveller's diarrhea were examined for production of heat-stable enterotoxin II (STII). Of 400 strains examined, 3 were found to produce STII. The nucleotide sequence of the STII gene of these human strains was shown to be identical to that of porcine strains. Cultured cells of these strains induced fluid accumulation in ligated mouse intestinal loops and the activity was neutralized by anti-STII antiserum. These results suggest that STII-produciing enterotoxigenic E. coli can cause human diarrhea.     

Occurrence and antimicrobial drug susceptibility patterns of commensal and diarrheagenic <Emphasis Type="Italic">Escherichia coli</Emphasis> in fecal microbiota from children with and without acute diarrhea

Acute diarrhea is a public health problem and an important cause of morbidity and mortality, especially in developing countries. The etiology is varied, and the diarrheagenic Escherichia coli pathotypes are among the most important. Our objectives were to determine the occurrence of commensal and diarrheagenic E. coli strains in fecal samples from children under five years old and their drug susceptibility patterns. E. coli were isolated from 141 fresh fecal samples; 84 were obtained from clinically injured donors with acute diarrhea (AD) and 57 from clinically healthy donors without diarrhea (WD). Presumptive phenotypic species identification was carried out and confirmed by amplification of specific 16S ribosomal RNA encoding DNA. Multiplex PCR was performed to characterize the diarrheagenic E. coli strains. Drug susceptibility patterns were determined by the disc-diffusion method. In total, 220 strains were recovered from the fecal specimens (61.8% from AD and 38.2% from WD). Diarrheagenic E. coli was identified at a rate of 36.8% (n=50) in diarrheic feces and 29.8% (n=25) in non-diarrheic feces. Enteroaggregative E. coli was the most frequently identified pathotype in the AD group (16.2%) and the only pathotype identified in the WD group (30.9%). Enteropathogenic E. coli was the second most isolated pathotype (10.3%), followed by Shiga toxin-producing E. coli (7.4%) and enterotoxigenic E. coli (2.9%). No enteroinvasive E. coli strains were recovered. The isolates showed high resistance rates against ampicillin, tetracycline, and sulfamethoxazole-trimethoprim. The most effective drugs were ceftazidime, ceftriaxone, imipenem and piperacillin-tazobactam, for which no resistance was observed. Differentiation between the diarrheagenic E. coli pathotypes is of great importance since they are involved in acute diarrheal diseases and may require specific antimicrobial chemotherapy. The high antimicrobial resistance observed in our study raises a broad discussion on the indiscriminate or improper use of antimicrobials, besides the risks of self-medication.     

Effects of Colistin and Bacteriocins Combinations on the In Vitro Growth of <Emphasis Type="Italic">Escherichia coli</Emphasis> Strains from Swine Origin

Escherichia coli strains from swine origin, either susceptible or resistant to colistin, were grown under planktonic and biofilm cultures. After which, they were treated with antibacterial agents including nisin and enterocin DD14 bacteriocins, colistin and their combinations. Importantly, the combination of colistin, enterocin DD14 and nisin eradicated the planktonic and biofilm cultures of E. coli CIP54127 and the E. coli strains with colistin-resistance phenotype such as E. coli 184 (mcr-1 ⁺) and E. coli 289 (mcr-1 ^?), suggesting therefore that bacteriocins from lactic acid bacteria could be used as agents with antibiotic augmentation capability.