Clostridium perfringens, one of the most common causes of food poisonings, can carry the enterotoxin gene, cpe, in its chromosome or on a plasmid. C. perfringens food poisonings are more frequently caused by the chromosomal cpe-carrying strains, while the plasmid-borne cpe-positive genotypes are more commonly found in the human feces and environmental samples. Different tolerance to food processing conditions by the plasmid-borne and chromosomal cpe-carrying strains has been reported, but the reservoirs and contamination routes of enterotoxin-producing C. perfringens remain unknown. A comparative genomic hybridization (CGH) analysis with a DNA microarray based on three C. perfringens type A genomes was conducted to shed light on the epidemiology of C. perfringens food poisonings caused by plasmid-borne and chromosomal cpe-carrying strains by comparing chromosomal and plasmid-borne cpe-positive and cpe-negative C. perfringens isolates from human, animal, environmental, and food samples. The chromosomal and plasmid-borne cpe-positive C. perfringens genotypes formed two distinct clusters. Variable genes were involved with myo-inositol, ethanolamine and cellobiose metabolism, suggesting a new epidemiological model for C. perfringens food poisonings. The CGH results were complemented with growth studies, which demonstrated different myo-inositol, ethanolamine, and cellobiose metabolism between the chromosomal and plasmid-borne cpe-carrying strains. These findings support a ubiquitous occurrence of the plasmid-borne cpe-positive strains and their adaptation to the mammalian intestine, whereas the chromosomal cpe-positive strains appear to have a narrow niche in environments containing degrading plant material. Thus the epidemiology of the food poisonings caused by two populations appears different, the plasmid-borne cpe-positive strains probably contaminating foods via humans and the chromosomal strains being connected to plant material.
Citation: Lahti P, Lindström M, Somervuo P, Heikinheimo A, Korkeala H (2012) Comparative Genomic Hybridization Analysis Shows Different Epidemiology of Chromosomal and Plasmid-Borne cpe-Carrying Clostridium perfringens Type A. PLoS ONE 7(10): e46162. doi:10.1371/journal.pone.0046162
Editor: Holger Bruggemann, Aarhus University, Denmark
Received: February 6, 2012; Accepted: August 30, 2012; Published: October 19, 2012
Copyright: © Lahti et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Funding: This work was supported by the Finnish Centre of Excellence in Microbial Food Safety Research of the Academy of Finland. The funder had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Enterotoxin gene-carrying (cpe-positive) Clostridium perfringens type A is one of the most common causes of food poisoning in the industrialized world, and the third leading cause of food poisoning in USA . Limited knowledge of the reservoirs and the contamination routes of cpe-positive C. perfringens complicates the prevention of C. perfringens food poisonings.
C. perfringens is an anaerobic ubiquitous spore-forming bacterium, frequently present in the normal intestinal microbiota of humans and animals. C. perfringens strains are classified into different types (A–E) based on their expression of alpha, beta, epsilon, and iota toxins . C. perfringens can cause several diseases in humans and animals due to the variety of toxins it produces.
Fewer than 5% of C. perfringens type A strains carry the enterotoxin gene cpe . The cpe can be located in the bacterial chromosome or on a large plasmid –. The chromosomal cpe is flanked by an insertion sequence (IS) element IS1470 (cpe-genotype IS1470) , whereas the plasmid-borne cpe is flanked by either the IS1470-like or IS1151 element (cpe-genotypes IS1470-like or IS1151) , . Until recently, only the chromosomal cpe-carrying strains were associated with food poisonings . This was explained by their better tolerance to heating, low temperatures, and preservatives than that of the plasmid-borne cpe-carrying strains , . However, also the plasmid-borne genotypes were found to cause food poisonings – and the cpe was carried on a plasmid in 25% of food poisoning outbreaks investigated in Finland and Germany .
Both chromosomal and plasmid-borne cpe-positive C. perfringens genotypes were found in retail meat products , , but the contamination route remains unknown. The contamination of meat by the intestinal contents of slaughtered animals has been suggested to serve as the main source of cpe-positive C. perfringens . However, no successful isolations of cpe-positive C. perfringens strains have been reported from healthy production animals –; thus, the role of animals as the main reservoir of cpe-positive C. perfringens has been questioned .
Humans are a rich reservoir for plasmid-borne cpe-carrying strains ,  and were thus suggested to introduce a contamination risk into foods through handling . However, only a few chromosomal strains were found in human feces . Plasmid-borne cpe-positive strains were also detected in soil and sediments , . For better prevention of C. perfringens food poisonings, the reservoirs of the cpe-positive C. perfringens strains and the potentially different epidemiology of C. perfringens type A food poisonings caused by the chromosomal and plasmid-borne cpe-carrying strains need to be elucidated.
Comparative genomic hybridization (CGH) with DNA microarrays was performed to shed light on the epidemiology of the chromosomal and plasmid-borne cpe-carrying and cpe-negative C. perfringens type A strains of food, human, or animal origin. The results of the CGH analysis were complemented with growth studies, which demonstrated different metabolism between the chromosomal and plasmid-borne cpe-carrying strains. The results suggest different epidemiology of the cpe-positive C. perfringens groups, which is relevant when designing prevention of C. perfringens food poisonings.
To assess genetic relatedness and possible metabolic differences between the chromosomal and plasmid-borne cpe-positive and cpe-negative C. perfringens strains, a DNA microarray was designed based on three sequenced Clostridium perfringens genomes ATCC13124, strain 13 and SM101. A wide collection of C. perfringens strains (n = 83) from food and feces associated with food poisonings, feces of healthy humans, feces of healthy production animals, soil and sludge, were studied (Table S1). The strains represented different cpe-positive genotypes and cpe-negative strains, the latter including the reference strains ATCC13124 and 13 which were used as positive controls. A two-color labeling system was used and the differently labeled DNA sample pairs to be hybridized into one of the eight subarrays on each array slide were randomly selected. Reproducibility of the hybridizations was controlled by hybridizing 20 samples in duplicate and the control strains in quadruplicate. The DNA samples of the reference strains 13 and ATCC 13124 hybridized 99.9% with their own gene probes. The putative metabolic differences suggested by the CGH analysis were further confirmed by metabolic tests using minimal growth medium. All strains tested grew in the minimal medium with glucose as the sole carbon source and failed to grow in minimal medium without any source of carbon, demonstrating that the medium supported the growth of C. perfringens.
The 54 cpe-positive C. perfringens type A strains formed two distinct clusters, one consisting of the chromosomal cpe-carrying genotypes and the other of the plasmid-borne cpe-carrying genotypes (Figure S1). The similarity between strains, based on Pearson's correlation on a scale from −1 to 1, was 0.85 in the chromosomal cpe group and 0.76 in the plasmid-borne cpe group. The similarity between the two groups of cpe-positive C. perfringens strains was 0.59 (Figure 1). When the 29 cpe-negative strains were included in the analysis, the chromosomal strains still clustered separately, and the plasmid-borne cpe-carrying strains and the cpe-negative strains were evenly distributed in the other cluster. The chromosomal cluster was homogeneous, whereas the cluster consisting of plasmid-borne cpe-carrying or plasmid-borne cpe-carrying and cpe-negative strains was more heterogeneous (Figure 1).
Figure 1. Chromosomal cpe-carrying C. perfringens strains clustered separately from the plasmid-borne cpe-carrying and cpe-negative strains.
The figure was constructed using the MEV software .doi:10.1371/journal.pone.0046162.g001
In general, the plasmid-borne cpe-carrying strains shared more CDSs (75,6%–87,4%) with the cpe-negative reference strains ATCC 13124 and 13 than with the chromosomal cpe-carrying reference strain SM101 (71,8%–84,4%) (Table 1). By contrast, the chromosomal cpe-positive C. perfringens strains shared more CDSs with the reference strain SM101 (86,2%-94,9%) than with the two other reference strains (63,8%–81,4%) (Table 1). Altogether 372 CDSs were exclusively present in the plasmid-borne cpe-positive strains, and 242 CDSs were exclusively present in the chromosomal cpe-carrying strains.
Table 1. Minimum and maximum percentage of CDSs in the three reference strains (SM101, ATCC13124, and 13) carried by chromosomal and plasmid-borne cpe-carrying and cpe-negative C. perfringens strains.doi:10.1371/journal.pone.0046162.t001
When the CDSs of the reference strains were divided into functional groups based on J. Craig Venter Institute Comprehensive Microbial Resource (CMR) annotations, the plasmid-borne cpe-positive strains carried more CDSs than chromosomal strains of all except two functional groups: transposable elements, and protein synthesis and electron transport (Table S2). Marked differences were present in the numbers of CDSs without specific annotation (Table S2).
The major differences between the chromosomal and plasmid-borne cpe-carrying strains were in the presence of the operons related to myo-inositole and ethanolamine utilization; a gene cluster encoding phosphotransferases and beta-glucanases, including laminarinase and cellobiose phosphotransferase; and a gene cluster encoding biotin synthesis.
All plasmid-borne cpe-carrying strains carried the myo-inositol operon, whereas all chromosomal cpe-positive strains lacked this operon (Figure 2, Table S4). Accordingly, all tested plasmid-borne cpe-positive C. perfringens strains and none of the tested chromosomal cpe-positive strains utilized myo-inositol (Table S3). In the reference strain ATCC13124, the myo-inositol operon is located in the chromosome and consists of 13 CDSs (locus CPF0079–CPF0092). iolR upstream of the cluster is predicted to encode a divergent regulator.
Figure 2. Genes differentiating the chromosomal cpe-carrying C. perfringens strains from the plasmid-borne cpe-carrying and cpe-negative strains.
The figure was constructed using the MEV software .doi:10.1371/journal.pone.0046162.g002
All the 21 chromosomal cpe-carrying strains lacked the operon predicted to encode ethanolamine utilization, whereas 23 of the 33 plasmid-borne cpe-carrying strains, including all strains representing genotype IS1151-cpe and ten of 20 strains representing genotype IS1470-like-cpe, had this operon (Figure 2, Table S4). Again, the result was verified by all tested plasmid-borne cpe-positive C. perfringens strains and none of the tested chromosomal cpe-positive strains utilizing myo-inositol (Table S3). The ethanolamine utilization operon is found in the genomes of the reference strains ATCC13124 and 13, and it contains 17 CDSs.
Nearly all (19 of 21) chromosomal cpe-carrying strains had a gene cluster predicted to encode cellobiose phosphotransferase, laminarinase, and beta-glucanases, whereas all plasmid-borne cpe-carrying strains lacked this gene cluster. In support of the CGH data, all the chromosomal cpe-positive strains tested utilized cellobiose as the only carbon source (Table S3). Of the 12 plasmid-borne cpe-positive strains that lacked this gene cluster, nine failed to grow in minimal medium with cellobiose as the sole carbon source, and three grew in the minimal medium with cellobiose despite lacking the gene cluster. The gene cluster predicted to encode phosphotransferases and beta-glucanases contains 11 CDSs and is located in the chromosome of the cpe-positive SM101 (locus CPR2599–CPR2609) (Figure 2, Table S4). Moreover, all chromosomal cpe-positive C. perfringens strains lacked a gene cluster containing nine CDSs, of which bioB and bioD encode biotin synthesis (locus CPF1787–1795 in ATCC 13124). All 83 strains carried bioY (CPF1796), predicted to encode biotin intake.
The genomic content of the cpe-negative strains resembled that of the the plasmid-borne cpe-gene carrying strains. All cpe-negative strains carried an operon for myo-inositol utilization, most (26 of 29) carried the operon encoding ethanolamine utilization, all carried the gene cluster encoding biotin synthesis, and all lacked the gene cluster encoding phosphotransferases and beta-glucanases.
The chromosomal and the plasmid-borne cpe-carrying C. perfringens type A strains differed in their gene composition and clustered separately in the CGH analysis. The microarray results were confirmed by functional metabolic studies. The main differences were related to genes involved in the utilization of myo-inositole, ethanolamine, and cellobiose, and the synthesis of biotin. Accordingly, different ability of the chromosomal and plasmid-borne cpe-positive strains to utilize myo-inositole, ethanolamine, and cellobiose as the only source of energy was demonstrated. This suggests that the chromosomal and plasmid-borne cpe-carrying C. perfringens strains are differently adapted to various environments, and thus, the epidemiology of C. perfringens food poisoning caused by the two strain populations may be different.
The plasmid-borne cpe-carrying and the cpe-negative strains formed a heterogeneous group, with some plasmid-borne cpe-carrying and cpe-negative strains being very similar. This supports horizontal transfer of the cpe plasmid between C. perfringens strains, as proposed in previous studies , , .
The chromosomal cpe-positive strains formed a homogeneous cluster, which is in agreement with an earlier study using multi-locus sequence typing . It seems plausible that the chromosomal cpe-positive strains have diverged from the remaining C. perfringens population, which is ubiquitous in nature and consists of a heterogeneous group of cpe-negative but also plasmid-borne cpe-carrying strains. Although the chromosomal cpe-carrying strains appear to better survive in certain extreme conditions , , the present results suggested that the plasmid-borne cpe-carrying and cpe-negative strains have specific properties by which they are better adapted to diverse environments than the chromosomal cpe-carrying strains.
The property of both the plasmid-borne cpe-positive and cpe-negative strains, utilizing myo-inositol, suggests that these strains are similarly adapted to multiple habitats. Apart from being abundant in the soil and environment, myo-inositol is a component of the eukaryotic cell wall and has been reported to be used by C. perfringens as an alternative carbon source in the absence of glucose . Several microorganisms inhabiting the soil can utilize myo-inositol . The absence of this operon in all chromosomal cpe-carrying strains may limit their ubiquitous occurrence considered typical for C. perfringens, which suggests that the chromosomal cpe-carrying strains have their own, an as-yet unidentified narrow niche in the environment.
Since ethanolamine is abundant in the human intestine , the presence of the operon encoding ethanolamine utilization in 70% of the plasmid-borne cpe-carrying strains and in 90% of the cpe-negative strains probably provides an advantage for survival and colonization of the intestine for these strains , . The clostridial ethanolamine operon resembles that of Enterobacteriacae , among which ethanolamine utilization is common. Due to their ability to utilize ethanolamine, the plasmid-borne cpe-carrying strains could be adapted to the intestinal environment, unlike the chromosomal cpe-carrying strains, that lacked the ethanolamine utilization operon.
Biotin is involved in the central pathways of cell metabolism, and bacteria unable to synthesize biotin need to acquire it from external sources . The lack of this gene cluster in the chromosomal cpe-positive strains may indicate that the habitat of these strains is rich in free biotin.
The ability of the chromosomal cpe-positive C. perfringens strains to utilize cellobiose obtained by enzymatic or acidic hydrolysis of cellulose and laminarin common in plant cell walls may indicate that these polysaccharides are available in the yet unknown habitat of the chromosomal cpe-positive strains. Despite lacking the gene cluster predicted to encode utilization of cellobiose, three plasmid-borne cpe-carrying strains utilized cellobiose, which may indicate that cellobiose utilization is encoded by multiple loci, not necessarily represented in our microarrays.
Based on the currently available genome sequences, we expect the cpe-positive C. perfringens strain population to contain hundreds of genes not present in the reference genomes and thus not represented on the microarrays. For example, majority of the 73 and 62 genes of the cpe-containing plasmids pCPF5603 and pCPF4969 , respectively, are specific to plasmids, since they share only 10 and 7 genes with SM101 according to BLAST. Therefore one should bear in mind that the differential gene pool observed in this study is likely to be larger and warrants future study.
The chromosomal cpe-carrying C. perfringens strains seem unable to utilize myo-inositol or ethanolamine or to synthesize biotin, which are important for soil and intestinal bacteria competing in complex environments. The majority of the chromosomal cpe-carrying strains in this study also lacked the fucose and sialidase encoding genes, which further diminishes the territory of the chromosomal cpe-positive strains . Presumably, the chromosomal cpe-positive strains are not ubiquitous and soil or intestines are not the habitat of these strains, although the chromosomal strains may compensate for some of the aforementioned deficiencies by producing toxins or by acquiring appropriate genes from the environment. This is supported by the presence of many IS-elements suggestive of gene transfer .
In light of our results, the habitat of the chromosomal cpe-carrying C. perfringens strains appears to be rich in biotin, and the ability to utilize cellobiose and laminarin may be beneficial. Cellobiose, laminarin, and biotin are available in environments where bacteria decompose plant material, such as composts. In composts, the temperature may be high, allowing only the most heat-tolerant strains, such as the chromosomal cpe-carrying strains, to survive. Access of the spores of chromosomal cpe-carrying C. perfringens to the food chain via the compost soil on the surface of vegetables should be investigated.
Other environments rich in biotin and cellobiose include sewage and sludge , where the chromosomal cpe-carrying C. perfringens strains may end up via the excretions of food-poisoning patients. The heat-resistant spores of the chromosomal cpe-positive strains could also tolerate heat treatments and drying , , which are usually included in the waste water treatment procedures. Thus, the role of sewage and sludge as a reservoir of chromosomal cpe-positive C. perfringens should be addressed, as the spores surviving the waste water treatment procedures may return to the food chain via sludge used as fertilizer.
In conclusion, the results suggest the plasmid-borne cpe-carrying strains and cpe-negative strains to be ubiquitous and adaptated to the mammalian intestine. By contrast, the chromosomal cpe-carrying strains appear to have a narrow niche in environments containing degrading plant material. Thus, the plasmid-borne cpe-carrying strains are proposed to contaminate foods by human due to poor hygiene, whereas the chromosomal cpe-carrying strains could spread to the food chain through ingredients of plant origin. Further research is needed to elucidate the habitat of these strains.
Materials and Methods
A total of 83 C. perfringens type A strains isolated from foods (n = 19) and feces (n = 9) associated with food poisonings, feces of healthy (n = 21) and ill (n = 6) people, feces of healthy production animals (pigs n = 7, cattle n = 5, broiler chickens n = 5), soil (n = 5), and sludge (n = 6) during 1986–2007 included 54 cpe-positive strains and 29 cpe-negative strains (Table S1). Of the cpe-positive strains, a chromosomal cpe was carried by 21 strains while 33 carried the cpe on a plasmid. Of the plasmid-borne cpe-carrying strains, 20 represented genotype IS1470-like and 13 represented genotype IS1151. The cpe-negative C. perfringens strains ATCC 13124 and 13, and the chromosomal cpe-positive strain SM101 were used as hybridization references. Genomic DNA of all strains was isolated as described by Keto-Timonen et al. (2005) .
The DNA microarrays, based on the genomes of C. perfringens type A strains 13 , ATCC13124, and SM101 , contained two 60-mer probes for all protein coding sequences (CDSs) annotated in the three genomes. The probes were designed using the OligoArray2.1 software . Upon the probe design, OligoArray2.1 software utilizes the BLAST algorithm for checking the specificity of a probe. There are 2170 conserved genes (core genome) in all the three reference genomes and over 2000 strain-specific genes or genes present only in two of the reference strains. First, probe design was done for each individual strain, and then the results were combined. Up to five candidate probes were designed for each CDS. Finally a maximum of two probes per CDS were selected, not accepting any duplicate probes. Moreover, four probes for each IS element (IS1469, IS1470, IS1470-like, and IS1151) , ,  were included for genotyping of cpe-positive C. perfringens. Each of the eight sub-arrays of Agilent 8*15K custom arrays (Agilent, Santa Clara, CA, USA) contained an equal set of 15 744 probes.
Hybridization and washes
A total of 0.5 mg of genomic DNA from each C. perfringens strain was fluorescently labeled using the BioPrime labeling kit (Invitrogen, Carlsbad, CA, USA). The 26-µl labeling reaction contained 11.5 µl of diluted DNA, 10 µl of random octamer primers (Invitrogen), 2.5 µl of 10× dCTP Nucleotide mix (Invitrogen), 1.5 µl of either Cy3 or Cy5-dCTP (GE Healthcare, Buckinghamshire, UK), and 0.5 µl of Exo-Klenow fragment solution (Invitrogen). The reactions were incubated at 37°C for 2 hours and stopped by adding 2.5 µl of stop buffer (EDTA, Invitrogen). For each hybridization, one Cy3-labeled and one Cy5-labeled DNA sample were combined; thus two samples were hybridized on each subarray and 16 samples on each array slide. The mixture was purified with a DNA purification kit (QIAquick PCR Purification Kit, Qiagen, Hilden, Germany) according to the manufacturer's instructions. The concentration of DNA and the incorporation of the dye were checked with the Nanodrop device (Nanodrop Technologies, Wilmington, MA, USA) before and after labeling. A volume of 2.2 µl salmon sperm DNA (1 mg/ml) was added to 17.8 µl of labeled combined sample solution, and the mixture was heated at 95°C for 2 minutes for denaturation. A volume of 5 µl of 10× blocking agent (Agilent) and 25 µl 2xGE (HI-RPI) hybridization buffer (Agilent) were added. A total of 45 µl of the solution was hybridized to each microarray at 65°C for 16 hours. The arrays were washed for 2×1 minute with Wash Buffer 1 (Agilent) and for 1 minute with Wash Buffer 2 (Agilent), pre-warmed to 37°C.
Scanning, image processing and data analysis
The slides were scanned (Axon GenePix Autoloader 4200 AL, Westburg, Leusden, The Netherlands) using 5 µm pixel resolution. Image processing was performed with the GenePix Pro 6.0 software. All hybridizations were normalized to the reference strains after background correction. Since the probes were designed based on three genomes, the location of the main mode of log2-ratio distribution was calculated between the hybridized strain and all reference strains, and the median value was used for normalization.
The distribution of logarithmic signal intensities formed two clear peaks in each hybridization. A threshold was set between the peaks based on replicated hybridizations of the two reference strains ATCC13124 and 13; signal intensities from the probes designed for the reference strain were above the threshold. The selected threshold divided the probes into two groups: The peak with greater values corresponded to probes with specific hybridization and genes predicted to be present, and the peak below the threshold corresponded to probes predicting a gene to be absent/divergent or yiedling unspecific hybridization and. The data analysis was done using the R software , and visualization and clustering were conducted using MEV . The data discussed in this publication are compliant with the MIAME guidelines and were deposited in NCBI's Gene Expression Omnibus and are accessible through GEO Series accession number GSE30954 (http://www.ncbi.nlm.nih.gov/geo/query/acc.cgi?acc=GSE30954).
To validate the DNA microarray results, the intensity of the IS element, plc (encoding the alpha toxin), and the cpe probe spots was compared with results of PCR assays showing the IS elements downstream of cpe , ,  and the presence of plc and cpe . The signal intensity values of all validated probe spots were in concordance with the PCR results.
Myo-inositol, cellobiose, and ethanolamine utilization of the cpe-positive C. perfringens strains
The minimal medium was prepared according to Sebald and Costilow (1975) . The growth of 10, 10, and 8 chromosomal, and 11, 12, and 7 plasmid-borne cpe-carrying C. perfringens strains was examined in the minimal medium using myo-inositol, cellobiose, and ethanolamine, respectively, as the sole source of energy. For controls, the growth of each strain was also examined in minimal medium with glucose and in a plain minimal medium. In brief, 25 µl of a 5×104 cfu/ml cell suspension of each strain was inoculated into 2.5 ml of fresh minimal medium containing 1% of either myo-inositol, cellobiose, or ethanolamine and incubated at 37°C overnight under anaerobic conditions. Growth in the presence of myo-inositol and cellobiose was studied in an automated turbidity reader (Bioscreen C Microbiology Reader, Growth Curves, Helsinki, Finland). To demonstrate ethanolamine utilization, 0.05% adenocylcobalamine, which is considered essential for ethanolamine consumption , was added to the media together with bromothymol blue as an indicator. Growth in the presence of ethanolamine was studied in 10-ml aliquots. A change of the indicator colour suggested ethanolamine utilization.
Similarity between the strains in the clusters of chromosomal and plasmid-borne cpe-carrying C. perfringens strains. The similarity between the chromosomal cpe-carrying strains is 0.85 (Pearson's correlation) The similarity between the plasmid-borne cpe-carrying strains (IS1470-like and IS1151) is 0.76, and the similarity between the two clusters is 0.59.
Characterization of Clostridium perfringens type A strains isolated from various sources.
Variable CDSs (probes) in chromosomal cpe-carrying C. perfringens strains related to plasmid-borne cpe-carrying strains.
Utilization of myo-inositole, ethanolamine, and cellobiose of chromosomal and plasmid-borne cpe-carrying C. perfringens strains.
The presence (+) and absence (−) of operons and gene clusters encoding the metabolic traits differentiating between the chromosomal and plasmid-borne cpe-carrying C. perfringens strains.
Conceived and designed the experiments: PL HK ML PS AH. Performed the experiments: PL PS. Analyzed the data: PL PS ML HK. Contributed reagents/materials/analysis tools: PL AH PS. Wrote the paper: PL ML HK.
- 1. Scallan E, Hoekstra RM, Angulo FJ, Tauxe RV, Widdowson MA, et al. (2011) Foodborne illness acquired in the united states–major pathogens. Emerg Infect Dis 17(1): 7–15. doi: 10.3201/eid1701.09-1101p1
- 2. Smedley JG 3rd, Fisher DJ, Sayeed S, Chakrabarti G, McClane BA (2004) The enteric toxins of Clostridium perfringens. Rev Physiol Biochem Pharmacol 152: 183–204. doi: 10.1007/s10254-004-0036-2
- 3. Kokai-Kun JF, Songer JG, Czeczulin JR, Chen F, McClane BA (1994) Comparison of western immunoblots and gene detection assays for identification of potentially enterotoxigenic isolates of Clostridium perfringens. J Clin Microbiol 32(10): 2533–2539.
- 4. Brynestad S, Synstad B, Granum PE (1997) The Clostridium perfringens enterotoxin gene is on a transposable element in type A human food poisoning strains. Microbiology 143(Pt 7): 2109–2115. doi: 10.1099/00221287-143-7-2109
- 5. Miyamoto K, Chakrabarti G, Morino Y, McClane BA (2002) Organization of the plasmid cpe locus in Clostridium perfringens type A isolates. Infect Immun 70(8): 4261–4272. doi: 10.1128/iai.70.8.4261-4272.2002
- 6. Cornillot E, Saint-Joanis B, Daube G, Katayama S, Granum PE, et al. (1995) The enterotoxin gene (cpe) of Clostridium perfringens can be chromosomal or plasmid-borne. Mol Microbiol 15(4): 639–647. doi: 10.1111/j.1365-2958.1995.tb02373.x
- 7. Sparks SG, Carman RJ, Sarker MR, McClane BA (2001) Genotyping of enterotoxigenic Clostridium perfringens fecal isolates associated with antibiotic-associated diarrhea and food poisoning in North America. J Clin Microbiol 39(3): 883–888 10.1128/JCM.39.3.883–888.2001. doi: 10.1128/jcm.39.3.883-888.2001
- 8. Li J, McClane BA (2006) Further comparison of temperature effects on growth and survival of Clostridium perfringens type A isolates carrying a chromosomal or plasmid-borne enterotoxin gene. Appl Environ Microbiol 72(7): 4561–4568. doi: 10.1128/aem.00177-06
- 9. Li J, McClane BA (2006) Comparative effects of osmotic, sodium nitrite-induced, and pH-induced stress on growth and survival of Clostridium perfringens type A isolates carrying chromosomal or plasmid-borne enterotoxin genes. Appl Environ Microbiol 72(12): 7620–7625. doi: 10.1128/aem.01911-06
- 10. Tanaka D, Kimata K, Shimizu M, Isobe J, Watahiki M, et al. (2007) Genotyping of Clostridium perfringens isolates collected from food poisoning outbreaks and healthy individuals in Japan based on the cpe locus. Jpn J Infect Dis 60(1): 68–69.
- 11. Grant KA, Kenyon S, Nwafor I, Plowman J, Ohai C, et al. (2008) The identification and characterization of Clostridium perfringens by real-time PCR, location of enterotoxin gene, and heat resistance. Foodborne Pathog Dis 5(5): 629–639. doi: 10.1089/fpd.2007.0066
- 12. Lahti P, Heikinheimo A, Johansson T, Korkeala H (2008) Clostridium perfringens type A strains carrying a plasmid-borne enterotoxin gene (genotype IS1151-cpe or IS1470-like-cpe) as a common cause of food poisoning. J Clin Microbiol 46(1): 371–373 10.1128/JCM.01650-07. doi: 10.1128/jcm.01650-07
- 13. Wen Q, McClane BA (2004) Detection of enterotoxigenic Clostridium perfringens type A isolates in American retail foods. Appl Environ Microbiol 70(5): 2685–2691. doi: 10.1128/aem.70.5.2685-2691.2004
- 14. Miki Y, Miyamoto K, Kaneko-Hirano I, Fujiuchi K, Akimoto S (2008) Prevalence and characterization of enterotoxin gene-carrying Clostridium perfringens isolates from retail meat products in Japan. Appl Environ Microbiol 74(17): 5366–5372. doi: 10.1128/aem.00783-08
- 15. Labbe R (2000) The microbial safety and quality of food. In: Anonymous Gaithersburg, Md, USA: Aspen Publishers. pp. 1110–1135.
- 16. Daube G, Simon P, Limbourg B, Manteca C, Mainil J, et al. (1996) Hybridization of 2,659 Clostridium perfringens isolates with gene probes for seven toxins (alpha, beta, epsilon, iota, theta, mu, and enterotoxin) and for sialidase. Am J Vet Res 57(4): 496–501.
- 17. Miwa N, Nishina T, Kubo S, Honda H (1997) Most probable numbers of enterotoxigenic Clostridium perfringens in intestinal contents of domestic livestock detected by nested PCR. J Vet Med Sci 59(7): 557–560. doi: 10.1292/jvms.59.557
- 18. Lindström M, Heikinheimo A, Lahti P, Korkeala H (2011) Novel insights into the epidemiology of Clostridium perfringens type A food poisoning. Food Microbiol 28(2): 192–198 10.1016/j.fm.2010.03.020. doi: 10.1016/j.fm.2010.03.020
- 19. Heikinheimo A, Lindström M, Granum PE, Korkeala H (2006) Humans as reservoir for enterotoxin gene–carrying Clostridium perfringens type A. Emerg Infect Dis 12(11): 1724–1729. doi: 10.3201/eid1211.060478
- 20. Carman RJ, Sayeed S, Li J, Genheimer CW, Hiltonsmith MF, et al. (2008) Clostridium perfringens toxin genotypes in the feces of healthy North Americans. Anaerobe 14(2): 102–108.
- 21. Li J, Sayeed S, McClane BA (2007) Prevalence of enterotoxigenic Clostridium perfringens isolates in Pittsburgh (Pennsylvania) area soils and home kitchens. Appl Environ Microbiol 73(22): 7218–7224. doi: 10.1128/aem.01075-07
- 22. Mueller-Spitz SR, Stewart LB, Klump JV, McLellan SL (2010) Freshwater suspended sediments and sewage are reservoirs for enterotoxin-positive Clostridium perfringens. Appl Environ Microbiol 76(16): 5556–5562 10.1128/AEM.01702-09. doi: 10.1128/aem.01702-09
- 23. Miyamoto K, Wen Q, McClane BA (2004) Multiplex PCR genotyping assay that distinguishes between isolates of Clostridium perfringens type A carrying a chromosomal enterotoxin gene (cpe) locus, a plasmid cpe locus with an IS1470-like sequence, or a plasmid cpe locus with an IS1151 sequence. J Clin Microbiol 42(4): 1552–1558. doi: 10.1128/jcm.42.4.1552-1558.2004
- 24. Brynestad S, Sarker MR, McClane BA, Granum PE, Rood JI (2001) Enterotoxin plasmid from Clostridium perfringens is conjugative. Infect Immun 69(5): 3483–3487 10.1128/IAI.69.5.3483-3487.2001. doi: 10.1128/iai.69.5.3483-3487.2001
- 25. Deguchi A, Miyamoto K, Kuwahara T, Miki Y, Kaneko I, et al. (2009) Genetic characterization of type A enterotoxigenic Clostridium perfringens strains. PLoS ONE 4(5): e5598. doi: 10.1371/journal.pone.0005598
- 26. Kawsar HI, Ohtani K, Okumura K, Hayashi H, Shimizu T (2004) Organization and transcriptional regulation of myo-inositol operon in Clostridium perfringens. FEMS Microbiol Lett 235(2): 289–295. doi: 10.1111/j.1574-6968.2004.tb09601.x
- 27. Roof DM, Roth JR (1988) Ethanolamine utilization in Salmonella typhimurium. J Bacteriol 170(9): 3855–3863.
- 28. Tsoy O, Ravcheev D, Mushegian A (2009) Comparative genomics of ethanolamine utilization. J Bacteriol 191(23): 7157–7164 10.1128/JB.00838-09. doi: 10.1128/jb.00838-09
- 29. Streit WR, Entcheva P (2003) Biotin in microbes, the genes involved in its biosynthesis, its biochemical role and perspectives for biotechnological production. Appl Microbiol Biotechnol 61(1): 21–31 10.1007/s00253-002-1186-2. doi: 10.1007/s00253-002-1186-2
- 30. Miyamoto K, Fisher J, Li J, Sayeed S, Akimoto S, et al. (2006) Complete sequencing and diversity analysis of the enterotoxin-encoding plasmids in Clostridium perfringens type A non-food-borne human gastrointestinal disease isolates. J Bacteriol 188(4): 1585–1598. doi: 10.1128/jb.188.4.1585-1598.2006
- 31. Myers GS, Rasko DA, Cheung JK, Ravel J, Seshadri R, et al. (2006) Skewed genomic variability in strains of the toxigenic bacterial pathogen, Clostridium perfringens. Genome Res 16(8): 1031–1040. doi: 10.1101/gr.5238106
- 32. Ho KL, Lee DJ (2011) Harvesting biohydrogen from cellobiose from sulfide or nitrite-containing wastewaters using Clostridium sp. R1. Bioresour Technol 102(18): 8547–8549 10.1016/j.biortech.2011.04.031. doi: 10.1016/j.biortech.2011.04.031
- 33. Keto-Timonen R, Nevas M, Korkeala H (2005) Efficient DNA fingerprinting of Clostridium botulinum types A, B, E, and F by amplified fragment length polymorphism analysis. Appl Environ Microbiol 71(3): 1148–1154 10.1128/AEM.71.3.1148-1154.2005. doi: 10.1128/aem.71.3.1148-1154.2005
- 34. Shimizu T, Ohtani K, Hirakawa H, Ohshima K, Yamashita A, et al. (2002) Complete genome sequence of Clostridium perfringens, an anaerobic flesh-eater. Proc Natl Acad Sci U S A 99(2): 996–1001 10.1073/pnas.022493799. doi: 10.1073/pnas.022493799
- 35. Rouillard JM, Zuker M, Gulari E (2003) OligoArray 2.0: Design of oligonucleotide probes for DNA microarrays using a thermodynamic approach. Nucleic Acids Res 31(12): 3057–3062. doi: 10.1093/nar/gkg426
- 36. R Development Core Team (2009) R: A Language and Environment for Statistical Computing. R Foundation for Statistical Computing, Vienna, Austria.
- 37. Saeed AI, Bhagabati NK, Braisted JC, Liang W, Sharov V, et al.. (2006) TM4 microarray software suite. In: Kimmel A, Oliver B, editors. Methods in Enzymology. San Diego, California, USA: Elsevier Academic Press. pp. 134–193.
- 38. Heikinheimo A, Korkeala H (2005) Multiplex PCR assay for toxinotyping Clostridium perfringens isolates obtained from Finnish broiler chickens. Lett Appl Microbiol 40(6): 407–411 10.1111/j.1472-765X.2005.01702.x. doi: 10.1111/j.1472-765x.2005.01702.x
- 39. Sebald M, Costilow RN (1975) Minimal growth requirements for Clostridium perfringens and isolation of auxotrophic mutants. Appl Microbiol 29(1): 1–6.