International Journal of Microbiology

International Journal of Microbiology / 2010 / Article

Research Article | Open Access

Volume 2010 |Article ID 754368 |

Veronica Casas, Joseph Magbanua, Gerico Sobrepeña, Scott T. Kelley, Stanley R. Maloy, "Reservoir of Bacterial Exotoxin Genes in the Environment", International Journal of Microbiology, vol. 2010, Article ID 754368, 10 pages, 2010.

Reservoir of Bacterial Exotoxin Genes in the Environment

Academic Editor: Barbara H. Iglewski
Received25 Oct 2010
Accepted12 Dec 2010
Published09 Jan 2011


Many bacteria produce secreted virulence factors called exotoxins. Exotoxins are often encoded by mobile genetic elements, including bacteriophage (phage). Phage can transfer genetic information to the bacteria they infect. When a phage transfers virulence genes to an avirulent bacterium, the bacterium can acquire the ability to cause disease. It is important to understand the role played by the phage that carry these genes in the evolution of pathogens. This is the first report of an environmental reservoir of a bacterial exotoxin gene in an atypical host. Screening bacterial isolates from the environment via PCR identified an isolate with a DNA sequence >95% identical to the Staphylococcus aureus enterotoxin A gene (sea). 16S DNA sequence comparisons and growth studies identified the environmental isolate as a psychrophilic Pseudomonas spp. The results indicate that the sea gene is present in an alternative bacterial host, providing the first evidence for an environmental pool of exotoxin genes in bacteria.

1. Introduction

Exotoxins are secreted polypeptides produced by certain bacterial pathogens. Many exotoxin genes are carried on mobile genetic elements, including bacterial viruses (bacteriophage or phage). These virulence genes are responsible for many of the symptoms associated with the human disease [13]. As highly mobile genetic elements, phage can readily move between different environments, and are generally more resistant to environmental stress than their bacterial counterparts [411]. As a result, phage may survive in the environment in reservoirs not yet characterized. Living in these environmental reservoirs, the phage can influence evolution of the bacteria within these environments in several different manners. Horizontal gene transfer between the phage and the bacterium can result in the rapid evolution of new pathogens and may have serious implications in public health [12].

When a phage infects a bacterium, two alternative possibilities may result. One possibility is that the phage can replicate itself using phage and host factors, resulting in lysis of the bacterial host and release of new phage (the lytic lifestyle). Alternatively, the phage can integrate into the bacterial genome and the bacterial host can utilize certain genes the phage carries in its genome for its own benefit (the lysogenic lifestyle) [13]. If a phage encodes virulence genes, such as exotoxin genes, the phage could facilitate the transfer of these genes to nontoxigenic bacterial hosts, thereby increasing the exotoxin gene pool.

The toxins of Vibrio cholera (cholera toxin), Escherichia coli (shiga toxin), Corynebacterium diphtheria (diphtheria toxin), and Staphylococcus aureus (enterotoxin A) are encoded by phage [1417]. The Staphylococcus enterotoxin A (sea) gene carried by virulent strains of S. aureus is encoded by multiple phages, including ϕ11, ϕ12, ϕ13, 80α, and 42D [1821]. Other toxins are carried by phages isolated from S. aureus strains from animals, food, and the environment [20, 2231]. Given that multiple S. aureus toxins are encoded by phage, it is possible that multiple transduction events over time have resulted in the generation of the current virulent S. aureus strains. An environmental reservoir of toxin genes would provide novel virulence genes, and the genetic exchange between phage and novel bacterial hosts, could provide the mechanism for evolution of novel human pathogens.

To explore this hypothesis, we cultured environmental bacteria and screened them for a phage-encoded exotoxin gene. In this study, we describe the isolation of bacteria from environmental ambient air and the screening of the isolates for the phage-encoded sea gene using an exotoxin-specific colony PCR assay. One isolate was confirmed positive for the sea gene, and the sequence of the sea gene was determined. Using 16S rDNA PCR sequencing and comparison to the nonredundant GenBank nucleotide database, we determined that the environmental isolate was a novel host for the sea exotoxin. This is the first report of an alternative bacterial host from the environment that carries a phage-encoded exotoxin gene that is commonly associated with a different bacterial host.

2. Results

2.1. Cultivation and Exotoxin-Specific (sea) PCR Screening of Environmental Isolates

Bacterial isolates were cultivated from the ambient environment by exposing Luria Bertani (LB) plates to air and then incubated at room temperature for 48–72 hr. Eighty nine isolates were subcultured into sterile 96-well plates containing LB with 15% glycerol, and grown with aeration for 48–72 hr. Using colony PCR specific for the Staphylococcus enterotoxin A (sea) gene, each of the cultivated environmental isolates was screened for the presence of the sea gene. Of 89 isolates screened, one putative sea positive isolate was identified. The isolate was single colony purified, and the sea PCR was repeated on this purified isolate to confirm that the isolate (SEAB3C070426 lab-designated identification) was positive for the sea gene. The resulting sea-specific PCR product was gel-purified and sequenced.

2.2. Characterization of Environmental Isolate

The cultivated and purified environmental isolate (“SEAB3C070426”) was microbiologically characterized by Gram staining and microscopic evaluation. The environmental isolate was identified as a Gram negative rod. Furthermore, the purified isolate’s growth characteristics were evaluated against a S. aureus known to carry the sea exotoxin gene (S. aureus Food Research Institute 913 strain). The environmental isolate did not grow on S. aureus enrichment media at 35°C [32], but grew on LB at room temperature after 48–72 hr. In contrast, the S. aureus FRI913 control grew on both the enrichment media and LB at both temperatures.

To molecularly identify the cultivated environmental isolate carrying the sea sequence, 16S rDNA colony PCR was performed and the resulting PCR product was sequenced. The resulting 16S rDNA sequence was imported into the ARB bacterial 16S rDNA database to identify its nearest relatives for downstream phylogenetic analyses [33]. The 16S rDNA PCR product sequence grouped with Pseudomonas spp. using the ARB alignment. The nearest relatives identified by ARB were exported and used to generate a phylogenetic tree. The phylogenetic analyses of the ambient air isolate, its nearest relatives, and select outgroups (including S. aureus) were performed using the PAUP* program (Figure 1) [33]. The consensus tree generated from Maximum Likelihood (ML), Maximum Parsimony (MP), and Neighbor Joining (NJ) analyses grouped the ambient air isolate with Pseudomonas spp., not with S. aureus. The ML, MP, and NJ bootsrap values for the main branches of the consensus tree separating the ambient air isolate from S. aureus and grouping it with Pseudomonas spp. were ≥94. The GenBank Accession number of environmental isolate “SEAB3C070426” is FJ979636.

2.3. Characterization of the sea PCR Product

Sequencing of the sea PCR product obtained from the environmental isolate generated a 280 bp DNA sequence. The nucleotide composition of the amplified sequence was analyzed using BioEdit [34]. The sequence of the amplified PCR product contained a G + C content of 30% over 92 predicted amino acids. A ClustalW [35] alignment of the translated partial sequence of the sea-related gene with known sea genes is presented in Figure S1 in Supplemental Material available online at doi: A BLASTN alignment of the sequence against the nonredundant GenBank database confirmed that the amplified PCR product shared 95–96% nucleotide sequence identity with known sea genes. Most notably, the amplified PCR product was 96% similar to a known S. aureus phage, ϕNM3. A multiple alignment of the partial sequence of the sea-related gene and guide tree of the top BLASTN hits were produced using ClustalX2 [36] (Figures 2 and 3). BLASTN alignment of the sea-related gene against annotated S. aureus genomes from The SEED database was also performed [37]. This alignment indicated the sea-related gene was related to other S. aureus phage-associated enterotoxin genes (supplementary Figure S2). The sea-related gene was uploaded to the GenBank database and the Accession number is HQ698309.

3. Discussion

Transfer of exotoxin genes to new, as yet uncharacterized, bacterial hosts may facilitate the evolution of novel human pathogens. Many of the exotoxins produced by phage-encoded genes target key eukaryotic cellular processes such as protein synthesis [3843]. These phage encode the genes responsible for many of the symptoms associated with the human disease. Until recently, most epidemiological and ecological studies of infectious diseases have focused on the presence and activity of the bacteria per se, neglecting the potentially significant role of the phage that carry the exotoxin genes and their role in transmitting these virulence traits [4447].

Sequence analysis of several environmental metagenomes has shown that phage carrying exotoxin genes are common in the environment, however 16S rDNA analysis of metagenomes from the same environmental samples did not identify the cognate bacterial phage host [48]. A potential explanation of this finding is that phage in the environment may propagate in alternate bacterial hosts rather than those commonly associated with the human disease. The classic textbook description of phage-bacteria interactions implies that phage infection is limited to a specific host. However, as the ecology and physiology of phages has been further investigated, it is clear that some phage can infect multiple bacterial hosts [23, 4973]. Examples of phage that carry exotoxin genes and can infect alternative hosts include ctxϕ (infects both Vibrio cholerae and Vibrio mimicus [74]), stx-2 phage (infects E. coli and Enterobacter cloacae [75]), and Botulinum toxin E phage (infects Clostridium botulinum and Clostridium butyricum [76]).

The mechanisms phage have developed to allow infection of a range of hosts are varied. Phage T2 and phage Mu alter their tail fibers to allow infection of alternative hosts [77, 78]. Bordetella phage carry diversity generating retroelements that allow the phage to infect bacteria with different cell surface receptors and physiology [79]. Some phage can inactivate or recombine with endogenous lysogens to alter their host range [45, 80, 81]. Inter- and intraspecies examples of phage showing a larger infection range than previously believed have been demonstrated through experimentation with lab strains [52, 62, 65, 67, 71, 72, 8287].

Infection of alternative hosts in nature has also been demonstrated. Phage isolated from natural marine environments have been shown to subtly influence the composition of the bacterial community of those same environments [88]. Conversely, phage populations from various natural environments such as soil, lake water, and marine sediments have been shown to replicate when incubated with microbes from a different marine environment [6]. Comparison of the distribution of phage types in particular environments with the types of bacteria found in that same environment suggests that phage with quite broad host ranges must exist in nature [89]. Additionally, analyses of uncultured environmental phage libraries have revealed an abundance of mobile elements and genes involved in the mobilization of DNA [9092]. Altogether these results suggest that phage are capable of infecting different hosts in the environment, providing a major mechanism for the spread of genes between bacteria. Thus, phage may promote promiscuous horizontal gene transfer in nature.

This report provides the first direct evidence that alternative microbial hosts can carry exotoxin genes. The environmental isolate cultivated from outdoor ambient air was confirmed to carry the sea exotoxin gene by repeated exotoxin-specific PCR, and by sequencing and alignment of the sea-specific PCR product. The sea-specific PCR product was 95-96% identical at the nucleotide level to known sea genes in the GenBank nonredundant database.

When characterized microbiologically, the cultivated environmental isolate did not share the same characteristics as the control S. aureus FRI913 strain known to carry the sea gene. It did not grow on Staphylococcus enrichment media, nor did it share the same Gram staining properties as the S. aureus FRI913 strain (the environmental isolate was a Gram negative rod versus Staphylococcus which are Gram positive cocci). These results suggested that the sea gene was present in an alternative environmental host.

Further support for this conclusion was provided by sequencing of the 16S rDNA from the cultivated environmental isolate. Alignment of the 16S rDNA sequence from this isolate with the ARB database indicated the isolate was a Pseudomonas spp. and did not group with S. aureus. Moreover, phylogenetic analyses using PAUP* indicated that the isolate was related to Pseudomonas spp, not S. aureus. The ML, MP, and NJ bootstrap values of the main branches of the consensus tree that group the isolate with Pseudomonas spp. were ≥94, indicating high probability that these branches are robust. This provides robust statistical evidence that the isolate is a Pseudomonas spp. Further evidence supporting this identification of the ambient air isolate was its relatively high G + C content (52.36%) like many Pseudomonas spp., as compared to the low G + C content of S. aureus (32.8%).

We were unable to induce a sea positive phage by treatment from the environmental isolate via mitomycin C treatment [81]. There are at least two possible explanations why the environmental isolate was carrying the sea-related gene, but did not produce phage. First, generalized transduction could have transferred a region of bacterial chromosomal DNA containing the sea gene into the Pseudomonas spp. without integration of the phage itself [93]. Second, it is possible that the exotoxin was transferred via a phage, but the phage genes were subsequently mutated due to selection against harmful phage genes in the lysogen [94102].

Based on the examples from the literature and the data generated from this study, we propose the following model for transfer of phage-encoded exotoxin genes to a novel bacterium leading to the creation of a new human pathogen. A “free phage pool” (Figure 4) can potentially lead to new disease outbreaks in three ways: (i) transduction of exotoxin genes to an environmental bacterium that subsequently infects a human; (ii) transduction of exotoxin genes from the environmental reservoir to a bacterium in the normal human microbiota; (iii) transduction of a bacterium associated with a nonhuman animal, with subsequent infection of a human. In all three scenarios, once the phage is propagated within the alternate bacterial hosts it can lyse the host and re-enter the “free-phage pool” ready to transduce the exotoxin genes to other bacteria. In this manner, the genes are maintained in the environment independent of the bacterial host typically involved in the human disease.

The evidence that there is an environmental reservoir of exotoxin genes in bacteria that are not normally associated with human disease, suggests the possibility that novel diseases may evolve through horizontal transfer of virulence genes via transduction to new microbial hosts (Figure 4).

4. Materials and Methods

4.1. Sampling of Indoor and Outdoor Air

To collect bacterial air isolates, Luria Bertani (LB) agar plates containing 50 mg of cyclohexamide to prevent growth of fungi, were exposed to ambient air. These plates were then incubated at room temperature for 48–72 hr. All isolates that grew on the LB plates conditions were then subcultured into sterile 96-well plates containing LB and 15% glycerol. These subcultured isolates were grown, with aeration, at room temperature for 48–72 hr then stored at 4°C until screened by PCR.

4.2. PCR Assays and Sequencing

A colony PCR assay was used to initially screen for the Staphylococcus enterotoxin A (sea) gene. The sea-specific PCR primers amplified a 498 bp partial sequence within the coding region of the sea gene. The sea primers were (forward primer) 5′-GCAGGGAACAGCTTTAGGC-3′ and (reverse primer) 5′-GTTCTGTAGAAGTATGAAACACG-3′. To identify the bacterial isolate carrying the sea gene, a 16S rDNA PCR assay was used and the resulting PCR product sequenced. The primers used for the 16S rDNA PCR were (forward) 5′-AGAGTTTGATCMTGGCTCAG-3′ and (reverse) 5′-TACGGYTACCTTGTTACGACTT-3′. Five microliters of the subcultured isolates suspension was used as a template in the sea-specific PCR16S rDNA PCR. The PCR thermocycling conditions for the sea-specific PCR and 16S rDNA PCR were as described previously [103]. To control against possible PCR contamination of the environmental sample DNAs, all PCRs were performed in a completely separate room and different building with different air handling systems. The PCR products were run on a 1% agarose gel at 150 V. Sequencing of the sea-specific PCR and 16S rDNA PCR products was performed at the SDSU Microchemical Core Facility. To confirm the sea PCR product was the target gene, a BLASTN alignment of the PCR product was performed against the nonredundant GenBank database [104]. The top 12 hits were then aligned and a tree generated using ClustalX2 [36].

4.3. Microbiological Characterization of Environmental Isolate

The air isolate carrying the sea-like gene was characterized by plating onto Staph 110 media [105], a media that enriches for Staphylococcus aureus, and LB medium. The plates were incubated at room temperature and at 35°C. A Gram stain was also performed on the isolate identified as sea-positive by colony PCR.

4.4. Molecular Characterization of Environmental Isolate

Phylogenetic analyses were performed on the 16S rDNA PCR product sequence to molecularly identify the ambient air isolate. An alignment with the ARB 16S rDNA database was used to identify the nearest relatives to the ambient air isolate for use in creating a phylogenetic tree in PAUP* [33]. Maximum Likelihood (ML) was implemented in PAUP* to build the highest likelihood tree under an HKY85 model of sequence evolution with estimated nucleotide frequencies, shape parameter, and number of invariant sites. The heuristic search approach to find the best ML tree included 100 random addition sequence searches using TBR branch swapping. The ML bootstrap involved 100 replicates with 10 random addition sequences searches per replicate. The best Maximum Parsimony (MP) tree was found through a random addition sequence heuristic search strategy with 100 replicates. The maximum number of trees kept during each search was capped at 1000. MP bootstrap analyses were performed using searches on 100 bootstrap replicated datasets using the same heuristic search strategy except with 10, rather than 100, search replicates. The Neighbor-joining (NJ) bootstrap analysis was performed with 1000 replicates.


V. Casas was supported by an NIH/NIGMS Minority Biomedical Research Support Fellowship (5R25-GM8907). This work was supported in part by grant U54CA132384 from the National Cancer Institute. The authors thank Dr. Joan Chen and the SDSU Microchemical Core Facility for DNA sequencing.

Supplementary Materials

Supplemental Figure S1: ClustalW alignment of translated sea-related gene to known sea genes.

Supplemental Figure S2. Genome browser view of sea-related gene BLASTN alignment against annotated Staphylococcus aureus genomes from The SEED database.

  1. Supplementary Material


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