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South African Journal of Science

versión On-line ISSN 1996-7489
versión impresa ISSN 0038-2353

S. Afr. j. sci. vol.109 no.9-10 Pretoria ene. 2013




Impact of solar irradiation on cholera toxin secretion by different strains of Vibrio cholerae



Cornelius C. SsemakaluI; Le Roux WoulterII; Michael PillayIII

IDepartment of Chemistry, Vaal University of Technology, Vanderbijlpark, South Africa
IINatural Resources and the Environment, Council for Scientific and Industrial Research, Pretoria, South Africa
IIIDepartment of Biosciences, Vaal University of Technology, Vanderbijlpark, South Africa





Cholera toxin is the aetiological agent of cholera - a deadly waterborne disease acquired through the consumption of untreated water contaminated with CTXO bacteriophage harbouring strains of V. cholerae. Solar disinfection is a re-emerging technique that relies on the ultraviolet component of sunlight to inactivate the growth of Vibrio cholerae in water, rendering the water microbiologically safe for consumption. However, studies have shown that DNA damaging agents, such as ultraviolet light, induce the replication of the CTXO bacteriophage with subsequent expression of the cholera toxin. In this study we investigated the impact of solar irradiation on the secretion of cholera toxin by toxigenic strains of V. cholerae in water. The cholera toxin ELISA assay, qualitative and quantitative real-time PCR as well as growth on solid media were used to determine cholera toxin secretion, DNA integrity and growth of the bacteria after 7 h and 31 h of solar irradiation. Solar irradiation in water reduced the integrity of DNA, inactivated the growth of V. cholerae and, most importantly, prevented the secretion of detectable levels of cholera toxin. This finding is encouraging for resource-poor communities that may rely on solar disinfection to alleviate the burden of cholera-related fatalities.

Keywords: solar disinfection; SODIS; cholera; cholera toxin; Vibrio cholerae




Cholera is a life-threatening waterborne disease caused by Vibrio cholerae, a motile Gram-negative bacterium that is autochthonous in natural aquatic ecosystems.1 The disease is a constant threat and continues to ravage resource-poor communities around the world that lack adequate access to safe potable water and sanitation, with subsequent high fatality rates.2,3 Seven cholera pandemics have been reported worldwide; six were ascribed to the classical biotype of the 01 serogroup of V. cholerae while the most recent pandemic was attributed to the El Tor biotype of the same serogroup. Another serogroup of V. cholerae (0139) has been implicated in cholera outbreaks in some parts of Asia.4,5

It has been hypothesised that only V. cholerae serogroups 01 and 0139 are capable of causing cholera outbreaks. However, this notion is changing as some non-01/0139 strains of V. cholerae have been reported to harbour the CTXO bacteriophage genes6,7 providing them with the potential to cause cholera outbreaks. The CTXO bacteriophage contains the genes responsible for the production of the cholera toxin - the aetiological agent of cholera.8,9 Cholera toxin is a multi-subunit ADP-ribosylating toxin that binds to the GM1 ganglioside of the intestinal epithelial cells. The toxin is made up of the cholera toxin A subunit, which consists of a single unit, and cholera toxin B, which contains five units.10 The subunits are produced in the bacterial cytoplasm and are transported to the periplasm where they are folded and assembled into the 84-kDa heterohexameric AB5 toxin complex.11

The culturability of a variety of waterborne pathogens has been shown to be inhibited by solar radiation, specifically its ultraviolet component,12-14 thereby reducing the risk associated with the acquisition of deadly water-related infections.15,16 The mechanisms through which solar ultraviolet radiation (SUVR) inactivates the growth of water contaminating microorganisms are quite complex. The technological application of solar radiation to inactivate microorganisms in water has been termed solar disinfection (S0DIS). S0DIS treatment involves the exposure of water in transparent colourless vessels to direct sunlight for at least 7 h on clear sunny days or 2 days in cloudy weather.17,18 Ultraviolet(UV)-A, which is the more abundant, active component of solar radiation, has been reported to directly and indirectly target various vital microbial cell components and processes such as transcription and translation, transport systems, metabolism, chaperones and catalase (responsible for counteracting dangerous oxygen radicals), thereby inducing microbial cellular death.19,20 UVA has also been reported to cause single-strand breaks in DNA, and conditions that result in such damage have been shown to induce multiplication of CTXO and, simultaneously, increase the expression of ctxAB genes as a result of the S0S DNA repair response.21 The DNA repair response increases the repression of the LexA protein on the CTXO promoter (PstA) upstream of the ctxAB gene, through the protease activity of the RecA protein,21 thereby enabling its transcription. Even though the ctxAB gene has its own promoter (PcMB), reports have shown that it can be transcribed from CTXO PsstA. DNA damaging agents, such as mitomycin C and uV light, have been shown to induce multiplication of CTXO as well as the expression of CT.21,22 Sunlight contains a sufficient dose of UV light and can increase the bacteriophage titre, thereby enabling its transmission to potential recipient strains of V. cholerae.23 The transmission of CTXO is, however, dependent on its stability which relies on factors such as the viability of the bacteria, duration of UV exposure and environmental factors such as temperature, salinity and pH.23

In this study we investigated the potential for sunlight to induce the secretion of cholera toxin by toxigenic strains of V. cholerae by means of solar irradiating the microorganisms in water.


Material and methods

Vibrio cholerae strains and culture conditions

Seven strains of V. cholerae - six toxigenic and one non-toxigenic - were used in this study: NCTC 5941 and NCTC 12945 obtained from the national collection of type cultures; BRITS01 isolated from Brits, South Africa; G4222 isolated from a cholera patient in Gauteng, South Africa; ERWATA01 isolated at East Rand Water, Johannesburg, South Africa; ENV1009 isolated at Rand Water (Vereeniging) in South Africa; and UG01 isolated from groundwater in Katojo, Uganda. All strains were stored at -80 °C as bacterial stocks on beads. Each strain was cultured on nutrient agar plates by incubation at 37 °C for 18 h. From each isolate, 2-5 colonies were inoculated in Luria broth (LB, pH 8.5) and incubated at 37 °C on a rotary shaker at 200 rpm overnight until the stationary phase was reached. These cultures were used for (1) cholera toxin analysis by an enzyme-linked immunosorbent assay (ELISA), (2) semi-quantitative and qualitative real-time polymerase chain reaction (qRT-PCR) analysis and (3) solar exposures in water because of their resilience, as recommended by Berney et al.24

Preparation of Vibrio cholerae for solar exposure

Vibrio cholerae was harvested by centrifugation (at 3000 rpm for 10 min) from overnight stationary phase cultures of the batch cultures grown in LB. The pellet for each strain was washed three times with 1 x phosphate buffered saline (PBS, pH 7.5) to remove all traces of LB and the bacteria were diluted in commercially available still bottled water (Bonaqua, Pretoria, South Africa) to an optical density (OD600nm) of 0.1 that corresponded approximately to 11.5 colony forming units (CFU)/mL before SUVR exposure. The unusually high starting dose was used to increase the possibility of detecting the cholera toxin produced by the toxigenic strains of V. cholerae.

Exposure to natural solar radiation

The bacterial suspension (15 mL) was transferred into 25-cm3 transparent polystyrene unventilated tissue culture flasks. The flasks were exposed to natural sunlight by placing them horizontally on the roof of a building at an elevation of 1400 m in Pretoria, South Africa (25o44'50.40"S, 28o16'50.50"E). Control samples were prepared in a similar manner and placed next to the experimental ones but were protected from direct sunlight by being covered with an opaque ventilated cardboard box. The samples were exposed to SUVR during clear sunny days for either 7 h or 31 h. The 7-h exposure period was used because it is the optimal recommended time for SODIS and the 31-h period was used to assess for any further production of cholera toxin. Following exposures to SUVR, the samples were prepared for enumeration by the plate count method. Cholera toxin production was assayed using an ELISA and qRT-PCR analysis was used to assess the integrity of the DNA.

Enumeration of Vibrio cholerae

Bacterial samples exposed to SUVR were serially diluted in sterile 1 x PBS and plated on nutrient agar using the Miles and Misra drop count technique25 with slight modifications. Briefly, 10 uL of the appropriate dilution was dropped onto sterile nutrient agar plates in quadruplicate. The plates were incubated at 37 °C for 18-20 h. Plates with fewer than 50 discrete colonies per drop were selected for counting. The total count was divided by the number of drops, multiplied by 100 to convert to 1 mL, and then divided by the dilution factor to give the number of CFU/mL.14

Ganglioside GM1 cholera toxin ELISA assay

Materials used for the cholera toxin ELISA were: 96-well ELISA microplates (Greiner Bio-One, LASEC SA Centurion, South Africa); purified choleragenoid rabbit polyclonal IgG horseradish peroxidase (HRP) conjugated antibody (catalogue number PA1-73189) against the B subunit of the cholera toxin (BIOCOM Biotech, Thermo Scientific, Rockford, IL, USA); monosialoganglioside GM1 (G7641-1MG, Sigma, Johannesburg, South Africa) purchased as 1 mg of powder and dissolved in methanol to a final concentration of 1 mg/mL; wash buffer prepared by adding 0.05% Tween 20 to 1 x PBS; blocking buffer consisting of 1% bovine serum albumin (BSA) in wash buffer (1% BSA); and tetramethylbenzidine (TMB) substrate reagent (catalogue number 421101, BioLegend, BIOCOM Biotech, San Diego, CA, USA) prepared and used for colour development according to the manufacturer's instructions. All incubations were done at room temperature (23-25 °C). After each incubation period, the ELISA plate was emptied and washed three times with the wash buffer. To each well in the plate, 100 ng/mL of ganglioside GM1 in 1 x PBS was added and left overnight (about 15 h). The plate was then washed with wash buffer and blocking buffer was added. After 1 h, the plate was emptied, washed and then the supernatants from the solar-irradiated and non-irradiated samples were added. The cholera toxin B subunit and wash buffer were used as positive and negative controls, respectively. After 1.5 h of incubation, the plate was emptied, washed and the polyclonal rabbit HRP conjugated anti-cholera toxin B subunit antibody (1:1000 dilution in blocking buffer) was added and left for 1 h. The plate was emptied, washed and 100 uL of TMB substrate was added to each well. The plate was left at room temperature for 30 min before the stop solution consisting of 100 uL of 1M sulphuric acid was added to the wells. Within 10 min of adding the stop solution, the plate was read at an OD450nm in the BioTek Power Wave HT plate reader (BioTek, Winooski, VT, USA). Prior to reading of the plates, the minimum detection ability of the cholera toxin ELISA was determined by using seven tenfold dilutions (from a concentration of 1 000 000 pg/mL to 1 pg/mL) of the cholera toxin. These results were used to plot a standard curve. All assays were performed in duplicate.

Qualitative and quantitative real-time PCR analysis

Prior to DNA extraction, overnight bacterial cultures in LB were diluted to a uniform OD600nm of 1. Genomic DNA was extracted using the InstaGene Matrix kit (Bio-Rad, Hercules, CA, USA) according to the manufacturer's instructions. RT-PCR was performed using 5 uL of the supernatant from each extraction. Two genes - the outer membrane protein gene (ompW) specific to V. cholerae and the ctx gene (complex A and B) involved in cholera toxin production - were targeted in the RT-PCR. Two primer sets26-28 were used to amplify the ompW and ctxAB gene segments. The classical and El Tor variants of the tcpA gene were amplified with primers designed by Mukhopadhyay et al.29 To distinguish the O1 and O139 serogroups, the O1 and O139 rfb genes were targeted with primers published by Hoshino et al.30 All the primers used were synthesised at Inqaba Biotech (Pretoria, South Africa) and are shown in Table 1.

Each single-plex RT-PCR amplification reaction contained: 1 x SensiMix HRM reaction buffer (containing dNTPs and 6 mM MgCl2); 0.2 uM primer; heat-activated DNA polymerase; EvaGreen dye (Quantace, London, UK); and 5 uL of DNA. Nuclease-free water (Applied Biosystems, Carlsbad, CA, USA) was used to make up the reaction to a final volume of 25 uL. Amplification was performed in a RotorGene 6000 rotary thermal cycler (5-plex) with high-resolution melting (HRM) capability (Qiagen, Hilden, Germany). The heat-activation step of the DNA polymerase was performed at 95 °C for 10 min, followed by 45 cycles of DNA denaturation at 95 °C for 30 s, annealing at 62 °C for 30 s and extension at 72 °C for 30 s. A final extension step was performed at 72 °C for 5 min.

To differentiate and identify amplification products, HRM curve analysis was performed by lowering the temperature to 60 °C for 5 min, followed by increasing the temperature to 90 °C in increments of 0.1 °C/s. Fluorescence was measured continuously and melting temperature peaks were calculated based on the initial fluorescence curve (F/T) by plotting the negative derivative of fluorescence over temperature versus temperature (-dF/dT versus T).

Statistical analysis

The measure of the significance of the difference observed between the solar irradiated and non-irradiated samples was determined using the Student's t-test; p<0.05 was considered statistically significant.



Characterisation of the Vibrio cholerae strains

The seven strains of V. cholerae used in this study were characterised by RT-PCR of four different gene targets: the ompW, ctxAB, tcpA (classical and El Tor biotype) and the rfb complex (specific for the 01 and 0139 serogroup). All the V. cholerae strains were positive for the ompW gene; only the 1009 strain was negative for the ctxAB gene (Table 2). However, not all the ctxAB gene positive V. cholerae strains belonged to the same serogroup or biotype; three of them - NCTC 5941, G4222, and ERWATA01 - belonged to the 01 serogroup while only one strain, NCTC 12945, was in the 0139 serogroup. The other two strains (UG01, BRITS01) were found to be ctxAB positive but did not belong to either the 01 or 0139 serogroups; the BRITS01 strain did not harbour any of the tcpA genes while the UG01 strain harboured a hybrid (classical and El Tor) tcpA gene.



Exposure of Vibrio cholerae to solar ultraviolet radiation

Exposure of the seven V. cholerae strains to SUVR was done on a sunny day in June (South African winter). The average (±s.d.) minimum and maximum ambient temperatures at the point of exposure were 19.96±0.65 °C and 27.25±1.06 °C, respectively, whereas the water in which the bacteria were irradiated had a temperature of 23.40 ±2.00 °C. There was a mean reduction in the culturability of all the exposed strains of V. cholerae of 7.5±0.81 log10 CFU/mL from an average initial level of 11.02±0.69 log10 CFU/mL after 7 h of exposure. The two toxigenic strains (NCTC 5941 and 12945) were non-culturable after exposure for a further 24 h (Figure 1). The lack of total inactivation was expected because an unusually high dose of the microorganism (11 log CFU/mL) was used initially to increase the odds of detecting any cholera toxin secreted.

Relative quantification of the ctxAB gene

A quantitative RT-PCR of the ctxAB gene relative to the ompW housekeeping gene was done for each of the ctxAB-positive V. cholerae strains (those that were cultured at 37 °C for 15 h in LB). On average, the crossing point for the ompW gene amplification of all the strains was 22.06 with the difference between the lowest and highest CT being 3.6 cycles. To control for possible cell copy number differences in each qRT-PCR, CT values of the ctxAB gene for each strain were normalised using the ompW CT values for the same strain (using the same DNA extraction from overnight cultures, diluted to an OD600nm of 1). The average crossing point for the ctxAB gene for all the ctxAB-positive strains was 14.58 with a difference of 10.2 cycles between the lowest and highest CT value (Table 3). The ctxAB gene in the isolate from BRITS required an additional 9.8 cycles of amplification compared to all the other toxigenic strains. HRM analysis showed that the ctxAB amplicon from the BRITS01 strain was very similar to that of the other toxigenic strains (unpublished data). The solar-irradiated samples showed higher CT values in comparison with the non-solar exposed ones (Table 3). Following 7 h of exposure, the ctxAB gene crossing point for all the toxigenic strains occurred on average 0.6 cycles (p=0.027) earlier for the controls than for the experimental samples. The same was observed for the ompW gene but with a slight decrease in the number of cycles (0.47 cycles, p=0.182). This result translated into an approximate 20% reduction in amplifiable DNA after 7 h of solar exposure relative to the non-solar exposed samples. After 31 h of exposure the crossing point for the ctxAB and ompW genes occurred 1.75 (p=0.0012) and 1.27 (p=0.021) cycles earlier, respectively, for the controls compared with the exposed samples, which translated into a 50% reduction in amplifiable DNA in the solar-irradiated samples when compared with the non-irradiated ones. The percentage reduction in amplifiable DNA was based on results obtained through qRT-PCR of serial dilutions of V. cholerae based on the ompW gene (unpublished data).

Secretion of cholera toxin

The standard curve for the cholera toxin ELISA is shown in Figure 2. On average none of the negative controls (wash buffer) yielded an OD450nm of more than 0.052± 0.002 (mean±s.d.). The mean±s.d. OD450nm for cholera toxin at a concentration of 1 pg/mL for this assay was found to be 0.056±0.003, while the mean±s.d OD450nm for a concentration of 10 pg/mL was 0.081±0.009. On this basis, an OD of 0.081 corresponding to a cholera toxin (sample : negative control) ratio of 1.45 or greater was selected as the cut-off value for what was considered positive for cholera toxin secretion.31 The six toxigenic and one non-toxigenic strains of V. cholerae were tested for their ability to secrete cholera toxin in the culture medium. After 15 h of incubation at 37 °C, the biomass (determined by the OD600nm reading) increased on average from 0.001 to 1.481±0.12 OD600nm units with visible biofilm formation in V. cholerae isolates obtained from Uganda (UG01) and South Africa (ENV1009, G4222, BRITS01). Of all the isolates assessed in this study, only three (G4222, UG01 and NCTC 129450) produced cholera toxin in the culture medium under laboratory conditions (Table 4).



The other strains had a cholera toxin ELISA (sample : negative control) ratio of below 1.45 units and hence were considered negative for cholera toxin secretion. Following exposure to SUVR, the secretion of CT by exposed and non-exposed samples was assessed after 7 h and after 31 h. There were no detectable levels of cholera toxin in either the exposed or non-exposed samples at both time points, with none of the samples showing a sample : negative control ratio of 1.45 or more.


Discussion and conclusions

As a means of mitigating the contraction of waterborne diseases or deaths resulting from the consumption of untreated water, the use of SUVR through a technique known as SODIS has been recommended. We investigated the effect of SUVR on the secretion of cholera toxin by V. cholerae.

The pathogenicity of V. cholerae has been linked to only two key virulence factors - toxin co-regulated pili (TCP) and cholera toxin.32 We used seven strains of V. cholerae, of which six harboured the genes responsible for cholera toxin production (Table 2). Four of the ctxAB-positive strains of V. cholerae contained the tcpA gene while the other two strains (UG01, Brits) were negative for both the rfbO1 and rfbO139 genes (Table 2). The latter were then categorised as non-01/0139 toxigenic strains of V. cholerae. The UG01 strain could not be characterised as either El Tor or classical as it was found to be positive for both tcpA genes. It is possible that this strain of V. cholerae is an El Tor/classical hybrid strain. El Tor variants of the 01/0139 V. cholerae have been isolated from Asia and Africa33,34 but there is no report on the existence of altered El Tor variants that are non-01/0139. The other non-01/0139 toxigenic strain (BRITS01) did not contain the tcpA gene, meaning that CTXФ may have found an alternative route into this strain. Besides horizontal gene transfer, the current theory is that the TCP was the only route through which CTXФ could gain access into the V. cholerae cell. However, recent studies by Campos et al.35,36 have shown that two novel filamentous bacteriophages (VEJФ and VGJФ) could also be used to transduce CTXФ amongst V. cholerae strains that express the mannose-sensitive haemagglutinin (MSHA) receptor. The MSHA receptor is ubiquitously expressed on the surface of many V. cholerae strains and the identification of these novel bacteriophages may explain the existence of non-01/0139 strains of V. cholerae containing CTXФ. Furthermore, this may also explain the sporadic cholera outbreaks that have recently been attributed to non-01/0139 strains of V. cholerae.37,38 Therefore the developments of affordable early detection systems for V. cholerae in the environment are necessary to prevent cholera outbreaks.

Exposure of the toxigenic strains of V. cholerae to SUVR showed that the bacteria did not produce detectable amounts of the cholera toxin in the water. Furthermore, the RT-PCR results confirmed that the integrity of the DNA significantly deteriorated as the quality of amplifiable DNA decreased (Table 3). These findings are contrary to what has been observed by other researchers in regard to cholera toxin secretion. Quinones et al.21,22 reported that the S0S DNA repair resulting from DNA damaging agents such as UV light induced the multiplication of CTXФ and increased the expression of cholera toxin. Similarly, Faruque et al.23 showed that the exposure of V. cholerae to sunlight resulted in an increase of viral titres, which has also been linked to cholera toxin production.21,22 Solar radiation contains UV light which is a DNA damaging agent19,20 and hence could initiate the S0S DNA repair thereby increasing multiplication of CTXФ as well as expression of cholera toxin. However, both these studies exposed V. cholerae to conditions containing a DNA damaging agent in a nutrient-rich environment and for shorter periods. It is also known that a nutrient-rich environment is capable of counteracting the oxygen radicals responsible for the deleterious effects on the microbial cell membrane, which thereby reduces the impact of SUVR on cellular targets.39 These findings suggest that cells that have undergone cellular damage as a result of SUVR in a nutrient-rich environment are capable of repairing themselves. In our study, all V. cholerae strains were solar irradiated for longer periods in water that could be regarded as a nutrient-poor environment. Therefore the bacterial cells received a full dosage of SUVR and were afforded no protection in comparison with cells growing in a nutrient-rich medium.

In conclusion, we have shown that the exposure of toxigenic strains of V. cholerae to SUVR, as recommended for S0DIS, reduces the quantity of amplifiable DNA and inactivates the culturability of these microorganisms.14 However, the major finding from this study was the inability of the pathogenic strains of V. cholerae to secrete cholera toxin above the baseline detection limit following SUVR. The detection limit used in this study (10 pg/mL) was lower than the lethal dose (LD50) of 250 ug of cholera toxin needed to cause cholera in mice.40 This finding is encouraging to communities that may rely on S0DIS for drinking water as a short-term intervention, especially in places where cholera outbreaks are frequent.



We thank Dr Eugenia Barros for providing some of the reagents used in the study.

Authors' contributions

M.P. was the project leader and made conceptual contributions. C.C.S. and W.J. were responsible for the design and execution of the experiments. C.C.S. conceptualised the study and wrote the manuscript.



1. Blow NS, Salomon RN, Garrity K, Reveillaud I, Kopin A, Jackson FR, et al. Vibrio cholerae infection of Drosophila melanogaster mimics the human disease cholera. PLoS Pathog. 2005;1(1):e8.        [ Links ]

2. World Health Organization (WHO). Progress on drinking water and sanitation: 2012 update. Geneva/New York: WHO/United Nations Children's Fund; 2012. p. 58. Available from:        [ Links ]

3. World Health Organization (WHO). Outbreak bulletin. Geneva: WHO; 2011. p. 5. Available from:        [ Links ]

4. Siddique AK, Akram K, Zaman K, Mutsuddy P Eusof A, Sack RB. Vibrio cholerae O139: How great is the threat of a pandemic? Trop Med Int Health. 1996;1(3):393-398.        [ Links ]

5. World Health Organisation (WHO). 1998-Cholera-Vibrio cholerae O139 strain. Geneva: WHO; 1998. Available from:        [ Links ]

6. Nasreldin E, Layla B, Mohammed A, Burhan I, Faisal A, Obeid ET, et al. Molecular characterization of Vibrio cholerae non-O1/non-O139 isolated from coastal water of Arabian Gulf. Afr J Microbiol Res. 2012;6(2):447-452.         [ Links ]

7. Sheikh AF, Goodariza H, Aslani S. Identification of Vibrio cholerae pathogenicity island (ctxA, OmpW and tcpA) in non-O139 and non-O1 V. cholerae strains isolated from Karun River in Ahvaz, Iran. Afr J Microbiol Res. 2012;6(6):1185-1189.         [ Links ]

8. Aliabad NH, Bakhshi B, Pourshafie MR, Sharifnia A, Ghorbani M. Molecular diversity of CTX prophage in Vibrio cholerae. Lett Appl Microbiol. 2012;55(1):27-32.        [ Links ]

9. Mekalanos JJ. Duplication and amplification of toxin genes in Vibrio cholerae. Cell. 1983;35(1):253-263.        [ Links ]

10. Sanchez J, Holmgren J. Cholera toxin structure, gene regulation and pathophysiological and immunological aspects. Cell Mol Life Sci. 2008;65(9):1347-1360.        [ Links ]

11. Aoki H, Wu H, Nakano T, Ooi Y Daikoku E, Kohno T, et al. Nanotransportation system for cholera toxin in Vibrio cholerae O1. Med Mol Morphol. 2009;42(1):40-46.        [ Links ]

12. Berney M, Weilenmann HU, Simonetti A, Egli T. Efficacy of solar disinfection of Escherichia coli, Shigella flexneri, Salmonella Typhimurium and Vibrio cholerae. J Appl Microbiol. 2006;101(4):828-836.        [ Links ]

13. Bosshard F, Berney M, Scheifele M, Weilenmann H-U, Egli T. Solar disinfection (SODIS) and subsequent dark storage of Salmonella typhimurium and Shigella flexneri monitored by flow cytometry. Microbiology. 2009;155(4):1310-1317.        [ Links ]

14. Ssemakalu CC, Pillay M, Barros E. The effect of solar ultraviolet radiation and ambient temperature on the culturability of toxigenic and non-toxigenic Vibrio cholerae in Pretoria, South Africa. Afr J Microbiol Res. 2012;6(30):5957-5964.        [ Links ]

15. Conroy RM, Meegan ME, Joyce T, McGuigan K, Barnes J. Solar disinfection of drinking water protects against cholera in children under 6 years of age. Arch Dis Child. 2001;85(4):293-295.        [ Links ]

16. Du Preez M, McGuigan KG, Conroy RM. Solar disinfection of drinking water in the prevention of dysentery in South African children aged under 5 years: The role of participant motivation. Environ Sci Technol. 2010;44(22):8744-8749.        [ Links ]

17. Boyle M, Sichel C, Fernändez-Ibänez P Arias-Quiroz GB, Iriarte-Puna M, Mercado A, et al. Bactericidal effect of solar water disinfection under real sunlight conditions. Appl Environ Microbiol. 2008;74(10):2997-3001.

18. Ubomba-Jaswa E, Boyle MAR, McGuigan KG. Inactivation of enteropathogenic E. coli by solar disinfection (SODIS) under simulated sunlight conditions. J Phys Conf Ser. 2008;101:012003.

19. Bosshard F, Bucheli M, Meur Y Egli T. The respiratory chain is the cell's Achilles' heel during UVA inactivation in Escherichia coli. Microbiology 2010;156(7):2006-2015.

20. Bosshard F, Riedel K, Schneider T, Geiser C, Bucheli M, Egli T. Protein oxidation and aggregation in UVA-irradiated Escherichia coli cells as signs of accelerated cellular senescence. Environ Microbiol. 2010;12(11):2931-2945.

21. Quinones M, Davis BM, Waldor MK. Activation of the Vibrio cholerae SOS response Is not required for intestinal cholera toxin production or colonization. Infect Immun. 2006;74(2):927-930.

22. Quinones M, Kimsey HH, Ross W, Gourse RL, Waldor MK. LexA represses CTX0 transcription by blocking access of the C-terminal domain of RNA polymerase to promoter DNA. J Biol Chem. 2006;281(51):39407-39412.

23. Faruque SM, Asadulghani, Rahman MM, Waldor MK, Sack DA. Sunlight-induced propagation of the lysogenic phage encoding cholera toxin. Infect Immun. 2000;68(8):4795-4801.

24. Berney M, Weilenmann H-U, Egli T. Flow-cytometric study of vital cellular functions in Escherichia coli during solar disinfection (SODIS). Microbiology. 2006;152(6):1719-1729.

25. Miles AA, Misra SS, Irwin JO. The estimation of the bactericidal power of the blood. J Hyg (Lond). 1938;38(6):732-749.

26. Nandi B, Nandy RK, Mukhopadhyay S, Nair GB, Shimada T, Ghose AC. Rapid method for species-specific identification of Vibrio cholerae using primers targeted to the gene of outer membrane protein OmpW. J Clin Microbiol. 2000;38(11):4145-4151.

27. Goel AK, Tamraker A, Nema V, Kamboj D, Singh L. Detection of viable toxigenic Vibrio cholerae from environmental water sources by direct cell duplex PCR assay. World J Microbiol Biotechnol. 2005;21(6-7):973-976.

28. Le Roux WJ, Van Blerk GN. Use of a high resolution melt real-time polymerase chain reaction (PCR) assay for the environmental monitoring of Vibrio cholerae. Afr J Microbiol Res. 2011;5(21):3520-3526.

29. Mukhopadhyay AK, Chakraborty S, Takeda YNair GB, Berg DE. Characterization of VPI pathogenicity island and CTXphi prophage in environmental strains of Vibrio cholerae. J Bacteriol. 2001;183(16):4737-4746.

30. Hoshino K, Yamasaki S, Mukhopadhyay AK, Chakraborty S, Basu A, Bhattacharya SK, et al. Development and evaluation of a multiplex PCR assay for rapid detection of toxigenic Vibrio cholerae 01 and 0139. FEMS Immunol Med Microbiol. 1998;20(3):201-207.

31. Centers for Disease Control and Prevention (CDC). Laboratory methods for the diaganosis of Vibrio cholerae. Atlanta, GA: CDC; 2012. Available from:        [ Links ]

32. Davis BM, Waldor MK. Filamentous phages linked to virulence of Vibrio cholerae. Curr Opin Microbiol. 2003;6(1):35-42.

33. Hasan NA, Choi SY Eppinger M, Clark PW, Chen A, Alam M, et al. Genomic diversity of 2010 Haitian cholera outbreak strains. Proc Natl Acad Sci USA. 2012;109(29):E2010-E2017.

34. Taneja N, Mishra A, Sangar G, Singh G, Sharma M. Outbreaks caused by new variants of Vibrio cholerae O1 El Tor, India. Emerg Infect Dis. 2009;15(2):352-354.

35. Campos J, Martinez E, Marrero K, Silva Y, Rodriguez BL, Suzarte E, et al. Novel type of specialized transduction for CTXO or its satellite phage RS1 mediated by filamentous phage VGJO in Vibrio cholerae. J Bacteriol. 2003;185(24):7231-7240.

36. Campos J, Martinez E, Izquierdo Y Fando R. VEJO, a novel filamentous phage of Vibrio cholerae able to transduce the cholera toxin genes. Microbiology. 2010;156(1):108-115.

37. Kirschner AKT, Schlesinger J, Farnleitner AH, Hornek R, Süß B, Golda B, et al. Rapid growth of planktonic Vibrio cholerae non-O1/non-O139 strains in a large alkaline lake in Austria: Dependence on temperature and dissolved organic carbon quality. Appl Environ Microbiol. 2008;74(7):2004-2015.

38. Nasreldin E, Layla B, Mohammed A, Burhan I, Faisal A, Obeid ET, et al. Molecular characterization of Vibrio cholerae non-O1/non-O139 isolated from coastal water of Arabian Gulf. Afr J Microbiol Res. 2012;6(2):447-452.

39. Navntoft C, Ubomba-Jaswa E, McGuigan KG, Fernändez-Ibänez P Effectiveness of solar disinfection using batch reactors with non-imaging aluminium reflectors under real conditions: Natural well-water and solar light. J Photochem Photobiol B Biol. 2008;93(3):155-161.        [ Links ]

40. Gill DM. Bacterial toxins: A table of lethal amounts. Microbiol Rev. 1982;46(1):86-94.



Cornelius Ssemakalu
Department of Chemistry
Vaal University of Technology, Private Bag X201
Vanderbijlpark 1900, South Africa

Received: 08 Mar. 2013
Revised: 24 Apr. 2013
Accepted: 25 Apr. 2013

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