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Applied and Environmental Microbiology, March 2009, p. 1604-1613, Vol. 75, No. 6
0099-2240/09/$08.00+0 doi:10.1128/AEM.01594-08
Copyright © 2009, American Society for Microbiology. All Rights Reserved.
Evaluation of Genotypic and Phenotypic Methods To Distinguish Clinical from Environmental Vibrio vulnificus Strains
,
Eva Sanjuán,1,
Belén Fouz,1
James D. Oliver,2 and
Carmen Amaro1*
Departamento de Microbiología y Ecología, Universidad de Valencia, Avda. Dr. Moliner 50, 46100 Burjassot, Valencia, Spain,1
Department of Biology, University of North Carolina at Charlotte, Charlotte, North Carolina 282232
Received 11 July 2008/
Accepted 5 January 2009

ABSTRACT
Vibrio vulnificus is a heterogeneous bacterial species that
comprises virulent and avirulent strains from environmental
and clinical sources that have been grouped into three biotypes.
To validate the typing methods proposed to distinguish clinical
from environmental isolates, we performed phenotypic (API 20E,
API 20NE, and BIOLOG tests) and genetic (ribotyping and DNA
polymorphism at several loci) studies with a large strain collection
representing different biotypes, origins, and host ranges. No
phenotypic method was useful for biotyping or grouping strains
with regard to the origin of an isolate, and only the BIOLOG
system was reliable for identifying the strains at the species
level. DNA polymorphisms divided the population into three major
profiles. Profile 1 strains were
vcg type C, 16S rRNA type B,
and
vvh type 1 and included most of the biotype 1 human septicemic
isolates; profile 2 strains were
vcg type E, 16S rRNA type A,
and
vvh type 2 and included all biotype 2 isolates together
with biotype 1 isolates from fish and water and some human isolates;
and profile 3 strains were
vcg type E, 16S rRNA type AB, and
vvh type 2 and included biotype 3 strains. Ribotyping divided
the species into two groups: one group that included profile
1 biotype 1 isolates and one group that included isolates of
all three biotypes with the three profiles described above.
In conclusion, no genotyping system was able to distinguish
either clinical strains from environmental strains or biogroups
within the species
V. vulnificus, which suggests that new typing
methodologies useful for public health have to be developed
for this species.

INTRODUCTION
Vibrio vulnificus is an aquatic bacterial species that produces
infections in fish and humans (
30,
31,
36). Although human infections
are relatively uncommon, they can be life threatening in patients
with chronic or immunocompromising diseases (
32,
36). The main
transmission routes of human vibriosis are consumption of raw
or undercooked shellfish and exposure of open wounds or sores
to seawater (
32,
36). The mortality rate due to primary septicemia
after contaminated shellfish consumption is approximately 50%,
and the mortality rate resulting from reported wound infections
is 25% (
4,
20).
This species is phenotypically and serologically heterogeneous (9, 17, 38). Originally, it was divided into two biotypes, one virulent for humans and one virulent for fish (38). In early studies, negative results for indole production, ornithine decarboxylase activity, acid production from mannitol and sorbitol, and growth at 42°C, as well as serological specificity, allowed investigators to distinguish the first fish isolates (biotype 2 serovar E) from human isolates (9, 38). However, this simple scheme of intraspecific classification lost its utility when more strains were isolated from fish vibriosis worldwide (19, 21, 24). These new isolates differed serologically and phenotypically from the isolates initially studied (21, 24) and were grouped in two additional serovars (serovars A and I) using the same serotyping system (21; C. Amaro, unpublished results). Interestingly, biotype 2 serovar E was also isolated from human infections, usually after manipulation of diseased fish, which increased the diversity of isolates able to infect humans (1). In addition to this biotype 2 heterogeneity, a third biotype was described in 1999 in Israel (11). To date, this biotype includes only isolates from wound infections initiated by handling spiny fish (11, 16). These isolates were immunologically identical to each other but distinguishable from biotype 2 serovars using the same serotyping system (12). At least four additional serovars can be found using this serotyping system among biotype 1 isolates, although they have not been fully characterized (2; C. Amaro, unpublished data).
Due to the public health importance of this species and the difficulties in rapidly differentiating the strains with human virulence potential, several typing systems have been developed. The main genotyping systems are based on differences in the sequences of some loci, such as 16S rRNA, hemolysin (vvhA) genes, or the vcg (virulence-correlated gene) locus, which divide V. vulnificus populations in two genotypes, one primarily associated with environmental isolates and the other primarily associated with clinical isolates (7, 28, 33, 35). Most of the typing techniques described have been used for V. vulnificus, including randomly amplified polymorphic DNA analysis, repetitive extragenic palindromic PCR, and ribotyping, among others (5, 15, 23, 37, 39). These techniques are able to distinguish some specific groups within V. vulnificus; however, the majority of studies were performed with strain collections biased toward biotype 1, since they included few or no biotype 2 and 3 strains, and toward North America, since the majority of the isolates were from that geographical region (14, 37).
The main objective of our study was to validate the usefulness of two typing methodologies (ribotyping and polymorphisms at selected loci) with a wide collection of strains of the different biotypes from different sources and geographic regions, whose biochemical diversity was also analyzed by different methodologies (API 20E, API 20NE, and BIOLOG).

MATERIALS AND METHODS
Bacterial strains and growth conditions.
A total of 111
V. vulnificus strains of different biotypes from
different sources and regions were used in this study (Table
1). The strains were maintained both as lyophilized stocks at
room temperature (25°C) and as frozen stocks at –80°C
in marine broth (Difco) plus 20% (vol/vol) glycerol. Strains
were grown in Luria-Bertani broth or on Luria-Bertani agar containing
1% (wt/vol) (total concentration) NaCl at 28°C for 24 h.
Phenotypic analysis. (i) Biotyping.
The biotypes of the strains were confirmed by multiplex PCR
(
34). This method allows identification at the species level
and at the same time discrimination between biotypes 1/3 and
2 and, within biotype 2, discrimination of serovar E, the zoonotic
serovar. The biotype 3 strains used in this study were previously
biotyped (
11).
(ii) API 20E and API 20NE analysis.
API 20E and API 20NE test kits (bioMerieux) were used according to the manufacturer's directions, with incubation of the strips at 28°C. Bacterial suspensions in saline solution or in AUX medium plus NaCl at a final concentration 1% (wt/vol) were used as the inocula for API 20E and API 20NE kits, respectively (10). Examination of the strips was conducted after 24 and 48 h. API profiles were compared using API DataBase version 4.0 for API 20E strips and version 6.0 for API 20NE strips (APILAB Software, version 3.3.3, Apilab Plus; bioMerieux).
(iii) BIOLOG analysis.
BIOLOG-GN MicroPlates (BIOLOG) were used to evaluate substrate utilization patterns of the strains. The cells were streaked on BIOLOG Universal Growth agar (Oxoid) supplemented with 5% sheep erythrocytes (BUG-S) and incubated for 24 h at 28°C. Wells of a plate were inoculated with 150 µl of bacterial suspensions adjusted to the appropriate density in saline solution. The inoculated microplates were incubated at 28°C for 24 and 48 h and analyzed using a BIOLOG Microstation reader. Test results were obtained and identification (BIOLOG Microlog 6.01 database) was performed using BIOLOG MicroLog 3 software (BIOLOG), applying the automatic threshold option. Differences in the use of carbon substrates between the different groups were analyzed using the chi-square test function at
= 0.05, employing SPSS 14.0 for Windows. Bionumerics software version 4.0 (Applied Maths) was used to cluster the strains based on their substrate utilization patterns using the unweighted-pair group method using arithmetic average (UPGMA) and two different similarity coefficients, the Jaccard and simple matching coefficients.
Genetic fingerprinting. (i) DNA sequence polymorphisms.
The polymorphisms at selected loci were determined by PCR analysis of all V. vulnificus strains. Differentiation between the described alleles of the hemolysin gene (vvhA) and the 16S rRNA gene was performed under conditions described elsewhere (35). vcg typing for the environmental (type E) or clinical (type C) genotype was performed as described by Rosche et al. (33). In all assays, ca. 250 ng of DNA per 25 µl of reaction mixture was amplified using the high-fidelity Expand PCR system (Roche Diagnostics) in a TC-312 thermal cycler (Techne). The existence of an association between polymorphism and group (biotype, origin, or serovar) was calculated using the Pearson chi-square test function at
= 0.05, employing SPSS 14.0 for Windows.
(ii) Automated ribotyping.
Ribotyping of the V. vulnificus isolates was carried out with the Riboprinter system (Qualicon Inc.). The assay was performed under conditions recommended by the manufacturer using HindIII (Roche) at 400 U µl–1. Riboprinter patterns were partially processed by the Riboprinter system software in order to reduce background noise and to normalize the band positions using DNA size standards as references. The normalized patterns were then exported for further analysis as .txt files and imported into the Bionumerics software (version 4.0; Applied Maths) using LoadSamples script (DuPont Qualicon). Clustering analysis was performed by UPGMA based on the Dice coefficient for band matching, with a position tolerance and an optimization setting of 1%. Bands for band matching were assigned automatically and manually edited if necessary.

RESULTS
Phenotypic analysis. (i) API 20E and API 20NE analysis.
A total of 25 different API 20E and API 20NE profiles were obtained
for the
V. vulnificus collection (see Tables S1 and S2 in the
supplemental material). In the case of the API 20E system, only
60% of the strains were correctly identified as
V. vulnificus,
and the percentage was 20% for biotype 3 isolates. The remaining
strains gave a mixed profile or were misidentified as
Burkholderia cepacia or
Vibrio parahaemolyticus. Three main profiles were
detected for biotype 1 isolates (5346105 [19.6%], 5146105 [15.7%],
and 5346005 [17.6%]), two main profiles were detected for biotype
2 serovar E isolates (5006005 [29.4%] and 5206005 [23.5%]),
two main profiles were detected for biotype 2 non-serovar E
isolates (5146105 [38%] and 5346105 [33%]), and one main profile
was detected for biotype 3 isolates (4146004 [40%]) (see Table
S1 in the supplemental material). None of the strains was correctly
identified as
V. vulnificus with the API 20NE system. Instead,
most of the isolates were identified at the genus level as
Aeromonas or
Vibrio, and the species
Aeromonas hydrophila and
Vibrio cholerae were the most frequent options (see Table S2 in the supplemental
material). The main profile exhibited by biotype 1 isolates
was 7476745 (43.1%), the main profile exhibited biotype 2 serovar
E isolates was 5472745 (73.6%), the main profile exhibited by
biotype 2 non-serovar E isolates was 7476745 (61.9%), and the
main profile exhibited by biotype 3 strains was 7062745 (40%).
(ii) BIOLOG GN2 plates.
The BIOLOG system correctly identified 84% of the 111 isolates studied. Eight of the low-discrimination identifications (7% of the strains) were listed as V. vulnificus as the first option, although with low probability. The carbon sources that V. vulnificus was able to oxidize are shown in Table 2. On average, 32 carbon substrates were utilized. V. vulnificus strains did not use amines or carboxylic acids, with the exception of D-glucoronic and succinic acid, which were metabolized by more than the 80% of the strains examined (Table 2). There was no specific profile (expressed as the carbon sources utilized by an isolate) that could be assigned to a particular group of strains. In fact, only two strains, isolated from the same water sample (PD-1 and PD-5), used the same carbon sources. In addition, cluster analysis performed by applying either the Jaccard index, which takes into account the similarity based on the number of positive coincidences, or simple matching, which takes into account the positive and negative coincidences, revealed that most of the groups of strains were not related to a common biotype, serovar, or origin (Fig. 1). Such variability in the use of carbon sources caused difficulties in attempts to establish a reliable test that could be used for discriminating biotypes or serovars. Nevertheless, we found statistical differences for the differential use of some carbon sources between groups (Table 2). Some examples are the use of the cellobiose and gentibiose, which was negative for the biotype 3 isolates but positive for the rest of the strains tested. The biotype 2 strains were able to oxidize β-methyl-D-glucoside; however, no biotype 3 and few biotype 1 isolates were able to use this carbon source.
Genetic diversity observed with DNA polymorphism locus typing.
Results of the multiplex PCR (
34) analysis are shown in Table
1. The allelic distribution among environmental, human, and
fish
V. vulnificus isolates for the three biotypes is shown
in Table
3. Biotype 1 strains from oysters and human blood predominantly
were
vcg type C, whereas the biotype 1 strains from fish and
nonsepticemic human infections and most of the biotype 1 isolates
from water, together with biotype 2 and 3 isolates regardless
of their origin, were
vcg type E. We detected
vvhA gene type
1 in biotype 1 strains from oysters and human septicemia together
with biotype 3 strains from human bacteremia, whereas biotype
1 strains from fish and human wounds and all biotype 2 strains,
irrespective of their origin, were
vvhA type 2. In contrast
to the
vcg results, we observed more variability in the
vvhA typing results with the water isolates of biotype 1. These isolates,
together with those from human wounds, also showed variable
results for the 16S rRNA gene polymorphisms, while fish biotype
1 and biotype 2 isolates, regardless of their origin, were type
A. Oyster and human blood biotype 1 isolates were type B, and
biotype 3 isolates were type AB. Thus, three main genotypic
profiles were found among the collection of
V. vulnificus isolates.
Profile 1 consisted of genotype
vcg type C, 16S rRNA type B,
and
vvh type 1 and was exhibited by biotype 1 strains from human
septicemia and oysters. Profile 2 consisted of genotype
vcg type E, 16S rRNA type A, and
vvh type 2 and was exhibited by
biotype 2 isolates, regardless of their origin, and by biotype
1 isolates from fish and water and some human isolates. Profile
3 consisted of genotype
vcg type E, 16S rRNA type AB, and
vvh type 2 and was exhibited only by biotype 3 strains. No specific
profile was found for water and human nonblood isolates of biotype
1, which showed variable results. Some atypical profiles were
also found, such as the profile showed by environmental biotype
1 isolate Riu-1, which was positive for both types of 16S rRNA
(as were the biotype 3 strains) and possessed hemolysin type
2.
View this table:
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[in a new window]
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TABLE 3. Distribution of genotypes and genotypic profiles among V. vulnificus biotypes according to strain origin
|
Automated ribotyping.
Figure
2 shows the dendrogram obtained from the normalized ribotypes
(Rt) after UPGMA clustering. The Riboprinter generated some
bands with low intensity, especially above 15 kb, that probably
corresponded to undigested DNA as they were not reproducible
when selected strains were ribotyped a second time. These bands,
together with those at <1 kb, were not taken into account
in the ribotyping cluster analysis. Forty-seven Rt were distinguished
among the 111
V. vulnificus strains (Table
1), which grouped
at a similarity level of 62%. We included two strains of other
Vibrio species as outgroups,
V. harveyi and
V. parahaemolyticus,
which were clearly different from the strains of
V. vulnificus and which grouped at 45% similarity (Fig.
2). Two main groups
of
V. vulnificus strains could be distinguished. Division A
included 92% of the biotype 1 strains and the majority of human
blood (70%) and oyster (75%) isolates with profile 1, whereas
division B included some biotype 1 strains from human wounds,
fish, and water with profile 2 and the majority of biotype 2
(96%) and 3 (100%) isolates with profiles 2 and 3, respectively.
These two divisions could be subdivided into five groups (ribogroups
AI, AII, BI, BII, and BIII) based on

80% similarity, even though
five strains (CECT 4869, CG106, V4, 94-9-118, and 534) did not
cluster with other strains (Fig.
2). All of the strains with
profile 1 were clustered in ribogroups AI and AII, except for
a strain from human septicemia (CECT 5169) and an environmental
strain (CG100). Ribogroups AI, AII, and BIII included strains
with a unique biotype; ribogroups AI and AII included biotype
1 strains, mostly from humans, and ribogroup BIII included biotype
2 and serovar E strains isolated from an unusual source, brackish
water of the estuary of the River Ebro (Mediterranean Sea).
The rest of the biotype 2 strains were included in ribogroup
BII, and most of them exhibited the same Rt pattern (Rt 25)
regardless of the serovar, while all the strains of biotype
3 were grouped in ribogroup BI, which also showed a unique Rt
(Rt 24).

DISCUSSION
In order to validate the genotyping systems designed for differentiating
clinical from environmental
V. vulnificus isolates, a selection
of these systems was used with a large collection of strains
of different biotypes and serovars recovered from sources worldwide.
The phenotypic diversity of the collection was analyzed first
with three miniaturized bacterial identification systems, whose
usefulness for identification of
V. vulnificus at the specific
or intraspecific level was evaluated in parallel. The BIOLOG
system was the most effective system, giving 84% correctly identified
strains. The BIOLOG results showed that
V. vulnificus has the
ability to oxidize a great variety of carbon sources. This species
is also highly heterogeneous, since almost every isolate had
a unique profile. The percentage of correctly identified strains
was 60% when the API 20E system was used and 0% with the API
20NE system. These results are in agreement with previous reports
on the doubtful usefulness of both API systems for identification
of clinical and environmental
V. vulnificus isolates (
10,
17,
18,
29), although they are still being used, mostly for clinical
diagnosis. Based on these results, the BIOLOG system is the
most adequate system for
V. vulnificus identification at the
species level, and the other two systems, especially the API
20NE system, should not be used unless the databases are updated
with the profiles found in the present work. When the utility
of the three systems for intraspecific classification was considered,
none of them was able to distinguish biotype 2 non-serovar E
(serovar A/I) isolates from biotype 1 isolates, although several
API 20E and API 20NE profiles were found to be specific for
biotype 2 serovar E and biotype 3 strains (see Tables S1 and
S2 in the supplemental material). Inclusion of these profiles
in the API database would facilitate correct identification
of more
V. vulnificus isolates and in some cases subclassification
into biotype 2 serovar E or biotype 3. In general, however,
the profiles would not allow discrimination of other biotypes
or groups. Despite finding several tests in the BIOLOG system
that revealed significant differences between groups, we found
that using these tests was not adequate for good discrimination.
Only the combination of negative results for cellobiose and
gentibiose breakdown allowed allocation of isolates to biotype
3.
Previous studies have proposed various genetic methods to distinguish strains of this species with human-pathogenic potential (14, 28, 33, 35). We performed an analysis of three of these methods, the 16S rRNA, vvhA, and vcg methods, with our V. vulnificus collection. According to previous reports, most V. vulnificus human isolates should be vcg type C, vvhA type 1, and 16S rRNA type B (genotypic profile 1 in our study), and most environmental isolates should be vcg type E, vvhA type 2, and 16S rRNA type A (genotypic profile 2 in our study). However, we were able to establish an association only between genotypic profile 1 and human isolates for biotype 1 strains from septicemic cases, regardless of their geographical origin. The remaining biotype 1 human isolates mostly exhibited genotype profile 2, like the majority of the environmental biotype 1 isolates, except those from oysters. Our results for oyster isolates are opposite the results obtained by other workers (22, 28, 33) and could be due to the inclusion of isolates from Asia, where a major proportion of 16S rRNA type B has been reported (25). In previous studies variation between ratios of 16S rRNA type A to rRNA type B were observed for different sampling points or water temperatures (22, 27, 39). For the rest of the isolates, we found an association between profile and biotype rather than an association between profile and origin of the isolate. Thus, all biotype 2 strains, regardless of their source (human, fish, or water), exhibited profile 2, and all biotype 3 strains, all from human bacteremia, exhibited profile 3. The variability in profiles observed among biotype 1 strains can be attributed to the greater genetic variability of this biotype. Genetic characterization of our V. vulnificus collection performed by ribotyping confirmed this observation. Ribotyping is a general technique also used in epidemiological studies of V. vulnificus (3, 5, 6, 9, 19, 23). We selected HindIII to perform the DNA digestion since it has been reported to provide the best discrimination between biotypes (9, 18). A common pattern was observed for all V. vulnificus strains, and a group of bands between 2 and 3 kb was absent in the profiles of the other vibrios examined. These bands were also observed in previous studies with manual protocols (9, 18, 22). The strains were grouped on the basis of their similarities in ribopatterns into two divisions and five groups. As expected, biotype 1 strains were found in almost every group and subgroup. Nevertheless, the biotype 1 strains that exhibited profile 1 were located mostly in division A, while the second division included all the biotype 2 and 3 strains together with additional biotype 1 strains from environmental sources and wound infections. In this division, the major genotypic profiles were profiles 2 and 3. Interestingly, ribogroup BI was comprised of all biotype 3 isolates that were closely related to environmental biotype 1 strains from sites related to fish farms. This result supports the previous hypothesis concerning the origin of biotype 3 as a clone associated with tilapia culture in Israel that recently emerged (13).
The eel-pathogenic strains were located in division B, with a major Rt (Rt 25) that included strains of the different serovars as well as other biotype 1 strains isolated mainly from the environment or from human wounds. This result also supports the hypothesis that biotype 2 strains could have been emerged from biotype 1 strains present in the environment. Recently, it has been shown that eel virulence relies on a 68-kb plasmid that can be transmitted between strains by conjugation with the aid of a conjugative plasmid (26). In this scenario, biotype 2 strains could have evolved independently by acquisition of the virulence plasmid by different clones of biotype 1 strains in the environment. Only one of these clones (serovar E) could be phenotypically distinguished from the rest of the biotypes, while the rest (serovars A and I) could not be distinguished. Additional studies based on multilocus sequence analysis with biotype 2 strains of different serovars and from different sources are needed to confirm this hypothesis.
Ribotyping has been used for differentiating clinical and environmental V. vulnificus isolates and biotypes, and several correlations between ribopatterns and geographic origin have been found (5, 6, 8). Our results, however, suggest that this technique may be useful for revealing genetic relationships among V. vulnificus isolates, but it is not likely to be useful for rapid identification of strains with public health interest.
In conclusion, the results obtained in the present work demonstrate that the species V. vulnificus is highly heterogeneous and that most of the diversity is present in biotype 1. Biotype 2 and 3 strains, in contrast, are more homogeneous, even though biotype 2 is serologically and phenotypically heterogeneous. There is a need for methods capable of rapid, sensitive, and accurate identification of the strains dangerous for public health. The DNA polymorphisms studied have been proposed for routine monitoring of the quality of seafood and water, but our results suggest that their use could eliminate samples containing strains with human-pathogenic potential, such as biotype 2 serovar E and biotype 3 strains. It is clear, therefore, that new genetic markers with epidemiological potential need to be found to clearly differentiate V. vulnificus.

ACKNOWLEDGMENTS
This work was financed by grants AGL2005-04688 (cofinanced with
FEDER funds), AGL2008-03977/ACU, and PET2005-0053 from the Spanish
Ministry for Education and Science and by grant MTKD-CT-2004-0145019
from the European Union.
We thank Sergi Ferrer for advice concerning the Bionumerics software.

FOOTNOTES
* Corresponding author. Mailing address: Departamento de Microbiología y Ecología, Universidad de Valencia, Avda. Dr. Moliner 50, 46100 Burjassot, Valencia, Spain. Phone: 34-96-3543104. Fax: 34-96-3544570. E-mail:
carmen.amaro{at}uv.es 
Published ahead of print on 9 January 2009. 
Supplemental material for this article may be found at http://aem.asm.org/. 
Present address: South Texas Center for Emerging Infectious Diseases and Department of Biology, The University of Texas at San Antonio, One UTSA Circle, San Antonio, TX 78249. 

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Applied and Environmental Microbiology, March 2009, p. 1604-1613, Vol. 75, No. 6
0099-2240/09/$08.00+0 doi:10.1128/AEM.01594-08
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