Throughout history various worldwide cholera pandemics have ocurred. In Mexico, seven states have been affected, and one of those was Veracruz. In the 5th Sanitary Jurisdiction, where this study was performed, 216 cases, including three deaths, were reported between 1991 and 1997 (
3). Following that date, no further cases have been reported. This means that they appear abruptly and then disappear, and again the question is always the same: What happens to
V. cholera during those intervals when it is not detected? Most researchers believe that it remains latent in reservoirs (
6-
9), and it has also been suggested that these may sustain
V. cholera for long periods of time (
6-
11). The reservoirs or sites of survival and multiplication of pathogenic vibrions between epidemics are not well known. It is well documented that during epidemics, toxigenic
V. cholera O1 can be isolated from local freshwater (
10,
11), but it disappears after the epidemic subsides (
4,
7), which is one reason to give importance to the identification of these reservoirs. After working in vitro, previous reports have suggested that aquatic plants such as
L. minor and
E. crassipens are
V. cholera reservoirs (
6-
9), and our results corroborate these findings.
The presence of
E. crassipens and
L. minor also coincide with municipal wastes and this may indicate water contamination by feces. As those plants have the capacity of denitrification (
12), they may be considered as indicators of fecal contamination and a potential risk for cholera disease. Our results, determined after biochemical and serological typification, demonstrated and corroborated the permanence and viability of
V. cholera biotype El Tor in aquatic plants, several years after the outbreaks (
7,
13).
The isolated and typified V. cholera El Tor, collected from either L. minor or E. crassipens roots, showed the same biochemical characteristics as the V. cholera isolated from a patient with cholera. We believe that this microorganism is toxigenic, considering the results obtained with polyvalent and monovalent antiserums to test V. cholera O1 agglutination, and its hemolysin activity in human group O and lamb’s blood.
Using serological tests, both strains were identified as Inaba. However, we do not know if we also started with Ogawa which mutated to Inaba, as this frequently occurs (
14). On the other hand we could have dealt with both serotypes, since the strains were isolated after the roots had been washed with chloride solution, which indicates high resistant capacity, as reported for the Ogawa rugose TSI-4/R strain (
15), and also with the colonies morphology. According to the appearance of the
V. cholera colonial morphologies, two-phase variants, including smooth and rugose, have been described for Ogawa. In addition, the reversible phase variation between the rugose and smooth colony variants, and associated phenotypes, is postulated to be an important factor for the survival of the organism, as it is also dependent on the nutritional conditions (
15,
16). These could happen in the Inaba strain too; in any case both of these strains are known to be a public health risk.
Therefore, it is very important to conduct future studies to find out more about this association and confirm the presence of dangerous microorganisms in those plants. In addition it is also important to verify if these plants are permanent reservoirs of
V. cholera, because this may explain some epidemiological cases, including reported cases in Peru, Hurricane Katrina and the situation in endemic zones (
1,
3). Poor sanitary conditions and the fact that cholera is one of the best examples of water-borne diseases that can be controlled through the implementation of water treatment and sanitation measures, make further investigations vital. Outbreaks should be controlled with appropriate water treatment, but in affected places the residual effluent is discharged directly into the rivers where these plants grow. The presence of organic materials favors the growth of V.
cholera roots, and this is due to stress factors such as; temperature, pH, and salinity, and they may induce the conversion from a nonpathogenic to a pathogenic phase, which is a constant risk.
Even if these plants are the only reservoirs of vibrions that are not toxigenic, they still present a high risk health, because filamentous phages live in those environmental conditions and they are involved in the transference of the toxigenic genes to V. cholera.