, 1997; Croci et al, 2007) However, due to the presence of both

, 1997; Croci et al., 2007). However, due to the presence of both false-positive and false-negative results in all the biochemical identification methods proposed, some authors (O’Hara et al., 2003; Thompson et al., 2004; Croci et al., 2007) suggested caution in the interpretation of such identifications and advise the use of additional confirmatory testing, such as PCR, Etoposide supplier which enables the detection of the specific nucleotide sequence of V. parahaemolyticus. To specifically detect V. parahaemolyticus by PCR, several researchers used the species-specific targets toxR

gene (Kim et al., 1999; Deepanjali et al., 2005; Croci et al., 2007) and the thermolabile hemolysin gene (tlh) (Bej et al., 1999). Recently Croci et al. (2007), utilizing Vibrio strains (reference, environmental and clinical strains) already identified by API 20E, API 20NE (API; bioMérieux, Marcy l’Etoile, France) and Alsina’s scheme (Alsina & Blanch 1994a, b), conducted a multicenter evaluation of biochemical and molecular methods for V. parahaemolyticus identification and found that Alsina’s scheme for biochemical characterization and toxR gene detection Selumetinib molecular weight for molecular analyses produced the best results for inclusivity, exclusivity and concordance. In addition, to determine the real risk posed to human health by the presence of V. parahaemolyticus,

strain identifications must Methocarbamol be followed by the detection of the pathogenicity marker genes: tdh (thermostable-direct hemolysin) and trh (thermostable-related hemolysin) (Bej et al., 1999). In the present study, aimed at investigating the presence of V. parahaemolyticus in two coastal sites in the Gulf of Trieste (North Adriatic Sea), to select environmental strains, we used the same three biochemical identification methods (Alsina’s scheme, API 20E and API 20NE) using media and bacterial suspensions with a slight modification of the salinity from 0.9% to 3% NaCl. Subsequent molecular analyses were performed to confirm phenotypic characterizations. The PCR results for the 16S rRNA gene, toxR and tlh genes

were compared with biochemical characterizations of V. parahaemolyticus environmental strains to evaluate the effectiveness of the biochemical methods applied. Finally, to investigate the spreading of pathogenic traits, the isolates were subjected to PCR assays to detect tdh and trh genes. The environmental strains had been isolated from a total of 24 seawater samples collected during a monitoring program carried out monthly throughout 2003, which aimed to investigate the presence of vibrios in two sites in the Gulf of Trieste (NE Adriatic Sea): C1 (45°42′03″N, 813°42′36″E) is about 200 m offshore and D2 (45°45′49″N, 13°35′36″E) is 1250 m offshore and is located near the Isonzo River delta. Surface (−0.

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