Some Ecological Aspects of Phlebotominae Sand Flies (Diptera: Psychodidae) in an Endemic Focus of Anthroponotic Cutaneous Leishmaniasis of Iran

Molecular Identification of Phlebotomus caucasicus and Phlebotomus mongolensis (Diptera: Psychodidae) in a Hyperendemic Area of Zoonotic Cutaneous Leishmaniasis in Iran

Phlebotomus caucasicus Marzinovsky and Phlebotomus mongolensis Sinton are morphologically similar sand fly species. Finding a reliable, fast, and simple method to differentiate these two sand flies is important in understanding their role in the transmission of Leishmania parasite. In our study, 20 specimens of male P. caucasicus, 4 specimens of male P. mongolensis, and 16 specimens of female of both species (Caucasicus group) were examined by polymerase chain reaction (PCR). The result shows identical patterns with a visible fragment of about 500 bp in size. In restriction fragment length polymorphism (RFLP), we observed identical patterns with TasI used as the restriction enzyme. After alignment with sequences of the ITS2 partial gene in GenBank, a perfect match was obtained for the P. mongolensis, but not for P. caucasicus whose sequence was not present in the GenBank. Based on the results of our study, the RFLP-PCR method with nucleotide gene fragment ITS2 was a rapid and reliable method for differentiating these sand fly species.

Distribution and seasonality of Phlebotomus sand flies in cutaneous leishmaniasis foci, Judean Desert, Israel

The ecology of Phlebotomus sand flies in cutaneous leishmaniasis foci as a result of Leishmania tropica in the Judean Desert was studied. Between 2005 and 2007, >265,000 specimens were trapped outdoors and 1,233 specimens were collected indoors. The catches included Phlebotomus sergenti Parrot, Phlebotomus papatasi (Scopoli), Phlebotomus syriacus Adler & Theodor, and Phlebotomus tobbi Adler & Theodor. P. sergenti, the local vector of Leishmania tropica, comprised 90% of outdoor catches, and relatively few were caught indoors. Conversely, P. papatasi were > 90% of the indoor collections, and only a few were caught outdoors. The efficiency of trapping methods varied, but species composition and sex ratio remained constant irrespective of method. Sand flies were abundant on slopes facing east where wind velocity was low, and scarce on slopes facing west and residential areas. Large numbers and high proportion of males that occur near breeding sites were found in man-made rock walls and in rock crevices on slopes of uncultivated hills. Population increase began in April, was more intensive between May and November, peaked in August-September, and significantly decreased in December. Indoors, most of the P. sergenti (< 80%) were collected from September to November. A few sand flies were found between January and March. The effects of climatic factors and human activities on sand fly populations and the risk of Leishmania infections are discussed.