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Article available at http://www.parasite-journal.org or http://dx.doi.org/10.1051/parasite/2007142173 DESCRIPTION OF BREEDING SITES OF CULICOIDES SPECIES (DIPTERA: CERATOPOGONIDAE) IN TURKEY USLU U.* & DIK B.** Summary: The aim of this study was to describe the breeding sites of Culicoides species in Konya province, Turkey. The samples taken from 11 different habitats in Konya province were examined for Culicoides species. The collected adult Culicoides specimens were reared in plastic buckets in our laboratory. Among 2,798 specimens reared, 18 species were identified. Culicoides circumscriptus Kieffer, 1918 was the most abundant species reared in the samples taken from mud rich in organic matters near the water reservoirs; C. circumscriptus, C. nubeculosus (Meigen), 1830 and C. shaklawensis Khalaf, 1957 in moist soil with organic matter; C. gejgelensis Dzhafarov, 1964 in moist soils, along watering channels and dripping waters; C. festivipennis Kieffer, 1914 and C. circumscriptus along sewage channel; C. festivipennis in reed sites and along garden watering channels; C. circumscriptus in rain pools; C. odiatus Austen, 1921 and C. circumscriptus in mud near the dams; C. gejgelensis and C. kibunensis Tokunaga, 1937 from sites along the stream. No Culicoides was reared in the samples obtained from livestock dung and tree holes. It was observed that C. circumscriptus, C. festivipennis and C. shaklawensis preferred mud rich in organic matters near the water reservoirs. Culicoides imicola Kieffer, 1913, which is the main vector of bluetongue, was not detected in Konya province. The others vectors of bluetongue, C. obsoletus gr. (Meigen), 1818, C. schultzei gr. (Enderlein), 1908 and C. pulicaris (Linnaeus), 1758 were only obtained in little numbers. KEY WORDS : Culicoides, breeding sites, Konya province, Turkey. Résumé : DESCRIPTION DES SITES DE DÉVELOPPEMENT LARVAIRE DES DIFFÉRENTES ESPÈCES DE CULICOIDES (DIPTERA : CERATOPOGONIDAE) EN TURQUIE Le but de cette étude était de décrire les sites de développement larvaire des espèces de Culicoides dans la province de Konya, en Turquie. Les Culicoides adultes, prélevés au niveau de 11 habitats, ont été élevés dans des seaux en plastique dans notre laboratoire. Parmi les 2798 spécimens élevés, 18 espèces ont été identifiées. Culicoides circumscriptus Kieffer, 1918 est l espèce la plus abondantes dans les échantillons de boue riche en matière organique à proximité des réservoirs d eau; C. circumscriptus, C. nubeculosus (Meigen), 1830 et C. shaklawensis Khalaf, 1957 dans les sols humides riches en matière organique; C. gejgelensis Dzhafarov, 1964 dans les sols humides le long des canaux d irrigation et des eaux d égouttement; C. festivipennis Kieffer, 1914 et C. circumscriptus le long des égouts; C. festivipennis dans les zones de roseaux et le long des canaux d irrigation de jardin; C. circumscriptus dans les réservoirs d eau de pluie; C. odiatus Austen, 1921 et C. circumscriptus dans la boue près des barrages; C. gejgelensis et C. kibunensis Tokunaga, 1937 le long des rivières. Aucun Culicoides en provenance du fumier du bétail ou de trous d arbre n a été élevé. En définitive, C. circumscriptus, C. festivipennis et C. shaklawensis préfèrent les boues riches en matières organiques à proximité des réservoirs d eau; C. imicola Kieffer, 1913, qui est le vecteur principal de la maladie de la langue bleue, n a pas été détecté dans la province de Konya; C. obsoletus gr. (Meigen), 1818, C. schultzei gr. (Enderlein), 1908 et C. pulicaris (Linnaeus), 1758, qui sont également des vecteurs de cette maladie, n ont été obtenus qu en petite quantité. MOTS CLÉS : Culicoides, site de reproduction, province de Konya, Turquie. Culicoides species are widely seen throughout the world (Blackwell, 2001). Some Culicoides species such as C. imicola Kieffer, 1913 and C. obsoletus gr. (Meigen), 1818 are known as vectors of a number of serious viral diseases such as bluetongue and african horse sickness (Braverman, 1994; Blackwell, 2001). The species belonging to the genus Culicoides may rear in various breeding sites (Mullen & Hribar, 1988). Some Culicoides species can rear in soil, mud rich in organic matter, swamps, marshes, mud around dams, water reservoirs, along the drainage channels and stream, tree holes, cow dung (Braverman et al., 1974; * Department of Parasitology, Faculty of Veterinary Medicine, University of Selcuk, Kampus, 42075, Konya-Turkey. Correspondance: Ugur Uslu. Tel.: +90 332 223/2730 Fax: +90 332 2410063. E-mail: uuslu@selcuk.edu.tr Lubega & Khamala, 1976; Bram, 1978; Braverman, 1978; Mullen & Hribar, 1988; Nevill et al., 1988). Such great diversity of habitats of different species of biting midges makes it difficult to find out the immature stages. Immature stages of Culicoides species usually lives in 0-5 cm depth of the soil (Lubega & Khamala, 1976; Blackwell & King, 1997; Uslu & Dik, 2006). It was stated that C. imicola were reared in cow dung and rich in organic material without surface water (Braverman, 1973; Braverman et al., 1974; Braverman & Galun, 1973), C. schultzei gr. (Enderlein), 1908 in between rows of tomatoes (Muradov, 1965), C. obsoletus gr. in stagnant water reservoirs and marsh-ridden parts with bushy vegetation (Dzhafarov, 1976), and C. pulicaris (Linnaeus), 1758 from small water logged areas in near lakes, bogs and small marsh-ridden places (Konurbayev, 1965; Dzhafarov, 1976). 173

USLU U. & DIK B. Hribar (1990) stated that gar-extraction and salt-flotation was the most effective method for collecting larvae samples of biting midges. In Turkey, the first systematic research on adult Culicoides species was carried out by Navai (1977). Afterwards, systematic and ecological studies on Culicoides species have been studied in different parts of Turkey (Jennings et al., 1983; Dik & Dinçer, 1992; Dik, 1993; 1996; Yılmaz, 1994; Eren et al., 1995; Yagcı et al. 1999; Tilki & Dik, 2004; Dik et al., 2006; Uslu & Dik, 2005; Uslu & Dik, 2006). No study has been found describing breeding sites of Culicoides species in Turkey. The purpose of this study was to describe the breeding sites of Culicoides species in Konya province, Turkey. MATERIALS AND METHODS Konya province has a climate that is hot and dry in the summer, cold and rainy in the winter season, and is located at least 1,000 m above sea level and between latitudes 37.59 N and 32.34 E. Four districts of Konya (Centrum, Çumra, Kadınhanı, Sarayönü) were regularly visited every 15 days from April 2001 to April 2002, and the samples from different breeding sites were taken. All samples were taken from ten different places, 10 cm in diameter and 5 cm deep for each breeding sites by using steel-made sampling tool, except of the materials obtained from tree holes using a metal spoon or scoop. The samples were put in nylon bags, brought to the lab and placed in the plastic buckets. The samples were kept for 30-35 days in the lab to allow rearing of adult Culicoides. In order to avoid drying out, the samples were humidified with sprayed distilled water every other day. The buckets were lighted up with 300 Watt bulb to capture the flying Culicoides specimens. The insects were caught by vacuum and transferred into a tube containing 70 % of ethyl alcohol. Big sized insects were removed by a brush and little sized insects were examined for identification of Culicoides under the light microscope. The Culicoides species were cleared in alcohol-phenol for a few days, and identified by using a Nikon SMZ-10 stereo microscope. In addition, the samples were analyzed to determine the amount of organic substances. Chi-square test was used for the statistical analyses. RESULTS Culicoides specimens of all samples were taken from 13 different breeding sites in Konya province, except from dung and tree holes. In this study, 2,798 Culicoides specimens were reared in the lab; of these, 1,559 were females and 1,239 males. The 18 identified Culicoides species were namely Culicoides circumscriptus Kieffer, 1918, C. festivipennis Kieffer, 1914, C. shaklavensis, C. gejgelensis Dzhafarov, 1964, C. puncticollis (Becker), 1903, C. nubeculosus (Meigen), 1830, C. riethi Kieffer, 1914, C. longipennis Khalaf, 1957, C. odiatus Austen, 1921, C. flavipulicaris Dzhafarov, 1964, C. cataneii Clastries, 1957, C. maritimus Kieffer, 1924, C. parroti Kieffer, 1922, C. kibunensis Tokunaga, 1937, C. schultzei gr., C. subfasciipennis Kieffer, 1919, C. salinarius Kieffer, 1914 and C. pulicaris. The range of Culicoides species is shown in Table I. Out of the specimens collected, 2,283 breed in the samples taken from organic matter rich mud near the water reservoirs, 126 in moist soils with organic matter, 78 in rain pools, 71 in watering channels, 67 in sewage channel, 66 in dripping water, 49 in reed sites, 28 in garden watering channels, 23 in moist soils, five along the stream and two in mud near the dams. C. circumscriptus and C. festivipennis were seen as dominant species especially in organic matter rich mud near the water reservoirs. C. circumscriptus was found in a wide variety of habitats. C. maritimus was detected only in organic matter rich mud near the water reservoirs. It was observed that C. gejgelensis was found in soils dripping water, watering channels and moist soils, C. festivipennis and C. circumscriptus in sewage channels, garden watering channels and rain pools, C. festivipennis in reed sites and in sewage channels, C. odiatus only in mud near the dams as dominant species. The results of statistical analysis were shown in Table II. Culicoides specimens were collected in May (0.25 %), June (3.75 %), July (34.13 %), August (33.95 %), September (23.44 %) and October (4.50 %). DISCUSSION 18 Culicoides species found in the current study were mainly C. circumscriptus, C. festivipennis, C. shaklawensis, C. puncticollis, C. nubeculosus and C. riethi, and were reared in the samples taken from organic matter rich mud near water reservoirs. Nubeculosus group (C. nubeculosus, C. puncticollis, C. riethi) are able to reproduce especially in habitats with rich organic contents and organic content complications. The remaining Culicoides species possibly breed in completely different sites with completely different needs. Culicoides circumscriptus, C. gejgelensis, C. shaklawensis and C. festivipennis were cosmopolite species and grew in different breeding sites. While Culicoides circumscriptus and C. gejgelensis were seen in 10 out of 174

BREEDING SITES OF CULICOIDES SPECIES Breeding sites Mud rich in organic matters Moist near soil with Garden Mud Sites the water organic Moist Dripping Sewage Reed watering Watering Rain near along the Totally Species reservoirs matter soils water channels sites channels channels pools the dams stream (%) C. circumscriptus 1,201 62 3 7 20 2 6 1 47 1 48.25 C. festivipennis 506 9 40 41 16 18 22.52 C. shaklawensis 233 17 1 2 6 9.26 C. puncticollis 167 5 6.15 C. nubeculosus 56 22 1 1 2.86 C. riethi 47 4 1.82 C. gejgelensis 33 4 19 56 2 3 3 56 5 3 6.58 C. longipennis 18 2 2 2 0.86 C. flavipulicaris 8 1 0.32 C. maritimus 3 2 1 0.21 C. parroti 3 0.11 C. schultzei 3 0.11 C. subfascipennis 2 0.07 C. cataneii 1 1 1 2 3 0.29 C. odiatus 1 1 7 2 1 0.43 C. kibunensis 1 2 0.11 C. salinarius iii 1 0.04 C. pulicaris iii 1 0.04 N 2,283 126 23 66 67 49 28 71 78 2 5 100.000 Table I. Larval habitats for Culicoides species in Konya. Mud rich in organic matters Moist near soil with Garden Mud Sites the water organic Sewage Reed watering Watering Rain near along the Moist Dripping reservoirs matter channels sites channels channels pools the dams stream soils water Totally N 2,283 a 126 b 67 c 49 c 28 d 71 c 78 c 2 e 5 e 23 d 66 c 2,798 a, b, c, c, d, e: Breeding sites having in row different character are statistically important (P < 0.05). Table II. Numbers of Culicoides spp. found in various breeding sites and statistically analyses. 175

USLU U. & DIK B. 13 different habitats (Table I), Culicoides parroti, C. schultzei gr., C. subfasciipennis and C. maritimus breed in the samples taken from organic matter rich mud near the water reservoirs. C. pulicaris and C. salinarius breed in only mud moist with organic matter and in garden watering channels, respectively. These species were not observed in other breeding sites. Culicoides species were not reared in the samples obtained from the tree holes in this study. The reason for this might be that the year 2001, when the study was done, was dry in Konya with the resultant effect of dry tree holes. No Culicoides specimen was found in the samples taken from dung in this study either. The reason for this may be that the heap dung where the samples were taken was sprayed with insecticides according to farmers to prevent reproduction of flies. Many Culicoides species breed in organic matter rich mud near the water reservoirs. This result showed that the immature stages of Culicoides species need organic substances for growth. The reason why there were several species in this habitat was that breeding sites where the samples were taken had high organic matter, and that these habitats were water-saturated during summer. Most of the Culicoides species were found in organic matter rich mud near the water reservoirs with statistically significant difference compared to the rest of the habitats. While no statistically significant difference was found among sewage channels, reed sites, watering channels, rain pools and dripping water, it was statistically significant among the rest of the habitats. There was statistically significant difference for the moist soil with organic matter compared to other habitats. Although no significant difference was found between the garden watering channels and in moist soils without organic matter, these two habitats were significant different from the rest of the habitats. A small number of Culicoides species was found in mud near the dam sites and along the stream with no statistically significant difference between the two, which was significantly different from the rest of the habitats (Table II). Culicoides imicola, the main vector of bluetongue in Europen and Middle-East, was not reared in the samples taken from organic matter rich mud near the water reservoirs in spite of many Culicoides specimens (2,283 individuals) collected from the samples taken from the same habitat in this study. Other vector of bluetongue, C. obsoletus gr. was not reared in the samples taken from wet soil rich in organic matter and other breeding sites in this study. C. imicola was not found in any samples taken from all habitats because it is a tropical and sub-tropical species, and climatic conditions are not suitable for its breeding in Konya. In a study done to detect distribution of Culicoides species in Konya province, C. imicola was not detected, however C. obsoletus gr. was found relatively rare (Dik & Dinçer, 1992). C. imicola has not ever been seen in this region up to date. These findings supported that C. imicola could be reared in tropical and subtropical regions. Dik (1993, 1996) observed small numbers of C. schultzei gr., C. pulicaris, C. obsoletus gr. and C. imicola in Mediterranean and Aegean regions of Turkey and reported that these species are also rare in Turkey. On the other hand, C. schultzei gr. was caught in high numbers in Mediterranean region of Turkey (Jennings et al., 1983). Tilki & Dik (2003) reported that C. imicola and C. schultzei gr. were relatively common species in Iskenderun located in eastern coast of Mediterranean Sea. It was concluded that this might be due to climatic conditions and geographical characteristics of the region. As a vector of bluetongue, C. pulicaris breed in only mud moist with organic matter in this study. In addition to this, probable vectors of bluetongue as C. schultzei gr. have also a range of breeding sites. Three specimens of C. schultzei gr. were found in the samples taken from organic matter rich mud near the water reservoirs. A number of species may rear in different habitats as in different geographical regions with various climate and vegetation. On the other hand, finding breeding sites of vector species where they grow will make it easier to fight against these species. ACKNOWLEDGEMENTS This study is a part of the Ph. D. Thesis of Dr. Ugur Uslu and supported by Selcuk University Research Foundation (Project No: SUAF 2001-007). We express our appreciation to Prof. Dr. Yehuda Braverman, Kimron Veterinary Institute, Kimrom-Israel for reviewing, editing, helpful critiques and suggestions during the study and preparation of this manuscript. REFERENCES BLACKWELL A. 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