First Record of Lernaea cyprinacea L. 1758 (Copepoda: Cyclopoida
Transcription
First Record of Lernaea cyprinacea L. 1758 (Copepoda: Cyclopoida
BIHAREAN BIOLOGIST 9 (1): 44-46 Article No.: 141130 ©Biharean Biologist, Oradea, Romania, 2015 http://biozoojournals.ro/bihbiol/index.html First Record of Lernaea cyprinacea L. 1758 (Copepoda: Cyclopoida) on Cyprinion macrostomus Heckel, 1843 from Eastern Anatolia, Turkey Mustafa KOYUN1,*, Mehmet ULUPINAR2 and Abdullah MART1 1. Department of Biology, Faculty of Arts and Sciences, Bingöl University, 12000, Bingöl, Turkey. 2. Department of Fisheries, Faculty of Agriculture, Bingöl University, 12000, Bingöl, Turkey. * Corresponding author, M. Koyun, E-mail: [email protected] Received: 26. August 2014 / Accepted: 22. September 2014 / Available online: 10. April 2015 / Printed: June 2015 Abstract. This study was conducted while working on the fish population in the Murat River in Eastern Anatolia, Turkey. During the field surveys, Lernaea cyprinacea L. 1758, an ectoparasitic copepod species was detected on the soft parts the dorsal and anal fins of Cyprinion macrostomus. It was concluded from a review of the literature that no data on the parasite host was not reported in previous studies conducted in the all over the world. Key words: Murat River, Cyprinion macrostomus, Lernaea cyprinacea, Copepoda. Introduction Anchor worm, Lernaea cyprinacea L. 1758, is a parasitic copepod that burrows into the skin of freshwater fishes. It has anchors that can penetrate the tissues below the skin of the host fish. In summer and spring, when water temperatures exceed 14–15 °C, copepod larvae attach to the gills of fish and may cause their death (Ekingen 1983, Koyuncu & Donmez 2006). Lernaea species have nine stages in the life cycle, including three free-living naupliar stages, five copepodid stages and one adult stage. After mating on the fish host, the males die and females metamorphose and insert their anterior body into the host tissue and then produce eggs (Nagasawa et al. 2007, Barson et al. 2008). Anchor worm can cause lernaeosis, also known as anchor worm disease, which results in hemorrhagic ulcers at the attachment site. The species can thereby cause the death of the host due to secondary infections and massive bleeding (Wellborn & Lindsey 1970, Khalifa & Post 1976, Kabata 1985, Hoffman 1999, Kupferberg et al. 2009). L. cyprinacea is the most common species that belongs to genus Lernaea among approximately 40 species in North America, South- and Southeast Asia, Africa and Europe (Acosta et al. 2013). The species is also known to parasitize more than 100 hosts (Kabata 1979, 1985, Hoffman 1999). L. cyprinacea recorded in Turkey and some European countries as Germany, France, Italy and Scandinavia. The parasite probably originates from Asia and spread to different parts of the world via the movement of aquarium species (Robinson & AvenantOldewage 1996, Innal & Oldewage 2012). It has also spread from the south of West Siberia to Japan throughout Central Asia. L. cyprinacea can grow in water temperatures of 23–30 °C displaying slightly thermophilic characteristics. Mature female parasites also reported in freshwater fish, frog and salamander in North America (Bauer 1959, Yashuv 1959, Hoffman 1967, Kupferberg et al. 2009). Cyprinion macrostomus, which is stated as a host in our study, is a Cyprinid fish that is used in thermal springs to treat dermatological diseases (Arkhipchuk 1999). It has a limited natural range, but has been reported in one part of Euphrates River which is within the borders of Iran (Coad 1996); Topardici and Kalkim Rivers in Sivas; Kangal thermal source; Diyarbakır, Karakaya, Devegeçidi Dams; and the Tigris River from Turkey (Kuru 2004, Daştan et al. 2012). This species known as Tigris king fish and Beni fish in Turkish which was recorded from Turkey by Kuru (2004) under the name C. macrostomus. Distribution on South-eastern Turkey and endemic to eastern Mediterranean, Asi River, Euphrates and Tigris river systems. Conservation status is endangered and sensitive to human activities (Fricke et al. 2007). No faunistic record exists in the Murat River. This parasite was not encountered in previous studies on fish parasites in Murat River (Koyun 2011a,b,c, 2012). And also this study is the first record of L. cyprinacea parasitizing C. macrostomus. Materials and Methods Samples of C. macrostomus was caught with gill nets (22 mm width) and casting nets, from the area of Garip village (Bingöl, 380 77´ 74” N, 40o 57´ 70” E, 992 m) on one of the small stream reaches of Murat River. L. cyprinacea was detected on the dorsal and anal fins on only five samples. It has been examined with stereoscopic microscope to identify the occurrence of Lernaea. The parasites were removed with a sharp implement. First, they were killed in formaldehyde solution of 4% (not boiled) then preserved in 70% ethanol. The parasite was photographed as totally (supplementary material 1). Results During this study, L. cyprinacea was observed on the skin of 5 fishes (5% prevalence) captured at one station on the Murat River at on January, 2012. Infection intensity was one, and Abundance 0.05, and located at soft part of the dorsal and anal fins regions. This parasite was not found on the Murat River at any of the remaining sampling stations where this fish was captured. Despite a lot of fish examination only 5 specimens lernaepodid were found. In present study we focused on the lernaepodid copepod (L. cyprinacea) an ectoparasite on the dorsal and anal fins of C. macrostomus. Previous reports of the parasite fauna of C. macrostomus include trematodes, nematodas and monogeneans, (Rahemo & Kasim 1979, Rahemo1980). However, C. macrostomus has not been recorded previously as a host for L. cyprinacea. As such this finding represents the first record of L. cyprinacea parasitizing C. macrostomus at its natural range (Table 1). The Murat River, Cyprinion macrostomus, Lernaea cyprinacea, Copepoda 45 Table 1. List of Lernaea cyprinacea records from different host species from all over the world. Host(s) of Lernaea cyprinacea Country References Carassius carassius, ornamental fish, Chondrostoma nasus, Gambusia affinis Turkey Tekin & Kir 2005, Koyuncu & Dönmez 2006, Kir 2007, Demir & Karakişi 2014, Innal & Oldewage 2012 Labeo altivelis, Oreochromis macrochir, Ctenopharyngodon idella, Oreochromis mossambicus, Oreochromis placidus, Tilapia rendalli Zimbabwe Dalu et al. 2012 Alburnus alburnus, Barbus lacerta, Capoeta aculeate, Capoeta damascina, Iran Capoeta aculeate gracilis,Carassius carassius, Chalcalburnus chalcoides, Chalcalburnus mossulensis, Chondrostoma orientalis, Ctenopharyngodon idella, Cyprinus carpio, Leuciscus cephalus, Hypophthalmichthys molitrix, Mastacembelus mastacembelus, Pseudorasbora parva, Aphanius vladykovi, Aristichthys nobilis, Chondrostoma regium, Gobio sp., Leuciscus persidis, Schizothorax sp., Pseudorasbora parva Jalali 1987, Jalali et al. 1995, Barzegar & Jalali 2009, Pazooki & Masoumian 2012 Natropis girardi, Macrhybobsis tetranema Mexico Durham, et al. 2002 Cyprinus carpio, Carassius carassius, Idus idus, Rutilus rutilus Britain Fryer 1968 Barbus graellsii, Barbus haasi, Cyprinus carpio , Leuciscus cephalus, Chondrostoma toxostoma, Parachondrostoma miegii Spain Sterling et al. 1995, Gutiérrez-Galindo & Lacasa-Millán 2005 Gambussia affinis Italy Benedetti et al. 1989 Astyanax bimaculatus Brazil Magalhães 2006 Silurus asotus Arapaima gigas, Anguilla japonica, Carassius auratus, Japan Carassius auratus langsdorfii , Carassius auratus subsp., Carassius cuvieri, Ctenopharyngodon idellus, Cyprinus carpio, Gnathopogon elongatus suwae, Hemibarbus labeo, Oncorhynchus mykiss, Pseudobagrus tokiensis, Silurus asotus , Plecoglossus altivelis, Pungitius pungitius, Lepomis macrochirus , Micropterus salmoides, Pterophyllum scalare, Chaenogobius macrognathos, Gymnogobius Tridentiger obscurus Ogawa 2004, Nagasava et al. 2007 Mugil cephalus, Gambussia affinis, Clarias lazera Israeli Yashuv 1959, Paperna 1964 Barbus altianalis, Lates albertianus Uganda Thurston 1969, 1970 Ctenopharyngodon idella Pakistan Tasawar et al. 2009 Catla catla, Labeo rohita, Catla catla, Ctenopharyngodon idella, Hypophthhalmichthys moltrix Pakistan Iqbal et al., 2012, Kanwal et al. 2012 Galaxias occidentalis, Edelia vittata , Bostockia porosa, Tandanus bostocki, Carassius auratus, Gambusia holbrooki, Phalloceros caudimaculatus W. Australia Marina et al. 2008 copepods that recorded in our study were adult female; they were anchored to host fins and feeds on the epithelial cells and mucus of the host, characteristically raising blisters on the fin surface. Discussion According to Coad (1996) C. macrostomus is a native and endemic fish for Tigris-Euphrates basin, especially in Turkey, Iran and Syria freshwater system. This present report is the first diagnosis of Lernaea cyprinacea in Murat River at Euphrates basin. The implication of this parasitosis for C. macrostomus is not known in Turkey and is the first report of L. cyprinacea in mentioned fish. This parasite was not previously encountered in C. macrostomus in studies conducted in Turkey and other at all; previous studies did not focus on this parasite, and C. macrostomus is present only in the East and Southeast Anatolia regions in Turkey. In literature, there are two species known as doctor fish and C. macrostomus is one of these species. Therefore, it is important to investigate the characteristics of C. macrostomus in detail. This study will provide significant contribution to determination of these fish parasites. The critical situation of this fish, which has medical importance, is given as an endangered in Turkey (Dagli & Erdemli 2009). This species of parasite shows a cosmopolitan distribution; it mostly parasitizes Cyprinidae, whereas other fresh- water fish species host other parasites. However, as is seen in Table 1, there is no data on C. macrostomus recorded in various countries at different times. According to Koyuncu & Dönmezer (2006) this parasite was reported on the gills of the fish, but in our study observed on the fins. This means, place of this parasite sometime changing. Anchor worm infections usually result in a single parasite per host fish in flowing rivers and streams, causing a little damage, but in closed environments severe infestations often result (Demaree 1967). 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