Fishfauna from the Lowland Mureş River (Romania) and the Floodplain

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Fishfauna from the Lowland Mureş River (Romania) and the Floodplain Fishfauna From the Lowland Mure ş River and the Floodplain Natural Park Area (Western Romania) FISHFAUNA FROM THE LOWLAND MURE Ş RIVER (ROMANIA) AND THE FLOODPLAIN NATURAL PARK AREA (WESTERN ROMANIA) Ilie C ătălin TELCEAN *, Diana CUP ŞA* *University of Oradea, Faculty of Science, Department of Biology, Oradea, Romania Corresponding author: Ilie C ătălin Telcean, University of Oradea, Faculty of Science, Department of Biology, 1 Universitatii Str., 410087 Oradea, Romania, tel.: 0040259408161, fax: 0040259408461, e-mail: [email protected] Abstract. The lowland Mure ş river has approximately 120 km in length, thereof more than 80 kilometers are comprised on the Mure ş Floodplain Natural Park that was established since the year 2007. This river stretch has different biotopes with lotic or lentic semblances with very characteristic and diverse fish fauna. Along the lowland main stream a system of canals, marshes and pools are connected. The results of repeated ichtiological surveys carried out during the years 1998 – 2001 and 2004 reveals that 48 fish species live in this river sector and other 2 species has uncertain presence. Most of the species from the river mainstream has maintain their former abundance (24 species) while other 16 fish species has increased their abundance. The burbot Lota lota and Zingel zingel becomes frequent in the lowland Mure ş, probably as consequence of their population renewal. The number of fish species that having undergone regression is less (4 species) and the exotic species present here are limited to 8 species. The major threatening factors in the lowland Mure ş represents the mineral aggregate extractions directly from the riverbed and the waste waters spill. Subsequent, the meanders and backwaters shortening or cutting down has a negative impact on the fish populations. Keywords: Fishfauna, Mure ş Floodplain Natural Park, changes in species range, Romania INTRODUCTION fishes have a large distribution in all of western Romanian rivers [22, 23, 24]. First records on the Mure ş river fishfauna were Due to the water pollution on the decades of 70’ provided by Rotarides [20] Jasfalusi [17] and B ăcescu and 80’ a number of species have become rare or [1]. These papers are devoted to the generally fishfauna extremely rare [19]. Some fishes such as Acipenser from the Transylvanian rivers and mention the Mure ş ruthenus, Abramis brama, Carassius carassius, river. More comprehensive data are furnished by Cyprinus carpio and Stizostedion lucioperca was Bănărescu [4, 5] in the two monograph works practically extinct species. Some moderate rheophilic dedicated to the systematic of bony fishes and to the species from lower Mure ş river such as Vimba vimba, lampreys. The data concerning the Mure ş fishfauna are Abramis ballerus and Gobio albipinnatus reached the the subject for successive papers [3, 4, 6, 7, 8, 9]. The upper stretches of the river [19]. Water pollution has a data mentions the species distributions along the main major influence on the river’s fishfauna [18, 21, 22, 27, Romanian rivers including also the river Mure ş. A 29]. The human impact on the fishfauna is now more special contribution concerning the species distribution diverse. Nearby the waste spill and the riverbed in the Mure ş river system is published in 1957 [6] and modifications, the fisheries activities can modify the later by Nalbant [19] who completed the species list fishfauna in the lowland rivers and canals [24]. During with ecological observations. The last paper represents the last decade the negative impact of water pollution the only recent published data concerning the Mure ş were diminished in the lower section of Mure ş. Thus fishfauna. It was mentioned more than 50 fish species some of the fish species has restored their former along the entire river. The fishfauna changes that is abundance. ascertain in the last decade are to motivate a new survey on this river. MATERIALS AND METHODS The subjects concerning the endemic fishes that live in different rivers from the Mure ş drainage system The fish species were identified during repeatedly are discussed in recent papers [10, 11, 19]. collecting trips which were conduct both on the river Morphological variation observed on the mainstream and the adjoined canals, marshes and representatives of Sabanejewia genus from different ponds. The study was performed in two steps: 1998- river stretch of Mure ş river was explained in several 2001 the investigations upon the fishfauna from the papers [6, 7, 10, 19]. The Mure ş river is the only that entire river and in the year 2004 investigations limited have no intergrades population between the two to the fish species which live in the lowland river. The loaches species Sabanejewia balcanica and S. ichtiological surveys were focused on the general bulgarica . In the other northwestern Romanian rivers fishfauna diversity and the species distribution. Thus in which the two loaches are distributed (Timi ş, Somes, we can observe the changes in species distribution Crisuri system), the lowland stretch has an intergrades along the river and the species abundance. zone. The present paper is referring to the results of the There are only four exotic fishes which are ichtiological surveys upon the lowland river fishfauna. mentioned in the lower Mure ş [19]. The recent The samples on the Mure ş Floodplain Natural Park investigations are proved that another 4 exotic fishes were located as follows: Bodrog, Pecica, Prundu Mare, are distributed on the lowland river both on Romanian Şeitin, N ădlac and Cenad. The upstream stretch was and Hungarian stretches [14, 15]. The presence of the investigated in two sites: near the Zam defile and near black bullhead Ictalurus melas on the small canals and the locality Mândruloc. pools was first mentioned from Crisuri rivers system The collecting methods were combined using both [18]. According to recent data it seems that the exotic the fishing nets (mesh size 5mm) and electro-narcosis 132 Analele Universit ăţ ii din Oradea, Fascicula Biologie Tom. XVI / 1, 2009, pp. 131-135 device (type IUP 12V, 4-10 A, 360W). The electric because of the habitats without swift streams. The fish fishing procedure was according to the CEN directive specimens were identified and recorded at the sampling [30] using pulsed direct current (PDC).The applied sites and then released. In some cases additional methods combine the boat fishing and fishing directly information from local competent people and anglers from the riverbanks. The stop nets were not necessary associations was used. Fig. 1. The sampling in the lowland Mure ş River RESULTS alburnus, Aspius aspius, Gobio kessleri and Rhodeus sericeus . A total number of 48 fish species were identified in Species identified on the mainstream river the lower sector of the Mure ş and neighboring canals between localities Pecica and Cenad and ponds (Table 1). Approximately a number of 29 of The river biotope is characterized here by the these species are widely distributed downstream to tendency of homogeneity on flowing velocity and the defile from the locality Zam until the locality predominance of sandy riverbed. The slopes especially Mândruloc (Figure 1). Others 19 fish species are those with vegetation such as Potamogeton and Trapa distributed predominantly on still waters and canals are densely populated by early stages of different from a limited sector in the lowland river. species. The crevices from the arduous shores are best Species identified on the mainstream river hiding places for many species. between localities Zam and Mândruloc On the mainstream of this river stretch were This river sector has characteristic a non identified 44 fish species which belongs to the homogenous flowing velocity and alternant pebbly and following taxa: Acipenseridae (one species), gravels bottoms. Cyprinidae (22 native and 5 exotic species); Cobitidae We identified here a total number of 26 fish (4 species), Siluridae (one species); Ictaluridae (2 species. The majority belongs to Cyprinidae family (13 species); Esocidae and Gadidae (each with a single are natives and 3 exotic). The others species are species), Percidae (7 species) Centrarchidae (one representatives of the Cobitidae family (2 species), species). Siluridae, Esocidae and Gadidae (each with a single Acipenseridae :: Acipenser ruthenus ; Native species), Percidae (3 species); Centrarchidae (one cyprinids : Rutilus rutilus, Leuciscus cephalus, species). Leuciscus idus, Scardinius erythrophthalmus, Aspius Native cyprinids : Rutilus rutilus, Leuciscus aspius, Alburnus alburnus, Blicca bjoerkna, Abramis cephalus, Scardinius erythrophthalmus, Aspius aspius, brama, A. ballerus, A. sapa, Vimba vimba, Pelecus Alburnus alburnus, Alburnoides bipunctatus, Abramis cultratus, Chondrostoma nasus, Leucaspius delineatus, ballerus, Vimba vimba, Chondrostoma nasus, Rhodeus Rhodeus sericeus, Gobio gobio, G. albipinnatus, sericeus, Gobio gobio, G. kessleri, Barbus barbus. Barbus barbus. Cyprinus carpio, Tinca tinca ; Exotic Exotic cyprinids : Carassius gibelio, Pseudorasbora cyprinids : Carassius gibelio, Pseudorasbora parva parva and Hypophthalmichthys molitrix . Cobitidae : Hypophthalmichthys molitrix , H. nobilis and Cobitis elongatoides, Sabanejewia balcanica ; Ctenopharyngodon idella ; Cobitidae : Misgurnus Siluridae : Silurus glanis ; Esocidae : Esox lucius ; fossilis, Cobitis elongatoides, Sabanejewia balcanica, Gadidae (Lotidae): Lota lota ; Percidae : Perca S. bulgarica ; Siluridae : Silurus glanis; Ictaluridae : fluviatilis,
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