BIOTROPIA Vol. 23 No. 1, 2016: 1 - 9 DOI: 10.11598/btb.2016.231 . .362 ICHTYOFAUNA AT CIJALU RIVE R, CILACAP RE GE NCY CE NTRAL JAVA PROVINCE , INDONE SIA AGUS NURYANTO, DIAN BHAGAWATI, M. NADJMI ABULIAS and INDARMAWAN Faculty of Biology, Jenderal Soedirman University, Purwokerto 53122, Indonesia Received 22 January 2014/Accepted 21 June 2016 ABSTRACT Cijalu River is located in Western Cilacap Regency of Central Java Province . The river runs through forestry, housing and farming areas. This condition leads to a prediction that the river has been altered on its physico-chemical characteristics causing the river to be inhabited by a variety of fish species. This study aimed to collect data about fish species inhabiting Cijalu River and its distribution. A survey method has been done with clustered random sampling technique. The river was divided into three different areas, i.e. upper-, middle- and downstreams. Species diversity was measured as the number of species, while distribution was measured as the presentation of fish species in each site. Nineteen fish species of 10 families were identified from Cijalu River. The 10 families were Anabantidae, Bagridae, Balitoridae, Channidae, Cichlidae, Cyprinidae, Loricariidae, Osphronemidae, Poecilidae and Sisoridae . Cyprinidae was the family having the highest number of species (6 species) , followed by Bagridae ( 3 species), Channidae (2 species) and Osphronemidae (2 species). The remaining respective families were represented by one species. A complex pattern of fish distribution was observed during the study. Glyptothorax platypogon and Channa gacua were only found at the upper-streams, while Anabas testudineus was obtained in downstreams. The other remaining species could be observed either from the middle- to downstreams, or even from upper- to downstreams. Different pattern of species distribution could be caused by physico-chemical characteristic s variation from upper to lower parts of the river, especially water velocity and substrate types. Keywords: Ci ja lu River , distribution, diversi ty , fish INTRODUCTION to global issue on biodiversity and biodiversity initiative (Nguyen & De Silva 2006) . Diversity indicates the presence of species at In general, biodiversity initiative focused on certain ecosystem. In macrotaxonomy, diversity terres trial ecosystem. However, at present days, measurement is a measure of number of species aquatic ecosystem becomes among the most in an area, whereas in ecology, diversity is discussed topics , especially about coral reef and represented by species number and its wetlands ecosystems. Later on, resear cher s are abund ances. High species diversity prove s that an also interested to study biodiversity aspect of ecosystem is in an equilibrium state and plays freshwater ecosystem including freshwater fish important role in keeping ecosystem in an diversity (Nguyen & De Silva 2006). Previous equilii br um condition. According to Odum report showed that a total of 13,000 freshwater (1971) high diversity is show n by no dominant fish species have been described and belong to species in an ecosystem. 2,513 genera (Dud geon et al. 2006; Leveque et al. Biodiversity is an integral part of nation 2008). development after Brundtland report was first The majority of freshwater fish species inhabit published in 1987 (UNEP 1987). High support of tropical areas, mainly in Asia (Nguyen & De international community on that report and Silva 2006). Asia harbors approximately 121 followed by global consultation has led to the freshwater fish families, higher than those in establishment of the Convention on Biological freshwater ecosystems in Africa and Latin Diversity in 1994, which provides guidance related America which have only 50 and 55 fish families, respectively.On species level, 28 up to 32% of the * C orresponding author: [email protected] 13,000 described freshwater fish species were 1 BIOTROPIA Vol. 23 No. 1, 2016 recorded from Asia with approximately 462 within 10 families . In Cileumeuh River, spesies are threatened. The number is equivalent Cypr inidae was the speciose family with 10 to 17.5% of total number of threatened species in species and followed by Bagridae with four the world (Le vequ e et al. 2008). A sum of 66 spec ies (Nuryanto et al. 2012 ). Nuryanto et al. species were critically endan gered or end an gered (2015) also recorded a total of 19 species and nine and 32 species of them belong to Cyprinid . families from Cikawung River. Indonesia is among 12 Asian countries with the Cijalu River is located in Western Cilacap highest number of threatened fish species Regency, Central Java Province . Administratively, (Nguyen & De Silva 2006). this river belongs to Majenang District with its High diversity of fish species in Asia is headwater located in Padontelu Mountains. especially found in big rivers and their floodplains Cijalu River empties into Cileumeu h River. Cijalu (Welcomme 2000; CBD 2003; Coates et al. 2003). River belong s to Citanduy Watershed together In detail, Asia's freshwater fish is dominated by with Cileumeuh and Cikawung Rivers. There have Cyprinid group (±1 , 000 spesies) and followed by been no data on fish diversity and it s distribution Balitoridae and Cobitidae (±400 species, recently, at Ci ja lu River. In addition to the fact that Cijalu Balitoridae is divided into Balitoridae, River is subjected to several impacts from Gastromyzontidae, Ellopostomatidae, forestry, farming and house waste which alter the Vaillantellidae, Barbuccidae, Serpenticobitidae physico-chemical characteristics of the river, and Nemacheilidae; while Cobitidae become s Cijalu River is overfished. Therefore , it is Cobitidae and Botiidae ( Kottelat 2012 ;) Gobiidae important to study fish diversity at Cijalu River to (300 species), catfishes Bagridae (±100 species) develop database on freshwater fish species in and Osphronemidae (85 species) (Nguyen & De Banyumas Region which is important for further Silva 2006). Specifically, Kar et al. (2006) also study, such as conservation strategy. This study reported that Cyprinidae is a dominan t freshwater aimed to collect data on fish diversity and fish family in India. distribution at Cijalu River, Cilacap Regency . Previous studies reported freshwater fish diversity in Africa (Albaret et al. 2004; Leveque 1997; Harrison & Whitfield 2006) and Europe MATE RIALS AND ME THODS (Collares-Pereira et al. 2002). Several studies had also been done in Indonesia, however, those Clustered random sampling technique was studies were mostly performed outside of Java; performed by dividing Cijalu River into three such as in Kalimantan (Haryono 2004; Sulistyarto clusters i.e. upper - , middle - and downstream et al. 2007) and Sumatera (Duya 2008). Studies in (Fig. 1), based on substrate types . Fish samples smaller rivers in Java have also been done in were collected at eleven sampling sites: five at Cileumeuh and Cikawung Rivers. A study in upper-, three at mi ddle- and three at downstreams Cileumeuh River found a total of 2 2 fish spec ies using 12 Volt electric shocker and nets with 0.5, Figure 1 Sampling sites across Cijalu River (108o 04' and 109 oo 30', 7 03' and 7 o 52') Notes : 1-11 = sam pling site numbers = border among river's parts 2 Ichtyofauna at Cijalu River , Central Java Province, Indonesia – Agus Nuryanto et al. Table 1 Physic o -chemical parameters mea surement methods Physico-chemical parameter Measurement methods Water depth (m) Sechi disk Light intensity (m) Sechi disk Water temperature (°C) Thermometer Water pH Universal pH papers Carbon dioxide (CO2) APHA 1985 Water velocity (m/sec) Linear measurement Substrate Visual 0.75 and 1 inch in mesh sizes. Sampling was which found 40 species (Sjafei et al. 2001) . performed from April to July 2012. Electric- Cimanuk River was chosen as the compar ison shocker and 0.5 inch nets were used during the because Cimanuk River is located in the same sampling in the upper-stream, whereas 0.75 and 1 biogeographic region and is in the same island inch nets were used at the middle- and down- with Cijalu River. D ifferen t result s between this streams. Sampling efforts were performed for one study at Cijalu River and the study at Cimanuk hour netting and electroshocking at each site . River could be caused by different ecological Biological variables and physico-chemical characteristics such as river length, river size and characteristics were examined during the study. annual water volumes. Based on survey at Cijalu Biological variables measured were number of River in 2012 and at Cimanuk River in 2011 fish species (S) and fish distribution in Cijalu (Nuryanto & Sugiharto 2011), Cijalu River is River . Physic o -chemical parameters measured shorter and smaller than Cimanuk River. Cijalu were water depth, light intensity, water River is only about 40 km in length, spanning only temperature, water acidity (pH), ca rbon dioxide, from northern to southern part of Majenang water velocity and river substrate . Methods used in District in Cilacap Regency, whereas Cimanuk measuring physico -chemical parameters are River has more than 100 km in length spanning summarized in Table 1 . from Garut Regency up to the offshore of Java Fresh fish samples were directly preserved in Sea in Indramayu Regency, West Java Province . labelled plastics bag filled with 70% ethanol. Moreover, Cijalu River is appro ximately 40 m in Direct fixation using eth a nol was carried out due width, while Cimanuk River reaches 100 m in to technical difficulties in obtain ing formalin. width at the lower part. In addition, Cimanuk Upon arrival in the laboratory, the samples were River has more constant annual water volumes washed under running water and the used soaking than Cijalu River. According to Kottelat et al. ethanol was replaced by the fresh 70% ethanol. (1993) longer and wider ecosystems are usually For permanent preservation, the samples were assumed to have higher microhabitat variation fixed inside bottles containing fresh 70% ethanol than smaller and shorter areas. H igh habitat (diluted from 100% pro-analysis ethanol). variation supports high variety of inhabitants.