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BIODIVERSITY AND BIOGEOGRAPHY J. Limnol., 2013; 72(s2): 327-344 DOI: 10.4081/jlimnol.2013.s2.e16 The groundwater-dwelling fauna of South East Asia STYGOBIONTS Anton BRANCELJ,1,2* Chaichat BOONYANUSITH,3 Santi WATIROYRAM,4 La-orsri SANOAMUANG3,5 National Institute of Biology, Večna pot 111, 1000 Ljubljana; 2Faculty for Environmental Sciences, University of Nova Gorica, Vipavska c. 13, 5000 Nova Gorica, Slovenia; 3Applied Taxonomic Research Center, Faculty of Science, Khon Kaen University, Khon Kaen 40002; 4Division of Science, Faculty of Liberal Arts and Science, Nakhon Phanom University, Nakhon Phanom 48000; 5Faculty of Science, Mahasarakham University, Maha Sarakham 44150, Thailand *Corresponding author: anton.brancelj@nib.si 1 INTRODUCTION ia l Received: February 2013. Accepted: September 2013. us Key words: Caves, groundwater fauna, karst, Southeast Asia, stygobionts. on co m m er c More than half of the stygobionts (i.e. obligate groundwater dwellers) reported globally are known from Europe. In total, there are about 3800 known stygobionts worldwide and about 2000 taxa are reported from groundwater in Europe (Gibert and Culver, 2009). This is the result of long-term research in fissured (i.e. karstic) and porous (i.e. alluvium, interstitial) aquifers in Europe. The first information related to stygobionts arose from caves and karstic springs, because animals there are relatively larger, more noticeable and easier to collect than animals in porous aquifers. Records were made sporadically as a result of occasional visits to caves or investigation of wells and were focussed mainly on larger body-sized groups like Isopoda, Amphipoda, Decapoda and Pisces. Some rare records on micro-crustacea from caves or wells have been existing for a long time as well [Tab. 1; after Botosaneanu (1986)]. Among the first records of groundwater fauna were those of Copepoda from the drinking water system of St. Petersburg from 1866 (although specimens recorded there were actually stygophiles) and of Bathynellaceae from a similar environment in Prague (in 1882) (Botosaneanu, 1986; Camacho, 1992). Among the first described stygobionts (some of them were actually stygophiles) were amphibians (Proteus anguinus Laurenti, 1768), fish [Monopterus albus (Zuiew, 1793)] and amphipods [Gammarus minus (Say, 1818), Niphargus puteanus (C.L. Koch, 1836)], followed by N e on ly ABSTRACT Groundwater fauna consists of organisms that are adapted to live their whole life-time in different types of groundwater (=aquifers): with fissured (karstic) and porous (alluvium) types as the most common. About 3800 species of obligate groundwater species (stygobionts) have been recorded worldwide and 2000 of them from groundwater in Europe. Before 1970, 19 species of stygobionts were known from Southeast Asia. After 1980, the number of stygobionts from this region started to increase, and, at present, 122 stygobionts are known here. Most of them are crustaceans, with the Copepoda, Isopoda, Amphipoda and Decapoda as the most abundant groups. Intensification of research on groundwater fauna can considerably increase the total number of stygobionts known from the region, which could rises up to several times the current tally if the intensity of research was comparable with that in Europe. crabs and shrimps [Orconeces pellucidus (Tellkampf, 1844), Troglocaris anophthalmus (Kollar, 1848)]. In contrast, stygobiotic Calanoida, also present in Southeast (SE) Asia, have been found just recently [Microdiaptomus cokeri (Osorio Tafall, 1942)] (Tab. 1). The main reason for their late discovery, is the generally rather low numbers of freshwater stygobiotic Calanoida (Brancelj and Dumont, 2007). The intensity of research related to groundwater fauna increased after the First World War and since then it has been increasing, not only in Europe but worldwide. Most recently, among the most intensive projects on groundwater and its fauna, which included both types of aquifers, was the project Protocol for the Assessment and Conservation of Aquatic Life in the Subsurface (PASCALIS; available from: http://pascalis-project.com/) that was conducted in Europe during the period 2002-2005 (Deharveng et al., 2009; Stoch and Galassi, 2010). The project revealed that even in areas with intensive and continuous research of groundwater fauna there was still a big potential for discovering new species. In six European regions with a total area of 11,777 km2, 217 species were known before project PASCALIS, and after the project the number increased to 379, with 109 new species for those six regions, including some that were new to science (Deharveng et al., 2009; Dole-Olivier et al., 2009). For example, intensive and systematic sampling of porous aquifers along the rivers, which were included in the PASCALIS project, resulted in a discovery of rich population of two 328 A. Brancelj et al. Tab. 1. List of the first three stygobiotic species of each higher taxonomic group described and present elsewhere in the world. Representatives of higher taxonomic groups are also present in Southeast Asia but with different species [data from Botosaneanu (1986)]. Ostracoda 4 Pseudocandona eremita (Vejdovsky, 1880) Central and South Europe Copepoda Calanoida 5 Microdiaptomus cokeri Osorio Tafall, 1942 Mexico 11 12 13 14 Sphaeromicola topsenti Paris, 1916 France Pseudocandona zschokkei (Wolf, 1919) West and Central Europe Speodiaptomus birsteini Borutsky, 1962 Krim peninsula (Ukraine) Ridgewayia marki (Esterly, 1911) - anchialine, Bermuda islands Nitocrella hirta Chappuis, 1923 Europe Anaspides tasmaniae (Thomson, 1893) Tasmania (Australia) Bathynella chappuisi Delachaux, 1920 Europe Spahaeromides raymondi Dollfus, 1897 France Faucheria faucheri (Dolphus and Virè, 1900) France Caecosphaeroma virei Dollfus, 1896 France Caecosphaeroma burgundum Dollfus, 1896 France Cyanthura curassavica Stork, 1940 Central America Cyanthura milloti Chappuis, Delamare Deboutteville and Paulian, 1956 Reunion island Caecidotea nickajackensis Packard, 1881 Tennessee (USA) Asellus hilgendorfi Bovallius, 1886 Japan Microcerberus remanei Chappuis and Delamare, 1952 Mediterranean area Microcerberus delamarei Remane and Siewing, 1953 Brazil Neophreatoicus assimilis Chilton, 1884 New Zealand Phreatoicoides gracilis Sayce, 1900 Australia To be continued on next page. m Anthuridea Cruregens fontanus Chilton, 1881 New Zealand Asellota Caecidotea stygia Packard, 1871 Central part of USA Microcerberidae Microcerberus stygius Karaman, 1933 Macedonia Phreatoicidea Phreatoicus typicus Chilton, 1882 New Zealand Eucyclops terras (Graeter, 1907) Switzerland Bryocamptus pyrenaicus (Chappuis, 1923) France, Slovenia co m on Sphaeromatidae Monolistra caeca Gerstaecker, 1856 Slovenia N Isopoda Cirolanidae 9 Cirolanides texensis Benedict, 1896 Texas (USA) 10 Trichodrilus cantabrigensis Beddard, 1908 United Kingdom Acanthocyclops venustus (Norman and Scott, 1906) Europe Harpacticoida Parastenocaris fontinalis Schnitter and Chappuis, 1915 Europe Syncarida 8 Bathynella natans Vejdovsky, 1882 Europe Trichodrilus intermedius Fauvel, 1903 France ia l 7 Cyclopoida Diacyclops languidoides (Lilljeborg, 1901) Europe Criconema minor (Scheider, 1940) Slovenia er c 6 Thalassoalamus aquaedulcis Schneider, 1940 Slovenia on ly Oligochaeta 3 Trichodrilus pragensis Vejdovsky, 1875 Czech lands Phagocata olivacea (Schmidt, 1862) Southeast Adriatic coast e Nematoda 2 Pseudorhablolaimus limnophilus Soos, 1937 Hungary, Austria Dendrocoelum nausicae Schmidt, 1861 South Europe and Anatolia us Turbellaria 1 Phagocata vitta (Duges, 1830) Europe, the Alps, Balkan Groundwater-dwelling fauna of SE Asia 329 Tab. 1. Continued from previous page. 17 18 Melitidae Eriopsia elongata (Bruzelius, 1859) Europe, USA Niphargidae Niphargus puteanus (C.L. Koch, 1836) Germany, Switzerland Crangonyctidae Crangonyx subterraneus Bate, 1859 West and Central Europe Thermosbaenacea 19 Thermosbaena mirabilis Monod, 1924 Tunisia N Coleoptera 24 Siettitia balsetensis Abielle de Perrin, 1904 France Pisces 25 Taenioides anguillaris (Linnè, 1758) China Niphargus longicaudatus A. Costa, 1851 Italy Stygobromus tenuis (Smith, 1874) East coast of USA Bactrurus mucronatus (Forbes, 1876) Central part of USA Monodella argentarii Stella, 1951 Italy us Caridina japonica De Man, 1892 Japan Orconeces inermis Cope, 1872 Kentucky, Indiana (USA) Cambarus hamulatus (Cope, 1881) Alabama, Tennessee (USA) Sesarmoides jacobsoni (Ihle, 1912) Central Java, Indonesia Sesarmoides verleyi (Rathbun, 1914) Jamaica Frontipodopsis staheli Walter, 1919 Central and South America Sczizobates disjunctus (Walter, 1925) Argentina Siettitia avenionensis Guignot, 1925 France Uvarus chappuisi (Peschet, 1932) Burkina Faso Monopterus albus (Zuiew, 1793) Mjanmar, China, Japan Trypauchen vagina (Bloch and Schneider, 1801) Taiwan, China ia l Barbouria cubensis (Von Martens, 1872) Cuba m on Acarina Hydrachnida 23 Wandesia thori (Schecthel, 1912) Europe Niphargus stygius (Schiödte, 1847) Slovenia er c Reptantia Orconeces pellucidus (Tellkampf, 1844) Tennessee (USA) Brachyura Thelphusula bidiens (Lanchester, 1900) Sarawak, Borneo Pseudoniphargus africanus Chevereux, 1901 Algeria co m 22 Eriopsella sechellensis (Chevreux, 1901) Seychelles Monodella stygicola Ruffo, 1949 Italy Decapoda Natantia 20 Troglocaris anophthalmus (Kollar, 1848) Slovenia, Italy 21 Sarathrogammarus guernei (Chevreux, 1889) Azores (Portugal) e 16 Rhipidogammarus rhipidophorus (Catta, 1878) Mediterranean area on ly Amphipoda Gammaridae 15 Gammarus minus Say, 1818 Central part of USA species of stygophilic groundwater dwelling cladocerans. In the past, both species were considered to be very rare, but the many specimens collected during the project enabled a new genus – Phreatalona, to be established (Van Damme et al., 2008). Other parts of the world remained rather cold spots for a long time. Until 1964, information on relatively rich troglobiotic/stygobiotic fauna existed only for Europe and the SE USA. Other parts of the world, including SE Asia, remained very poorly known, even three decades later (Holsinger, 1993). Actually, most of the information on cave-dwelling fauna from SE Asia was limited to terrestrial species (Deharveng, 2004). Among stygobiotic fauna, at least one representative from each main group 330 A. Brancelj et al. Historical overview and present status of stygobionts in Southeast Asia e on ly At the beginning of the 20th century only six stygobionts were known from SE Asia; this increased to 20 species in 1970 and reached 22 species in 1986, when the first list of global and regional stygobiotic fauna was compiled (Tab. 3; Botosaneanu, 1986). In the period between 1986 and 2001 the number of newly recorded species increased by 57 species (Juberthie and Decu, 2001) and in 2012 reached a total number of 122 species included in 74 genera (Fig. 1). In this number are also species from anchialine caves and some species which probably belong to the stygophiles. Most of the newly recorded species were also new to science and thus described in adequate taxonomic papers. The highest number of stygobionts so far recorded is from Thailand (36 species) and the Philippines (35 species), followed by Indonesia and Malaysia (20 and 19 species, respectively), Vietnam (9 species), Cambodia (3 species), Laos (2 species) and Myanmar (1 species) (Tabs. 3 and 4). Most of the species are recorded from a single location or, less frequently, from several in close proximity to each other (usually several kilometres). So far, only three species from SE Asia are known from more than one country (Attheyella vietnamica Borutzky, 1967: Vietnam and Thailand; Theosbaena cambodjiana Cals and Boutin, 1985: Cambodia and Thailand; Parhippolyte uveae Borradaile, 1899: Indonesia and Philippines). N on co m m er c Southeast Asia includes the countries of Cambodia, Laos, Burma (Myanmar), Thailand, Vietnam and peninsular Malaysia. It also includes the maritime areas of SE Asia: Brunei, East Malaysia, East Timor, Indonesia, the Philippines and Singapore (Wikipedia, 2013). Total land area is about 4,300,000 km2, 408,000 km2 (9.7%) of which is karstic (Day and Urich, 2000; Tab. 2). Apart from the karstic areas, there are also vast alluvial areas, with an array of potential habitats for stygobiotic organisms (Gibert et al., 1990). Data on stygobiotic fauna from the countries of SE Asia was collected from various literature sources. For the period up to 1986, the source was Stygofauna Mundi (Botosaneanu, 1986), where all relevant literature on groundwater fauna worldwide is presented till 1986. For the period between 1986 and 2001 the source was Encyclopaedia RESULTS us METHODS Biospeleologica (Juberthie and Decu, 2001). After 2001, individual papers on fauna from SE Asia were used. To present the intensity of research on stygofauna in SE Asia, a cumulative curve over time was constructed by adding each record of a new stygobiotic species in the region to the previous, already recorded taxa. ia l of stygobionts so far recorded in SE Asia had already been known from elsewhere before the beginning of the 20th century (Tab. 1). This is an additional indication that stygobiotic fauna in SE Asia was not adequately sampled since relatively recently, i.e. after the 1970s. More recent inventories revealed that about 160 stygobiotic taxa are known from SE Asia and the Indian subcontinent combined (Gibert and Culver, 2009). From the Indian sub-continent, about 50 stygobionts are known; there, several new stygobionts – especially among the micro-crustaceans (Copepoda and Syncarida) – were recently found to live in porous aquifers (Ranga Reddy and Defaye, 2008; Ranga Reddy et al., 2008; Ranga Reddy and Schminke, 2009). In the present paper a more detailed analysis of stygobiotic fauna in SE Asia is presented, with special emphasis on the most recent investigation of epikarst in Thailand and Vietnam. Tab. 2. Extent of karstic area per country in Southeast Asia [after Day and Urich (2000)]. Country Cambodia Indonesia Laos Malaysia Myanmar Philippines Thailand Vietnam Total Country area (km2) 181,035 1,904,569 236,800 131,598 676,578 300,000 513,120 331,689 4,275,389 Karstic area (km2) (%) 20,000 145,000 30,000 18,000 80,000 35,000 20,000 60,000 408,000 11.0 7.6 12.7 13.7 11.8 11.7 3.9 18.1 9.7 Fig. 1. Cumulative number of stygobiotic taxa recorded in Southeast Asia from 1820 up to 2012. Elaphoidella jaesornenis Watiroyram, Brancelj and Sanoamuang, 2013 Elaphoidella margaritae Pesce and Apostolov, 1985 (Pesce and Apostolov, 1985) Elaphoidella namnaoensis Brancelj, Watiroyram and Sanoamuang, 2010 Elaphoidella thailadensis Watiroyram, Brancelj and Sanoamuang, 2013 Elaphoidella vietnamica Borutzky 1967 Epactophanes philippinus Bruno and Cottarelli, 1999 (Bruno and Cottarelli, 1999) Fierscyclops solaris Boonyanusith, Brancelj and Sanoamuang, 2013 Fierscyclops tanasosriensis Boonyanusith, Brancelj and Sanoamuang, 2013 Boholina crasicephala Fosshagen, 1989 Boholina purgata Fosshagen, 1989 Bryocyclops maewaensis Watiroyram, Brancelj and Sanoamuang, 2012 Elaphoidella bidens decorata (Sars, 1904) Copepoda (22 taxa) Asiacaris dispar Cottarelli, Bruno and Berera, 2010 (Cottarelli et al., 2010) Attheyella (Canthosella) vietnamica Borutzky, 1967 Ostracoda (2 taxa) Batucypretta paradoxa Victor and Fernando, 1980 Candonopsis putealis Klie, 1932 Oligochaeta (1 taxon) Haplotaxis glandularis Yamaguchi, 1953 Nematoda (1 taxon) Dorylaiumus selengorensis De Man, ? x x x on N x co m x x x x x x ia l er c m x x x x x x x x e us x x x x Location Batu caves near Kuala Lumpur, Gombak district Batu caves near Kuala Lumpur, Gombak district Well, Bogor island x Cave Spring To be continued on next page. Wat Yang Kao temple, Sangkhlaburi district, Kanchanaburi province Kaeo Sawan Badan cave, Sangkhlaburi district, Kanchanaburi province Tham Yai Nam Nao cave, Nam Nao National Park, Nam Nao district, Phetchabun province Cave Tham Khun cave, Noen Maprang district, Phitsanulok province Cave Cave in North Vietnam, Lac Thuy district, Hoa Bin province Interstitial Phreatic, Matitunao river, Cebu island Cave on ly Than Sadet river, Pha-ngan island, Surat Thani province x Cave Cave in NorthVietnam, Lac Thuy district, Hoa Bin province; Tham Bot Wangna cave, Noen Maprang district, Phitsanulok province Anchialine cave San Vicent cave, San Vicente Anchialine cave San Vicent cave, San Vicente Cave Tham Nam Phar Ngam cave, Mae Wa National Park, Mae Phrik district, Lampang province Cave Pauh Cave, Bukttinggi; Vijer cave near botanic garden; several caves in Kanchanaburi province Cave Tham Phar Ngam cave, Jaesorn National Park, Wang Nuea district, Lampang province Well Wells on Phuket island, Phuket province Hyporheic Cave Spring Cave Tham Kubio cave, Chum Phae district, Khon Kaen province Cave Cave Batu cave near Kuala Lumpur, Gombak district Cave Tham Kubio cave, Chum Phae district, Khon Kaen province Tham Phulu cave, Muang district, Phang Nga province Cave Gua Tanette cave, Maros island, Sulawesi Cave Water Polo cave, Gunung Mulu National Park, Sarawak, Borneo Country Habitat Cambodia Indonesia Laos Malaysia Myanmar Philippines Thailand Vietnam Dugesia leclerci Kawakatsu and Mitchell, 1995 Mitchellia sarawakana Kawakatsu and Chapman, 1983 Turbellaria (4 taxa) Dugesia batuensis Ball, 1970 Dugesia deharvengi Kawakatsu and Mitchell, 1989 Taxa Tab. 3. List of stygobiotic taxa for Southeast Asia, locations of records and habitats. Groundwater-dwelling fauna of SE Asia 331 Stenasellus foresti Magniez, 2002 Stenasellus covillae Magniez, 1987 Stenasellus deharvengi Magniez, 1991 Stenasellus boutini Magniez, 1991 Stenasellus brignolii Pesce and Argano, 1981 Stenasellus cambodianus Boutin and Magniez, 1985 Stenasellus chapmani Magniez, 1982 x x x x on N x x x x x co m x x x x x ia l er c m x x x e x x x us x x Cave Cave Cave Cave Spring Cave Cave Cave on ly Interstitial Cave Interstitial Cave Cave Cave To be continued on next page. Interstitial 1.3 m deep, Bambu river, Papua New Guinea, Lae Morobe province Tham Phanthurat cave in Khao Sok National Park, Phanom district, Surat Thani province Caves in Batammbang province Spring, Phuket island, Phuket province Cave near Kampong Trach district, Kampot province, Snake cave, Water Polo cave, New High Level cave, Sarawak, Borneo Bat Quarry cave, Aceh Besar, Sumatra Tham Keao cave near Nong Bua Daeng, Phakdi Chumphon district, Chaiyaphum province Ngalau Surat cave, Ngalu Pelayangan cave, Sumatra Sungai Masalong river, Sabah, Borneo Tham Yai Nam Nao cave, Nam Nao National Park, Nam Nao district, Phetchabun province Cave, Rom island Batu caves near Kuala Lumpur, Gombak district Hang Trinh Nu cave, Bo Hon island Shore of lake Wisdom, New Guinea Cave Tham Rusi cave, Muang district, Phang Nga province Anchialine Cave on islet north of Koron island cave Anchialine cave Cave, Palau islands, Republic of Palau Cave Gua Air Jernih cave, Gunung Mulu National Park; Borneo Cave, spring Caesar’s cave, well, Batuan, Bohol island x x Interstitial Interstitial Phreatic, Mindoro island Location Cave Dang Water cave, Cuc Phuong National Park, Ha Noi Therm. spring Salt thermal spring, Kuripan, Java x Anchialine Cave, Ninh Binh province cave x Anchialine Cave, Ninh Binh province cave Cave Batu caves near Kuala Lumpur, Gombak district Interstitial Phreatic near Talipanan village, Mindoro island x Country Habitat Cambodia Indonesia Laos Malaysia Myanmar Philippines Thailand Vietnam Isopoda (21 taxa) Annina fustis (Bowman and Iliffe, 1991) Anopsilana conditoria Bruce and Iliffe, 1992 (Bruce and Iliffe, 1992) Anopsilana lingua Bowman and Iliffe, 1987 Cyathura (Stygocyathura) chapmani Andreev, 1982 Cyathura (Stygocyathura) filipinica Botosaneanu and Sket, 1999 (Botosaneanu and Sket, 1999) Cyathura (Stygocyathura) papuae Weagle, Coleman and Hosse, 1987 (Weagle et al., 1987) Stenasellus bedosae Magniez, 1991 Syncarida (5 taxa) Batubathynella malaya (Sars, 1929) Paraeobathynella vietnamensis Camacho, 2005 (Camacho, 2005) Sabahbathynella wongi Schminke, 1988 Siambathynella laorsriae Camacho, Watiroyram and Brancelj, 2011 Sketinella trontelji Camacho, 2005 (Camacho, 2005) Parastenocaris arganoi Cottarelli and Mura, 1982 Parastenocaris mangyans Bruno and Cottarelli, 1999 (Bruno and Cottarelli, 1999) Parastenocaris distincta Cottarelli, Bruno and Berera, 2006 (Cottarelli et al., 2006) Phyllognathopus bassoti Rouch, 1972 Nitocra vietnamensis Tran and Chang, 2012 Hadodiaptomus dumonti Brancelj, 2005 Halicyclops thermophilus Kiefer, 1929 Microarthridion thanhi Tran and Chang, 2012 Taxa Tab. 3. Continued from previous page. 332 A. Brancelj et al. Tab. 3. Continued from previous page. Adelana chapmani (Holthuis, 1979) Arachnothelphusa rhadamanthysi (Ng and Goh, 1978) Archipelothelphusa cavernicola Takeda, 1983 Decapoda (Natantia, Reptatntia and Brachyura) (33 taxa) Thermosbaenacea (2 taxa) Theosbaena cambodjiana Cals and Boutin, 1985 Thermosbaena sp. Flagitopsia fluviatilis (Stock, 1991) Paraniphargus ruttneri Schellenberg, 1931 Psammogammarus fluviatilis Stock, 1991 Seborgia vietnamica Jaume, Sket and Boxshall, 2009 (Jaume et al., 2009) Tegano barnadi Sawicki and Holsinger, 2005 Eriopsia philippensis (Chilton, 1921) Cottarellia minima Ruffo, 1994 Bollegidia sootai (Coineau and Rao, 1972) Bogidiella thai Botosaneanu and & Noteboom, 1988 Bogidiella deharvengi Stock and Botosaneanu, 1988 Bogidiella (Medigidiella) sarawacensis Stock, 1983 Bogidiella daccordii Ruffo, 1994 Amphipoda (13 taxa) Aequigidiella aquilifera Botosaneanu and Stock, 1989 Stenasellus javanicus Magniez and Rahmadi, 2006 (Magniez and Rahmadi, 2006) Stenasellus mongnatei Magniez and Pantivong, 2005 (Magniez and Pantivong, 2005) Stenasellus monodi Magniez, 2000 Stenasellus rigali Magniez, 1991 Stenasellus stocki Magniez, 2001 Stenasellus strinatii Magniez, 1991 Thalandoniscus annae Dalens, 1989 Taxa x x x x x on N x x x x x co m x x x x x x x x ia l er c m e x x us x x x x x Interstitial Interstitial Cave Cave Cave Interstitial Cave Airport well cave, Peleliu island Tham Phulu cave, Muang district, Phang Nga province; Tham Keao cave, Phakdi Chumphon district, Chaiyaphum province Phreatic on Palawan island, St. Paul subterranean river Nat Park, Western Visayas Batu Lubang cave, Halmashera island Niah Great cave, Batu Niah National Park, Sarawak, Borneo; Deer cave, Gunung Mulu National Park, Sarawak, Borneo Tham Poung Chang cave, Muang district, Phang Nga province Interstitial, Sabang beach, eastern Mindoro, Palawan islands Interstitial, Sabang beach, eastern Mindoro, Palawan islands Well near Los Baños, southern shore of Laguna de Bay, Luzon island Pagsanjan falls, Laguna province, Luzon island Batu Lubang cave, Halmahera, east Java Gravel bar near Pagsanjan falls, laguna Cave Dong Duc Tie, Dao Van Gio island Cave Cave Cave To be continued on next page. Niah Great cave, near Miri, Borneo Simud Puteh cave, Sabah, Borneo Quinapon-an cave, Antequera, Bohol island Cave Cave near Kampong Trach district, Kompot province Cave Tham Kubio cave, Chum Phae district, Khon Kaen province Cave Interstitial Cave Interstitial Cave Well on ly x Tham Nam cave, Kaeng Khoi district, Saraburi province Cikaray cave, Leuwi Kares island Location Cave Ngalau Lagung cave, Sumatra Cave Tham Kubio cave, Chum Phae district, Khon Kaen province Cave Ngalau Indah cave, Sumatra Cave Ngalu Baso cave, Ngalau Kamang cave, Sumatra Cave Springs near the Tham Tapan cave, Muang district, Phang Nga province Cave Cave Country Habitat Cambodia Indonesia Laos Malaysia Myanmar Philippines Thailand Vietnam Groundwater-dwelling fauna of SE Asia 333 x x x Phricothelphusa deharvengi Ng, 1988 Samarplax principe Husana, Tan and Kase, 2011 (Husana et al., 2011) Sesarmoides cerberus (Holthuis, 1964) Sesarmoides emdi Ng and Whitten, 1994 Sesarmoides jacobsoni (Ihle, 1912) Stygothelphusa bidiensis (Lanchester, 1900) Sundathelphusa cavernicola Takeda, 1983 Sundathelphusa boex Ng and Sket, 1996 (Ng and Sket, 1996) Sundathelphusa hades Takeda and Ng, 2001 (Takeda and Ng, 2001) Sundathelphusa lobo Husana, Naruse and Kase, 2009 Sundathelphusa sottoae Ng and Sket, 1996 (Ng and Sket, 1996) Phaibulamon stilipes Ng, 1992 x x on N x x x co m x x x x x x x x x x x e us x Bantakay cave, Luzon island Marulas caves, Luzon island Bautakay cave, Atimonau, Quezon province, Luzon island Gua Tanette cave, Lubang Batu Neraka cave, cave in Maros, Maros, Sulawesi Deer cave, Green cave, Clearwater cave, Gunung Mulu National Park, Sarawak, Borneo Clearwater cave, cave of Winds, Wonder cave, Gunung Api masiff, Gunung Mulu National Park, Sarawak, Borneo Subterranean river near Santiago, Isabela province, Luzon island; cave near Sitio Disiluad, Aglipay Quirino province, Luzon island Bantakay cave, Luzon island Location Cave, Nusa Lain island Gua Paon cave, Nusa Penida island Guwa Djamblang cave, Guwa Ningrng caves, Bedojo district, Gunung Sewu, Java Bau caves in the region of Bau and Sarawak, Borneo Quinaponan cave, Ughob cave, Antequera, Bohol island Castigio cave, Capiro springs and rivers near Batuan, Bohol island Latay cave, Agusan del Sur, Surigao del Sur, Mindanao To be continued on next page. Cave Lobo cave, Samar, Jiabong Cave, well Ughob cave, Bonugan cave, well, Batuan, Bohol island Cave Cave Cave Cave on ly Cave Cave Cave Cave Tham Tê cave, Thakhek district, Khammouane province Anchialine Bat cave, Boracay island; Tagbaobo cave, Samal island cave Cave Several caves, probably only in Gunung Sewu Karst x Cave Cave in Phong Nha, Hang Toi, Quang Binh province Cave Tiniguaban cave, Gimaras, Tinigualban island; Holmahera, Maluccas Cave Tham Nam Phrah Khoan cave, Sangkhlaburi district, Kanchanaburi province Cave Tham Poung Chang cave, Muang district, Phang Nga province Anchialine cave Principe cave, Eastern Visayas, Samar Cave x ia l er c m Cave Cave Cave Cave Cave Cave Cave x x x x Country Habitat Cambodia Indonesia Laos Malaysia Myanmar Philippines Thailand Vietnam Edoneus erwini Cai and Husana, 2009 (Cai and Husana, 2009) Edoneus marulas Cai and Husana, 2009 (Cai and Husana, 2009) Edoneus sketi Cai and Husana, 2009 (Cai and Husana, 2009) Erebusa calobates Yeo and Ng, 1999 Karstarma philippinarum Husana, Naruse and Kase, 2010 (Husana et al., 2010) Macrobrachium poeti Holthuis, 1984 Nemoron nomas Ng, 1996 Parhippolyte uveae Borradaile, 1899 Edoneus atheatus Holthuis, 1978 Cerberusa tipula Holthuis, 1979 Cerberusa coeca Holthuis, 1979 Archipelothelphusa longipes Balss, 1937 Cancrocaeca xenomorpha Ng, 1991 (Ng, 1991) Taxa Tab. 3. Continued from previous page. 334 A. Brancelj et al. 3 20 x x on 2 x 19 x x co m x x 1 x 35 x ia l er c m x Names of species and genera are as published in original papers; no taxonomic revisions are included in this analysis. Total: 122 species Silurus furnessi = Pterocryptis furnessi (Fowler, 1905) Troglocyclocheilus khammouaensis Kottelat and Bréhier, 1999 Schistura spekuli Kottelat, 2004 Schistura spiesi Vidthayanon and Kottelat, 2003 Schistura jarutanini Kottelat, 1990 Neolissochilus subterraneus Vidthayanon and Kottelat, 2003 Pterocryptis buccata Ng and Kottelat, 1998 Puntius microps (Günther, 1868) Schistura deansmarti Vidthayanon and Kottelat, 2003 Monopterus albus (Zuiew, 1793) (rice-field eel) Nemacheilus oedipus Kottelat, 1988 Nemacheilus troglocatarctus Kottelat and Géry, 1989 Caecogobius cryptophthalmus Berti and Ercolini, 1991 Cryptotora thamicola (Kottelat, 1988) Clarias nieuhofii Valenciennes, 1840 Pisces (15 taxa) Barbus speleops Roberts, 1991 Coleoptera (1 taxon) Siamoporus deharvengi Spangler, 1996 Acari/Hydrachnida (1 taxon) Soldanellonyx monardi sarangensis Viets, 1929 Thelphusula styx Ng, 1989 N x x 36 x x x x x x x e us x x x 10 x Cave Cave Cave Cave Cave Cave Cave Cave Bikahan cave, Antequera, Bohol island Quilas cave, Batuan, Bohol island Location Tham Phu Khieo cave, Nong Bua Daeng district, Chaiyaphum province Cave on Samar island Susa cave, Pang Ma Pha district, Mae Hong Son province Clearwater cave, Snake cave, Gunung Mulu National Park, Sarawak, Borneo Several caves along the country Several caves in Pang Mapha district, Mae Hong Son province Tham Wang Badan cave, Sai Yok district, Kanchanaburi province Tham Phra Wang Daeng cave, Noen Maprang district, Phitsanulok province Sai Yok Noi cave, Sai Yok district, Kanchanaburi province Djamblang cave, Bedojo district, Gunung Sewu, Java Tham Phra Sai Ngam cave, Noen Maprang district, Phitsanulok province Sao Hin cave, Thong Pha Phum district, Kanchanaburi province Tam Duong cave, Lai Chau province Tham Phra Wang Daeng cave, Noen Maprang district, Phitsanulok province Logan’s cave, Sarawak, Borneo Spring Nam Dôn, Thakhek district, Khammouane province Tham Pulu cave, Muang district, Phang Nga province; Tham Kubio cave, Chum Phae district, Khon Kaen province Java Langun cave, Samar, Calbiga Caves at Bidi, Posih cave, Jambusan cave, Fairy cave, near Bau Bat cave, Gunung Mulu National Park, Sarawak, Borneo on ly Cave Cave Cave Cave Cave Cave Cave Cave Cave Spring Cave Cave Cave Cave Cave Country Habitat Cambodia Indonesia Laos Malaysia Myanmar Philippines Thailand Vietnam Sundathelphusa urichie Ng and Sket, 1996 (Ng and Sket, 1996) Sundathelphusa vedeniki Ng and Sket, 1996 (Ng and Sket, 1996) Sundathelphusa waray Husana, Naruse and Kase, 2009 Thelphusula bidiens (Lanchaster, 1900) Taxa Tab. 3. Continued from previous page. Groundwater-dwelling fauna of SE Asia 335 336 A. Brancelj et al. on ly Structure of stygobiotic fauna in Southeast Asia e Thirteen higher taxonomic groups have been recorded so far in SE Asia (including vertebrates, i.e. fish; Tab. 3). The most abundant groups so far are the Decapoda (Natantia, Reptantia and Brachyura), represented by 33 taxa (6+3+24 species, respectively), followed by Copepoda (22 species), Isopoda (20 species), Amphipoda (13 species), Pisces (10 species) and Syncarida (5 species). Other groups (Turbellia, Nematoda, Oligochaeta, Ostracoda, Thermosbaenacea, Acari/Hydrachnida and Coleoptera) are represented only with one to four species each. Out of 74 genera with stygobionts, there are 56 genera where only one stygobiotic representative is known. The number of species per certain group within a particular country varies considerably – from 1 to 17 (Tabs. 3 and 4). The group with the highest number of species per country is the Decapoda in the Philippines, where 17 species are known, followed by ten species of Copepoda from Thailand. Groups with seven species each per county are the Amphipoda from the Philippines, the Decapoda from Malaysia and the Isopoda from Thailand. Four groups have six representatives per country: Copepoda in the Philippines, Isopoda in Indonesia, Decapoda in Indonesia and the Pisces in Thailand. The group with five species is Copepoda in Vietnam, while Isopoda has four species in the Philippines. There are 29 groups with only one or two species known for each group and for each country. The time series of stygobiotic records indicates that there are 41 papers, where 48 authors (alone or as co-authors) contributed one single record on stygobiotic fauna; 17 of the records were published before 1980. The rest of the records were contributions by 30 authors who recorded/described two or more new species (Tab. 5). Among those, two records by the same author were done in 1900 (Lanchester, Decapoda) and additional two in 1967 (Borutzky, Copepoda). Up to 1986, 15 more records N on co m m er c Revision of biospeleological studies and the cavedwelling fauna of Thailand has been previously done by Deharveng and Bedos (2001) and more recently the terrestrial cave-dwelling fauna was reviewed by Ellis (2006, 2012). Investigations on cave-dwelling fauna have been carried out since the early 20th century but focussed only on terrestrial fauna from some caves in southernmost Thailand (Annandale et al., 1913). Stenasellus brignoli Pesce and Argano, 1981 was the first stygobiotic species described for Thailand. It was collected from freshwater wells in Phuket province in 1980 (Pesce and Argano, 1981). After 1983, the number of biospeleological studies increased as French researchers from the Association Pyrénéenne de Spéléologie started their caving activities in Thailand. In 2001, when Deharveng and Bedos (2001) provided the list of aquatic cave-dwelling fauna from Thailand, the list included 21 invertebrate and vertebrate species belonging to 9 higher taxonomic groups (Tab. 3). The ecology and biology of more than half of those species were not known (Deharveng and Bedos, 2000). The most abundant on the list were Isopoda (5 species) and the Pisces (6 species). In addition, there were two species of Amphipoda and two of Decapoda. Several groups (flatworms, oligochaetes, copepods, syncarids, thermosbaenaceans and coleopterans) were represented with only one species and all of them were endemic to Thailand (Tab. 3). After 2000, 14 new stygobiont species were discovered, among them four new species of fish (Vidthayanon and Kottelat, 2003; Kottelat, 2004), which increased the number of stygobiotic fishes in Thailand from six to ten species. In the last 10 years significant progress has been made in research on the groundwater Copepoda (Fig. 2A and 2B). Before then, only one stygobiotic species was known from the freshwater interstitial habitat (Elaphoidella margaritae, Pesce and Apostolov, 1985) (Tab. 3). The first cave-dwelling species found in Thailand was Elaphoidella namnaoensis Brancelj, Watiroyram us Historical overview and present status in Thailand and Sanoamuang, 2010 from a cave in Nam Nao National Park (Phetchabun province) (Brancelj et al., 2010) and the most recently described species are Bryocyclops maewaensis Watiroyram, Brancelj and Sanoamuang, 2012 (Watiroyram et. al., 2012) and two species from the genus Fierscyclops published in this volume (Boonyanusith et. al., 2013). Three papers with descriptions of six new species (but not included in this analysis) have been already submitted to journals (Boonyanusith, personal communication; Watiroyram, personal communication). Intensive research on cave environments, especially on epikarst, conducted during the PhD studies of two of the co-authors (CB and SW), revealed that stygobiotic fauna is very rich and not only present in Thailand but also in nearby countries (Vietnam and Laos) (Fig. 2C-G). It includes, apart from the Copepoda also Ostracoda, Syncarida, Isopoda and Amphipoda. ia l One-hundred and one species from the list of stygobionts in SE Asia living in karstic habitats are recorded from caves (8 of them from anchialine caves), four species are recorded from karstic springs and one from a thermal spring. Two species were found both in caves and wells, while only one was found from a well. In addition, 13 species were recorded only from porous aquifers (i.e. interstitial/hyporheic environment), where micro-crustaceans (body size ≤1 mm) prevailed. In contrast to porous environments, in karstic caves and springs a wide array of body size could be found – from small-body sized Nematoda and Copepoda (body size <1 mm) to largebody sized organisms like Decapoda and Pisces (body size >10 cm). 337 Groundwater-dwelling fauna of SE Asia Tab. 4. Number of stygobiotic species per higher taxonomic group per country. Cambodia Species (n) Groups (n) Turbellaria Nematoda Oligochaeta Ostracoda Copepoda Syncarida Isopoda Amphipoda Thermosbaenacea Decapoda Acari/Hydrachnida Coleoptera Pisces 3 2 Indonesia Laos 20 8 1 2 2 Malaysia 19 9 2 1 1 2 2 6 2 1 6 1 1 1 Philippines 1 1 2 2 1 1 6 4 7 7 1 35 6 17 2 1 1 Thailand 36 10 1 Vietnam 1 10 1 7 2 2 2 1 9 on ly 1 Myanmar 10 4 5 2 1 1 1 Decapoda, Pisces Isopoda Pisces Syncarida, Copepoda Decapoda Copepoda Decapoda Decapoda, Ampipoda, Isopoda Amphipoda, Isopoda Copepoda Syncarida, Copepoda Amhipoda Copepoda Decapoda Decapoda Syncarida Isopoda Turbellaria Decapoda Decapoda Pisces Copepoda Thermosbaeanaceae, Isopoda Isopoda Copepoda Copepoda Turbellaria Isopoda, Copepoda Amphipoda Copepoda Turbellaria Turbellaria Nematoda Oligochaeta Ostracoda Ostracoda Ostracoda Copepoda Copepoda er c m co m on N Ng - 13 Magniez - 12 Kottelat - 10 Brancelj - 7 Husana - 7 Cottarelli - 6 Holthuis - 6 Sket - 6 Botosaneanu - 5 Sanoamuang - 5 Watiroyram - 5 Stock - 5 Bruno - 4 Kase - 4 Cai - 3 Camacho - 3 Ilife - 3 Kawakatsu - 3 Naruse - 3 Takeda - 3 Vidthayanon - 3 Borutzky - 2 Boutin - 2 Bowman - 2 Chang - 2 Fosshagen - 2 Mitchell - 2 Pesce - 2 Ruffo - 2 Tran - 2 Ball - 1 Chapman - 1 De Man - 1 Yamaguchi - 1 Fernando - 1 Klie - 1 Victor - 1 Apostolov - 1 Kiefer - 1 Group(s) studied Author - no. of taxa recorded Mura - 1 Rouch - 1 Schminke - 1 Andreev - 1 Argano - 1 Bruce - 1 Coleman - 1 Hosse - 1 Pantivong - 1 Rahmadi - 1 Weagle - 1 Boxshall - 1 Chilton - 1 Coineau - 1 Holsinger - 1 Jaume - 1 Noteboom - 1 Rao - 1 Sawicki - 1 Schellenberg - 1 Cals - 1 Balss - 1 Borradaile - 1 Goh - 1 Ihle - 1 Tan - 1 Whitten - 1 Yeo - 1 Viets - 1 Spangler - 1 Berti - 1 Bréhier - 1 Ercolini - 1 Fowler - 1 Géry - 1 Günther - 1 Roberts - 1 Valenciennes - 1 Zuiew - 1 ia l Author - no. of taxa recorded us e Tab. 5. Authors who published papers on stygofauna from Southeast Asia and their contribution to the knowledge of a particular group (most of them as author or co-author of taxonomic papers) (for details on recorded taxa see Tab. 3). Group(s) studied Copepoda Copepoda Syncarida Isopoda Isopoda Isopoda Isopoda Isopoda Isopoda Isopoda Isopoda Amphipoda Amphipoda Amphipoda Amphipoda Amphipoda Amphipoda Amphipoda Amphipoda Amphipoda Thermosbaeanaceae Decapoda Decapoda Decapoda Decapoda Decapoda Decapoda Decapoda Acari Coleoptera Pisces Pisces Pisces Pisces Pisces Pisces Pisces Pisces Pisces 338 N on co m m er c ia l us e on ly A. Brancelj et al. Fig. 2. Epikarst stygobionts and habitats in Southeast Asia. A) Scanning electron microscopy image of a female representative of epikarst copepods, from the order Cyclopoida - Bryocyclops maewaensis Watiroyram, Brancelj and Sanoamuang, 2012 (photo by Santi Watiroyram); B) light microscopy image of a female representative of the epikarst copepods, from the order Harpacticoida – Paramorariopsis irenae Brancelj, 2006 (photo by Anton Brancelj); C) entrance into a karstic cave (view from outside) in Thailand (photo by Santi Watiroyram); D) entrance into a karstic cave (view from inside) from Laos (photo by Anton Brancelj); E,F,G) sampling of the epikarstic fauna from the pools filled by percolating water in caves in Thailand (photo by Santi Watiroyram); H) a detail from a comparable ecosystem (karstic cave) in Slovenia (photo by Anton Brancelj). 339 Groundwater-dwelling fauna of SE Asia were recorded by 7 authors. After 1986, 67 new species were added by authors, who contributed more than two descriptions of a new species. The greatest contributions were by Ng and Martinez – 13 and 12 descriptions, respectively – on Decapoda, Pisces and Isopoda. co m e us m er c ia l The first exploration of the freshwater cave fauna in SE Asia started at the end of the 19th century and was mainly limited to terrestrial habitats (Price, 2004). Actually, even today, most work is still focussed on terrestrial fauna (=troglobionts) (Juberthie and Decu, 2001). Some limited exploration was done also on aquatic fauna in the caves. Among the first explorations were those in the Philippines (in 1820), followed by Myanmar (in 1888), Vietnam (in 1906), Indonesia (in 1910), Thailand (in 1913) and Laos (in 1919) (Botosaneanu, 1986). Research on cave fauna in Cambodia and Malaysia started later, in 1960/1961 (Annandale et al., 1913; Botosaneanu, 1986). Tropical and subtropical karstic areas worldwide were for a long time neglected as suitable places for collecting and studying stygobionts. When comparing Europe (an area of 10,180,000 km2 and about 2000 stygobionts) and SE Asia (an area of about 4,304,000 km2 and 122 stygobionts), it is obvious that there is a big potential for more stygobionts to be found in SE Asia. A comparison of the number of stygobionts in SE Asia vs the rest of the world, on ly DISCUSSION and vs the total number of members of particular groups in freshwater, revealed that the number of stygobionts in SE Asia compared with the rest of the world is (still) relatively low (Tab. 6). The only exception is Brachyura (Decapoda), for which the number of stygobionts has significantly increased in the last 25 years. Comparing the area of SE Asia and the rest of the world and number of stygobionts from interstitial and karstic aquifers already known in the rest of the world, at least 800 stygobionts could be expected in SE Asia. The actual numbers of stygobionts recorded for Europe and SE Asia are a combination of stygobionts in fissured (i.e. karstic) as well as porous (i.e. alluvium; interstitial) aquifers. As both types are common in SE Asia, the estimated number of 800 stygobionts is quite probable and could even be exceeded. In addition to exclusively freshwater caves, there are also numerous anchialine caves along the coasts, which are rich in freshwater, brackish and marine stygobionts (Fosshagen and Ilife, 1989; Husana et al., 2009; Tran and Chang, 2012). A high potential for discovery of new stygobionts is also indicated by the cumulative curve of stygobiotic taxa over time, which is still very steep and where, in the last 40 years (after 1970), the number of stygobionts increased almost six-fold (from 19 to 122 species) (Fig. 1). The increase of species within a particular group is uneven and reflects mainly the interests and intensity of work by individual authors on the specific group. Currently, the most Tab. 6. List of the main groups of crustaceans and fish, with the number of known taxa in subterranean habitats in Southeast Asia, worldwide and in all inland surface habitats. Crustaceans and fish fauna Copepoda Calanoida Harpacticoida Cyclopoida Gelyelloida on Ostracoda N Cladocera Southeast Asia* Syncarida 0 Amphipoda 2 References 620 Forró et al. (2008) 1936 20 1 17 2 0 607 11 441 153 2 2774 552 1124 1096 2 21 553 994 154 1+1? Decapoda Anomura Brachyura Natantia Reptantia World inland water bodies# 119 13 Thermosbaenaceae Worldwide° 5 5 Isopoda Pisces Stygobionts 16 Camacho and Valdecasas (2008) 665 1870 Väinölä et al. (2008) 121 2 15 42 (69§) 31 2844 63 1476 655 640 Bond-Backup et al. (2008) Yeo et al. (2008) De Grave et al. (2008) Crandall and Buhay (2008) 92 18 12,470 Data from this paper; data from Botosaneanu, 1986; see references in right column; after De Grave et al. (2008). * ° # Boxshall and Defaye (2008) 240 10 33 0 24 6 3 Martens et al. (2008) § Wilson (2008) Jaume (2008) Lêvêque et al. (2008) 340 A. Brancelj et al. ia l us e on ly entrances of the caves, where litter or drift can accumulate. For this reason, Decapoda, especially Brachyura, were frequently reported from those zones in the past as stygobionts when in fact some of them were stygoxenes or stygophiles (Leclerc et al., 2001). However, they contributed to the overall biodiversity of subterranean habitats. For that reason, the distinction between stygophiles and stygobionts is more blurred in the tropical zones when compared to that in temperate zones. Due to the low intensity of research on fauna in many aquifers worldwide, the distribution of the majority of taxa is still very poorly known. As most stygobionts were found in one or a few sampling campaigns and/or in one or a few locations only, most of them are considered as endemics while in reality they might not be. Scarcity of data on their distribution can lead to the wrong conclusion that all stygobionts are endemic on a small scale (i.e. narrow endemics) (Deharveng et al., 2009). Some data about a few species from SE Asia indicates that their range of distribution can be extended at least over two countries (examples in groups of Copepoda, Thermosbaenacea and Decapoda). An example of misinterpretation of endemism can be found in the Copepoda from epikarst in Thailand. After five years of intensive sampling it appears that rare and endemic taxa are actually quite common – but limited to specific habitats (Brancelj et al., 2010; Watiroyram, 2012; Watiroyram et al., 2012). This supports the idea to put more effort into searching for representatives of some aquatic groups, which are common in surface water bodies but still rare in groundwater, either in porous or karstic aquifers. The most appropriate candidates are groups of Cladocera and Calanoida. Both groups have many representatives in epigean water bodies, while in groundwater they are represented by only a few species (Brancelj and Dumont, 2007). So far, there is only one known stygobiotic species of Calanoida from SE Asia (Brancelj, 2005). Cladocera are represented with representatives from the genus Nicsmirnovius, which lives in rheic and hyporheic conditions, much like Phreatalona, yet it is not a stygobiont (Van Damme et al., 2003). For that reason, more intensive and systematic sampling programmes should be prepared for different habitats in interstitial as well as karstic aquifers. Special attention should be put on sampling techniques and equipment. In principle, all sampling methods already known and used in caves and alluvium in Europe and North America (hand-nets, drift nets, plankton nets, baited traps, Bou-Rouch pump and Karaman-Chappuis method) (for details see: PASCALIS protocol) can be applied in the caves and gravel bars of SE Asia. In the past incorrect sampling devices (especially nets with too coarse mesh size) resulted in a loss of many smaller stygobionts. When new techniques were introduced, the number of collected species/specimens increased significantly (Brancelj, N on co m m er c intensively studied groups are the Copepoda, Isopoda, Amphipoda, Decapoda and Pisces, while some other groups, which are well studied elsewhere, are underestimated in SE Asia. Among those groups are the Oligochaeta, Ostracoda and Hydrachnida, represented by only a few species (Tabs. 3 and 5). The effect of highly motivated taxonomists can be seen, for example, in the case of the Indian stygofauna, where a significant increase in the knowledge of micro-crustaceans was achieved in relatively short period by only a few specialists (Ranga Reddy and Defaye, 2008; Ranga Reddy et al., 2008; Ranga Reddy and Schminke, 2009). The same is valid for China, where research on karst systems resulted in the description of several new stygobionts (Sket and Fišer, 2009) (Tab. 5). Although both countries, India and China, have high potential for groundwater fauna, there is a slight possibility of sharing common fauna with SE Asia on the species level, except on a very local scale. Based on the present knowledge of the distribution of groundwater fauna in SE Asia, distribution of particular species is rather limited and is usually confined to a region. Only some exceptionally species have trans-border distributions over several provinces or countries. Recent intensive inventory of fauna from relatively unknown environments (i.e. epikarst) in Thai caves, has resulted in the discovery of one species of bathynellid and six species of copepods as well as several species of Harpacticoida and Cyclopoida that are not yet described (Brancelj et al., 2010; Camacho et al., 2011; Watiroyram et al., 2012; Boonyanusith et al., 2013; Watiroyram et al., 2013). Along with the true stygobionts from epikarst, many species of Copepoda were collected from pools or streams, but the majority were stygoxenes or stygophiles transported into the caves during floods or as regular drift (Boonyanusith, personal communication; Watiroyram, personal communication). The problem of identifying the correct ecological position of species found in the caves is that specimens can become pale after some time in subterranean environments, which leads to misinterpretation of the stygobiotic nature of collected specimens. Such an example was Argyrodiaptomus cavernicolax Shen and Tai, 1965, from a cave in Southern China, which recently appeared to actually be two closely related species of Sinodiaptomus, which freely move in and out of the cave (Dumont, personal communication). Another example is Mesocyclops francisci Hołyńska, 2000, which was collected from a cave in Northern Thailand (Watiroyram, 2012) but was previously recorded in Malacca, Malaysia, Sumatra and Cambodia from surface water habitats (Hołyńska, 2000; Chaicharoen, 2011). Food in subterranean habitats is an important element that determines population size and biodiversity in temperate zones (Culver et al., 2006). As primary production in tropical zones is more intense, more food is available, especially at the Groundwater-dwelling fauna of SE Asia 2003). One of the new techniques, specific for SE Asia, is sampling epikarst fauna from Buddha pots (Brancelj et al., 2010). They are actually plastic or metal buckets, placed near Buddha statues in the caves to collect dripping water from the ceiling. They appeared as very efficient sampling devices for sampling epikarst fauna and where several new species of Copepoda had been already collected (Brancelj et al., 2010; Watiroyram et al., 2012; 2013). CONCLUSIONS co m m er c ia l us e ACKNOWLEDGMENTS We thank Martin Ellis who supplied the list of organisms found in karstic areas and subterranean habitats in Thailand. This work was partly supported by the National Research University Project of Thailand, Office of the Higher Education Commission, through the Holistic Watershed Management Cluster of Khon Kaen University. The senior author (AB) would like to thank to the organisers of the FISA conference for invitation to the meeting. The authors wish to thank Dr. Jolyon Dodgson for his help with the English corrections and two anonymous reviewers for their useful comments on the earlier version of the paper. 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