Research Article |
Corresponding author: Vladimir Ivanov ( v--ivanov@yandex.ru ) Academic editor: Dominique Zimmermann
© 2014 Hans Malicky, Vladimir Ivanov, Stanislav Melnitsky.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Malicky H, Ivanov V, Melnitsky S (2014) Caddisflies (Trichoptera) from Lombok, Bali and Java (Indonesia), with a discussion of Wallace’s Line. Deutsche Entomologische Zeitschrift 61(1): 3-14. https://doi.org/10.3897/dez.61.7046
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Caddisflies (Trichoptera) of Southeast Asia are analyzed with special attention to the Sunda Islands to evaluate the zoogeographic effects of island isolation and potential influence from the neighboring continental faunas. Results of recent Trichoptera collections and synopsis of previously published data for the islands of Java, Bali, and Lombok are presented along with their zoogeographical interpretation on the islands as well as on the adjacent regions. A total of 202 Trichoptera species is known to occur on the three islands; 146 species are known in Java, 73 in Bali and 61 in Lombok. 43 species are common to Java and Bali, 27 to Java and Lombok, 30 to Bali and Lombok, 70 to Java and Sumatra. A significant decrease in species richness has been observed in comparison to the Asian mainland. The caddisfly fauna of the three islands is of Asiatic origin, no Australian influence was noted. The well-known Wallace’s line does not act as a faunistic border between Bali and Lombok for Trichoptera.
faunistics, new records, Asia, Sunda Islands, zoogeography
Caddisflies (order Trichoptera) have a complicated distribution in the world, with significant species diversity concentrated in Tropical Asia, especially in the Himalayas (
The amazing species richness and endemism of the Malay Archipelago exists in one of the most geologically dynamic regions of our planet. The geological history of the Malay Archipelago is very complex (
A famous boundary dividing the Asian and Australian biotas, Wallace’s line, is one of the most disputed topics in biogeography since the end of the XIX century (
Malay Archipelago, sampling areas (rectangles), and the major biogeography divider lines: 1 – Wallace’s lines (divergence around Sulawesi Island is caused by the changing views of Wallace, while the western branch is currently accepted as the canonic one), 2 – Weber’s line, 3 – Lydekker’s line. Wallacea is delimited by Wallace’s and Lydekker’s lines.
The knowledge of the caddisflies of the Sunda Islands was poor for a long time. The first representative summary was given by Georg
Nevertheless, the caddisflies of the island of Lombok remained practically unknown, and this is still the state of knowledge of the caddisflies of the islands east of Lombok, including the Moluccas. This was the reason for the members of the Department of Entomology of the State University of St. Petersburg to make collections on the islands of Java, Bali, and Lombok in 2008 and 2009. The species which were new for science have been already described elsewhere (
Field collection included the well-known methods of light catch by small water-filled UV traps installed close to the water edge, net sweeping during daytime in the riparian vegetation, and hand picking. Only adults were collected; larvae and pupae were left for future investigations. The material is preserved in 70% ethanol and is stored in the collections of the Zoological Institute of the Russian Academy of Sciences in St. Petersburg. Some specimens are in the collection of the first author. Data from the faunistic publications and some material from the Malicky collection have been used for the analysis of zoogeography and species distribution.
Sampling localities were as follows:
LOCALITY 1: Lombok, Senaru, Sindanggala waterfall, Tiu Kelep waterfall and irrigation canal, 08°18’09’’S, 116°24’30’’E (Sindanggala waterfall, 455 m, lowest point), 08°18’29’’S, 116°24’27’’E (irrigation channel, 508m, highest point), 2–4 March 2008, at light and net sweeping, leg. V.D. Ivanov and S.I. Melnitsky; Lombok, Senaru, 19–26 September 2009, leg. N. Yu. Kluge. There were 5 biotopes situated close to each other: 2 of them were large waterfalls, one was a shallow rapid tropical river with stony bed in a deep canyon, and another one was an irrigation channel with fast running water and stony bottom some 30 m above the river. Several new species of Tinodes and Hydropsyche were present only near a leakage from the irrigation channel flowing down the mountain slope.
LOCALITY 2: Lombok, Sembalung Lawang, 08°21’37’’S, 116°32’17’’E, h=1160 m, 5 March 2008, at light, leg. V.D. Ivanov and S.I. Melnitsky. An irrigation channel with warm water in a flat mountain terrace surrounded by fields and shore bushes.
LOCALITY 3: Lombok, vic. Kembangkuning, 7 March 2008, 08°30’40’’S, 116°25’23’’E, h=835–875 m. Rinjani National Park, Jeruk Manis waterfall, at light and net sweeping, leg. V.D. Ivanov and S.I. Melnitsky. A high waterfall and a short piece (approximately 100 m) of rapid river below it followed by cascading waterfalls downstream.
LOCALITY 4: Lombok, vic. Kembangkuning, 2 km N Kotaraja, 08°33’33’’S, 116°25’23’’E h=490 m, river and irrigation canal, 8 March 2008, at light and net sweeping, leg. V.D. Ivanov and S.I. Melnitsky. An irrigation complex including a river with rapids and reaches in a deep canyon with an irrigation channel originating at the water divider.
LOCALITY 5: Lombok, Pelangan Barat, near mt. Embit, 08°48’23’’S, 115°56’24’’E, h=20 m, 11 March 2008, at light, leg. V.D. Ivanov and S.I. Melnitsky. Shallow muddy slowly running and warm river nearby the village Pelangan Barat.
LOCALITY 6: Bali, Gitgit waterfall, 08°11’34’’S, 115°08’04’’E, h=520 m, 14–15 March 2008, at light and net sweeping, leg. V.D. Ivanov and S.I. Melnitsky. Cascading waterfalls above the sampling place followed by a rapid river with large boulders.
LOCALITY 7: Bali, Munduk, Melanting waterfall, 08°15’27’’S, 115°04’12’’E, h=700–900 m, 16–17 March 2008, at light and net sweeping, leg. V.D. Ivanov and S.I. Melnitsky. A river and an irrigation channel originating right below a large waterfall in deep canyon.
LOCALITY 8: Java, Bogor, Sadame river, Botanical Garden, 06°35’34’’S, 106°48’06’’E, h=250 m, 23 February 2008, at light, leg. V.D. Ivanov and S.I. Melnitsky. Large warm muddy river crossing the Bogor Botanical Garden; rapids at the bridge below the garden.
LOCALITY 9: Java, Ciapus, Gunung Salak, 06°39’29’’S, 106°44’55’’E, h=625 m, 24 February 2008, leg. V.D. Ivanov and S.I. Melnitsky. A brook with stony bottom above a small unstable river on the northern slope of Salak volcano.
LOCALITY 10: Java, Cipanas, 30 km SE Bogor, 6°42’43’’S, 107°01’12’’E, h=1100 m, 25–26 February 2008, 06°42’S, 107°01’E, leg. V.D. Ivanov and S.I. Melnitsky; Java, Cipanas, Cibodas, 6–11 August 2009, leg. N. Yu. Kluge. A small river in a rural environment.
List of species known from Java, Bali and Lombok, with new records
Abbreviations: B – Borneo, P – Peninsular Malaysia, S – Sumatra, Wd – wide distribution; m – males, f – females.
Taxa/family, species | Java | Bali | Lombok | other | Found in localities (Loc) |
---|---|---|---|---|---|
RHYACOPHILIDAE Stephens, 1836 | |||||
Rhyacophila anakbatukau MALICKY, 1995 | + | + | Loc.1:5m,1f; Loc.7:1m | ||
Rhyacophila curvata MORTON, 1900 | + | + | + | S, P | Loc.1:1m; Loc.3: (1f); Loc.6: 1m; Loc.7:1m |
Rhyacophila lieftincki ULMER, 1951 | + | ||||
GLOSSOSOMATIDAE Wallengren, 1891 | |||||
Glossosoma gera MALICKY & CHANTARAMONGKOL, 2009 | + | ||||
Glossosoma kerambos MALICKY, 2004 | + | ||||
Agapetus abbreviatus ULMER, 1913 | + | + | + | Loc.1:21m, 159f; Loc.3:2m, 5f; Loc.4:7m, 19f; Loc.6:17m, 26f; Loc.7:10f; Loc.8:3m; Loc.9:2m, 15f | |
Agapetus antilochos MALICKY, 1998 | + | ||||
Agapetus cataractae ULMER, 1951 | + | Loc.10:2m | |||
Agapetus kekrops MALICKY, 2004 | + | ||||
HYDROPTILIDAE Stephens, 1836 | |||||
Hydroptila baukis MALICKY, 1998 | + | ||||
Hydroptila crenata ULMER, 1951 | + | S | |||
Hydroptila elongata ULMER, 1951 | + | ||||
Hydroptila pintal WELLS & HUISMAN, 1992 | + | B, P, S | |||
Hydroptila rahel MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.4:12m | |||
Hydroptila ruben MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.7:1m, (5f) | |||
Hydroptila rumpun WELLS & HUISMAN, 1992 | + | P, S | Loc.4:5m | ||
Hydroptila sphinx MALICKY & CHANTARAMONGKOL, 2007 | + | S | |||
Hydroptila tong WELLS & MALICKY, 1997 | + | S | |||
Hydroptila trullata ULMER, 1951 | + | P, S | |||
Microptila innokentiyi MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.1:3m | |||
Microptila pasak WELLS, 1993 | + | ||||
Microptila rinjani MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.1:1m | |||
Microptila taji WELLS, 1993 | + | ||||
Tricholeiochiton fortensis ULMER, 1951 | + | P, S | |||
Oxyethira bogambara SCHMID, 1958 | + | B, P, S, Wd | |||
Oxyethira incana ULMER, 1906 | + | P, S | |||
Ugandatrichia kebumen WELLS & MALICKY, 1997 | + | ||||
Orthotrichia curvata ULMER, 1951 | + | + | + | Loc.4:1m; Loc.8:16m, (numerous f); Loc.10:4m, (13f) | |
Orthotrichia indica MARTYNOV, 1935 | + | S, P, Wd | |||
Orthotrichia jethran MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.4:2m | |||
Orthotrichia litoralis ULMER, 1951 | + | + | S, P, Wd | ||
Orthotrichia maeandrica ULMER, 1951 | + | P, S | |||
Orthotrichia ranauana ULMER, 1951 | + | + | S | ||
Saranganotrichia decussata ULMER, 1951 | + | ||||
Scelotrichia jari WELLS & HUISMAN, 1993 | + | B, P | Loc.1:4m; Loc.4:1m | ||
Scelotrichia milka MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.4:1m, (1f) | |||
Scelotrichia nikolayi MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.1:1m, (1f); Loc.4:1m | |||
Scelotrichia saranganica ULMER, 1951 | + | + | S | Loc.1:17m, (3f); Loc.4:1m; Loc.10:1m, (2f) | |
Chrysotrichia piring WELLS, 1993 | + | ||||
Chrysotrichia sukamade WELLS & MALICKY, 1997 | + | S | |||
Chrysotrichia terpisaduri WELLS, 1993 | + | ||||
Chrysotrichia trisula WELLS, 1993 | + | ||||
Plethus baliana ULMER, 1951 | + | + | |||
Plethus berbulu WELLS, 1993 | + | ||||
Plethus cruciatus ULMER, 1951 | + | + | + | S | Loc.1:2m; Loc.6:59m, numerous f |
Parastactobia duatali WELLS & MALICKY, 1997 | + | + | + | Loc.1:1m | |
Stactobia bersisik WELLS, 1993 | + | + | + | Loc.4:2m Loc.6:1m | |
Stactobia betiri WELLS & MALICKY, 1997 | + | ||||
Stactobia crassa ULMER, 1951 | + | ||||
Stactobia germani MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.4:1m | |||
Stactobia keluk WELLS, 1993 | + | + | |||
PHILOPOTAMIDAE Stephens, 1829 | |||||
Chimarra anam MALICKY, 2008 | + | S | |||
Chimarra ard MALICKY, 2008 | + | ||||
Chimarra arkit MALICKY, 2008 | + | ||||
Chimarra batukaua MALICKY, 1995 | + | + | + | Loc.1:4m, 41f; Loc.5:1m; Loc.6:15m, 68f; Loc.4:43m, 193f | |
Chimarra berenike MALICKY, 1998 | + | ||||
Chimarra briseis MALICKY, 1998 | + | + | S | Loc.1:2m | |
Chimarra chiangmaiensis MALICKY & CHANTARAMONGKOL, 1989 | + | P | |||
Chimarra concolor ULMER, 1951 | + | S | Loc.10:1m, (1f) | ||
Chimarra gunungkawi MALICKY, 1995 | + | + | |||
Chimarra jacobsoni ULMER, 1951 | + | + | |||
Chimarra mahalaleel MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.5:1m | |||
Chimarra sythoffi ULMER, 1951 | + | ||||
Chimarra thienemanni ULMER, 1951 | + | + | P, S | ||
Chimarra xumappa MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.7:1m, 2f | |||
Chimarra yskal MALICKY, 1989 | + | ||||
Gunungiella aguha MELNITSKY & IVANOV, 2010 | + | Loc.1:7m, 1f; Loc.3:1m | |||
Gunungiella britomartis MALICKY, 1998 | + | ||||
Gunungiella kalliope MALICKY, 2004 | + | ||||
Gunungiella reducta ULMER, 1913 | + | ||||
Pseudoneureclipsis ramosa ULMER, 1913 | + | + | + | P, S, Wd | Loc.1:3m, 6f; Loc.3:2f; Loc.4:3f; Loc.7:5m, 3f |
POLYCENTROPODIDAE Ulmer, 1903 | |||||
Polyplectropus gedehensis ULMER, 1951 | + | ||||
Polyplectropus jahzeel MALICKY & MEY, 2011 | + | ||||
Polyplectropus javanicus ULMER, 1905 | + | S | |||
Polyplectropus kristyantoi MALICKY, 1998 | + | ||||
Nyctiophylax baydeom MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.9:1m | |||
ECNOMIDAE Ulmer, 1903 | |||||
Ecnomus anakagung MALICKY, 1995 | + | + | Loc.10:1m | ||
Ecnomus jethet MALICKY, IVANOV & MELNITSKY, 2011 | + | ||||
Ecnomus obtusus ULMER, 1910 | + | S | |||
Ecnomus quordaio MALICKY, 1993 | + | S, P | Loc.8:2m, (1f) | ||
Ecnomus robustior ULMER, 1951 | + | P, S | |||
Ecnomus serratus ULMER, 1930 | + | + | S | ||
Ecnomus tjurupensis ULMER, 1951 | + | S | |||
Pseudoneureclipsis ramosa ULMER, 1913 | + | + | + | P, S, Wd | Loc.1:3m, 6f; Loc.3:2f; Loc.4:3f; Loc.7:5m, 3f |
PSYCHOMYIIDAE Walker, 1852 | |||||
Paduniella kalamos MALICKY, 2004 | + | + | + | S | Loc.1:27m, (23f); Loc.2:1m; Loc.3:9m, (1f); Loc.4:15m; Loc.7:9m, (4f); Loc.9:1m, (10f) |
Paduniella koehleri MALICKY, 1995 | + | + | + | Loc.5:3m; Loc.8:1m, (5f) | |
Paduniella semarangensis ULMER, 1913 | + | + | S, P | ||
Paduniella trichobogiella MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.4:3m | |||
Psychomyia anaksusuan MALICKY, 1995 | + | ||||
Psychomyia capillata ULMER, 1910 | + | P, S | |||
Psychomyia feuerborni ULMER, 1951 | + | + | + | S | Loc.1:1m; Loc.4:4m; Loc.6:16m, 16f |
Psychomyia kalais MALICKY, 2004 | + | Loc.9:7m; Loc.10:5m, (3f) | |||
Psychomyia monto MALICKY & CHANTARAMONGKOL, 1993 | + | P | |||
Psychomyia thienemanni ULMER, 1951 | + | P, S | |||
Tinodes dedan MALICKY, 2009 | + | ||||
Tinodes flavopunctatus ULMER, 1910 | + | + | Loc.7:6m; Loc.8:2m, (5f); Loc.9:3m, (9f); Loc.10:1m | ||
Tinodes ihalauwi MALICKY, 1998 | + | ||||
Tinodes katreus MALICKY, 2004 | + | ||||
Tinodes kawiensis MALICKY, 1995 | + | + | Loc.1:16m; Loc.3:1m; Loc.6:1m | ||
Tinodes kepheus MALICKY, 2004 | + | ||||
Tinodes luhurensis MALICKY, 1995 | + | + | Loc.1:47m, (9f); Loc.4:20m, (46f) | ||
Tinodes mataram MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.1:52m; Loc.2:1m | |||
Tinodes methusael MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.1:1m; Loc.4:2m | |||
Tinodes moab MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.10:1m | |||
Tinodes noah MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.10:1m | |||
Tinodes prihatmoi MALICKY, 1998 | + | ||||
Tinodes pujungan MALICKY, 1995 | + | Loc.7:5m, (3f) | |||
Tinodes saul MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.8:5m; Loc.10:3m | |||
Tinodes simeon MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.9:5m, (7f) | |||
Tinodes tegenungan MALICKY, 1995 | + | ||||
Tinodes timotii MALICKY, 1998 | + | ||||
Tinodes zibeon MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.1:1m | |||
Trawaspsyche weilgunii MALICKY, 2004 | + | ||||
XIPHOCENTRONIDAE Ross, 1949 | |||||
Melanotrichia samaconius MALICKY & CHANTARAMONGKOL, 1992 | + | + | P | Loc.6:11m | |
HYDROPSYCHIDAE Curtis, 1835 | |||||
Diplectrona aspersa ULMER, 1905 | + | ||||
Diplectrona aurovittata ULMER, 1906 | + | + | + | P, S | Loc.1:5m, 2f |
Diplectrona extrema BANKS, 1920 | + | K, S | |||
Diplectrona jacobsoni ULMER, 1909 | + | S | |||
Diplectrona lavinia MALICKY, 2002 | + | B | |||
Diplectrona pseudofasciata ULMER, 1909 | + | B, S, P, Wd | |||
Diplectrona salakensis ULMER, 1951 | + | ||||
Diplectrona ungaranica ULMER, 1951 | + | S | |||
Oestropsyche vitrina HAGEN, 1859 | + | + | B, S, P, Wd | ||
Polymorphanisus nigricornis WALKER, 1852 | + | P, S, Wd | |||
Polymorphanisus ocularis ULMER, 1906 | + | B, P, S, Wd | |||
Polymorphanisus scutellatus BANKS, 1939 | + | B, S, | |||
Macrostemum fastosum WALKER, 1852 | + | + | P, S, Wd | Loc.7:2f | |
Macrostemum fenestratum ALBARDA, 1887 | + | B, P, S | |||
Amphipsyche meridiana ULMER, 1909 | + | P, S, Wd | |||
Amphipsyche petiolata ULMER, 1930 | + | B, P, S | |||
Hydromanicus dilatus BETTEN, 1909 | + | ||||
Hydromanicus flavoguttatus ALBARDA, 1881 | + | S | |||
Hydromanicus irroratus BRAUER, 1865 | + | ||||
Hydromanicus ornatus ULMER, 1951 | + | ||||
Hydromanicus unicolor ULMER, 1951 | + | ||||
Potamyia aureipennis ULMER, 1930 | + | S | Loc.8:16m | ||
Potamyia dentifera ULMER, 1930 | + | ||||
Potamyia flavata BANKS, 1934 | + | + | + | P, S | Loc.4:(5f); Loc.5:1m, 22f |
Cheumatopsyche brevis ULMER, 1930 | + | ||||
Cheumatopsyche concava ULMER, 1930 | + | + | S | Loc.6:(2f); Loc.7:8m, (40f) | |
Cheumatopsyche contexta ULMER, 1951 | + | B, S | |||
Cheumatopsyche dodan MALICKY & MEY, 2009 | + | Loc.1:1m | |||
Cheumatopsyche globosa ULMER, 1910 | + | + | B, S, P | ||
Cheumatopsyche kebumena MALICKY, 1997 | + | ||||
Cheumatopsyche kraepelini ULMER, 1905 | + | + | |||
Cheumatopsyche lucida ULMER, 1907 | + | + | + | B, P, S, Wd | Loc.4:1m, (6f); Loc.5:7m, (25f); Loc.8:23m, (28f) |
Cheumatopsyche misma MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.1:2f | |||
Cheumatopsyche sindanggala MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.1:8m, (227f); Loc.4:3m, (6f) | |||
Hydropsyche annulata ULMER, 1905 | + | + | Loc.6:1m; Loc.8:26m, (numerous f); Loc.9:1m, (12f); Loc.10:2m, (4f) | ||
Hydropsyche bryanti BANKS, 1939 | + | S | |||
Hydropsyche didyma MEY, 1999 | + | Loc.1:8m, (20f); Loc.3:3m, (4f) | |||
Hydropsyche doctersi ULMER, 1951 | + | P | |||
Hydropsyche irroratella ULMER, 1951 | + | B? | |||
Hydropsyche javanica ULMER, 1905 | + | ||||
Hydropsyche kottos MALICKY, 2004 | + | ||||
Hydropsyche mesech MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.7:4m, (4f) | |||
Hydropsyche renschi MEY, 1999 | + | + | S | Loc.1:1m; Loc.4:3m, (3f); Loc.6:1m | |
Hydropsyche saranganica ULMER, 1951 | + | + | + | S, Wd | Loc.1:1m; Loc.4:2m; Loc.6:4m, (11f) |
Hydropsyche sasakorum MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.1:6m, (3f); Loc.3:4m, (5f); Loc.4:1m | |||
Hydropsyche sinear MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.3:1m | |||
Hydropsyche staphylostirpis MEY, 1998 | + | ||||
LEPIDOSTOMATIDAE Ulmer, 1903 | |||||
Lepidostoma brevior ULMER, 1913 | + | + | S | Loc.7:1m | |
Lepidostoma conjunctum BANKS, 1934 | + | B, S | |||
Lepidostoma diehli WEAVER, 1989 | + | + | S | Loc.1:8m, 3f | |
Lepidostoma jacobsoni ULMER, 1910 | + | S | |||
Lepidostoma kephalos MALICKY, 2004 | + | ||||
Lepidostoma lombokensis MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.1:1m, (1f) | |||
Lepidostoma picea ULMER, 1913 | + | + | S | Loc.7:2m, 2f | |
BRACHYCENTRIDAE Ulmer, 1903 | |||||
Micrasema ripat MALICKY, IVANOV & MELNITSKY, 2011 | + | Loc.10:1m | |||
GOERIDAE Ulmer, 1903 | |||||
Goera conclusa ULMER, 1905 | + | + | + | Loc.1:3m, 1f | |
Goera pugnio ULMER, 1951 | + | + | S? | Loc.6:1m | |
Goera ranauana ULMER, 1951 | ? | S | |||
Gastrocentrides sumatranus ULMER, 1930 | + | + | + | S, P, Wd | Loc.4:1f; Loc.7:2m, 3f |
HELICOPSYCHIDAE Ulmer, 1906 | |||||
Helicopsyche lata Ulmer, 1951 | + | S, P | |||
LEPTOCERIDAE Leach, 1815 | |||||
Adicella byblis MALICKY, 1998 | + | + | S | Loc.1:14m, 9f; Loc.4:2m | |
Adicella evadne SCHMID, 1994 | + | + | S, P, Wd | Loc.4:4m; Loc.7:1m | |
Adicella kanake MALICKY & CHANTARAMONGKOL, 2002 | + | S, P | Loc.1:3m, (5f) | ||
Adicella pulcherrima ULMER, 1906 | + | S | |||
Adicella oviformis ULMER, 1951 | + | + | |||
Leptocerus ciconiae MALICKY, 1993 | + | S, P | |||
Setodes karnyi ULMER, 1930 | + | + | S | Loc.1:1m | |
Setodes klakahanus ULMER, 1951 | + | + | + | Loc.4:1m; Loc.5:1m | |
Setodes larentia MALICKY & CHANTARAMONGKOL, 2006 | + | + | S | Loc.4:2m, (4f); Loc.7:1m, (5f) | |
Setodes nauplios MALICKY & CHANTARAMONGKOL, 2006 | + | ||||
Setodes uncinatus ULMER, 1913 | + | S | |||
Trichosetodes handschini ULMER, 1951 | + | Loc.8:11m, (6f); Loc.9:2m, (5f) | |||
Oecetis karnyi MALICKY, 2009 | + | ||||
Oecetis kyparissos MALICKY, 2005 | + | + | Loc.4:2m, 9f; Loc.5:1m | ||
Oecetis pelops MALICKY, 2006 | + | + | Loc.3(1f); Loc.7:(16f) | ||
Oecetis singularis ULMER, 1930 | + | S | |||
Oecetis spatula CHEN & MORSE, 1991 | + | Wd | |||
Oecetis tripunctata FABRICIUS, 1793 | + | + | + | B, P, S, Wd | Loc.4:1m, 6f |
Tagalopsyche brunnea ULMER, 1905 | + | + | B, S, P | Loc.4:1m | |
Triaenodes pelias MALICKY, 2005 | + | S | |||
Parasetodes respersella RAMBUR, 1842 | + | B, P, S, Wd | |||
Triplectides indica WALKER, 1852 | + | + | S, P, Wd | Loc.4:5f | |
CALAMOCERATIDAE Ulmer, 1905 | |||||
Anisocentropus flavomarginatus ULMER, 1906 | + | B, S | |||
Anisocentropus handschini ULMER, 1951 | + | ||||
Anisocentropus ulmeri MALICKY, 1998 | + | ||||
Ganonema fuscipenne ALBARDA, 1881 | + | + | + | P, S | Loc.1:1f; Loc.4:1f; Loc.6:3m |
ODONTOCERIDAE Wallengren, 1891 | |||||
Marilia javana ULMER, 1951 | + | ||||
Marilia sumatrana ULMER, 1951 | + | S | |||
Total: 202 species | 146 | 73 | 61 | Collected by V.Ivanov, S.Melnitsky, N. Kluge: 84 species |
Synopsis of the number of species in Thailand, Sumatra, Java, Bali, and Lombok (except Odontoceridae: see text)
Taxa/family, genus | Thailand | Sumatra | Java | Bali | Lombok |
---|---|---|---|---|---|
RHYACOPHILIDAE | |||||
Rhyacophila | 37 | 7 | 3 | 2 | 2 |
GLOSSOSOMATIDAE | |||||
Glossosoma | 3 | 2 | 2 | 0 | 0 |
Agapetus | 14 | 5 | 4 | 1 | 1 |
HYDROPTILIDAE | |||||
Hydroptila | 33 | 14 | 5 | 3 | 2 |
Microptila | 2 | 0 | 0 | 2 | 2 |
Tricholeiochiton | 1 | 1 | 1 | 0 | 0 |
Oxyethira | 4 | 4 | 1 | 1 | 0 |
Ugandatrichia | 5 | 1 | 1 | 0 | 0 |
Orthotrichia | 32 | 11 | 5 | 3 | 2 |
Saranganotrichia | 2 | 0 | 1 | 0 | 0 |
Scelotrichia | 5 | 3 | 1 | 0 | 4 |
Chrysotrichia | 13 | 5 | 2 | 2 | 0 |
Plethus | 9 | 1 | 2 | 3 | 1 |
Parastactobia | 2 | 1 | 1 | 1 | 1 |
Stactobia | 7 | 0 | 4 | 2 | 2 |
PHILOPOTAMIDAE | |||||
Chimarra | 60 | 21 | 10 | 8 | 3 |
Gunungiella | 9 | 3 | 3 | 0 | 1 |
STENOPSYCHIDAE | |||||
Stenopsyche | 8 | 1 | 0 | 0 | 0 |
POLYCENTROPODIDAE | |||||
Polyplectropus | 13 | 14 | 2 | 2 | 0 |
Nyctiophylax | 20 | 6 | 1 | 0 | 0 |
ECNOMIDAE | |||||
Ecnomus | 51 | 16 | 6 | 2 | 1 |
Pseudoneureclipsis | 41 | 5 | 1 | 1 | 1 |
PSYCHOMYIIDAE | |||||
Paduniella | 13 | 2 | 3 | 3 | 3 |
Psychomyia | 24 | 10 | 5 | 2 | 1 |
Tinodes | 19 | 5 | 11 | 5 | 5 |
Trawaspsyche | 0 | 0 | 1 | 0 | 0 |
XIPHOCENTRONIDAE | |||||
Melanotrichia | 4 | 1 | 1 | 1 | 0 |
HYDROPSYCHIDAE | |||||
Diplectrona | 8 | 10 | 8 | 1 | 1 |
Oestropsyche | 1 | 1 | 1 | 1 | 0 |
Polymorphanisus | 5 | 5 | 3 | 0 | 0 |
Macrostemum | 12 | 8 | 2 | 1 | 0 |
Amphipsyche | 2 | 3 | 2 | 0 | 0 |
Hydromanicus | 13 | 5 | 5 | 0 | 0 |
Potamyia | 13 | 3 | 3 | 1 | 1 |
Cheumatopsyche | 29 | 11 | 7 | 4 | 4 |
Hydropsyche | 30 | 13 | 7 | 4 | 6 |
LEPIDOSTOMATIDAE | |||||
Lepidostoma | 41 | 15 | 5 | 3 | 2 |
BRACHYCENTRIDAE | |||||
Micrasema | 6 | 0 | 1 | 0 | 0 |
GOERIDAE | |||||
Goera | 16 | 6 | 2 | 2 | 1 |
HELICOPSYCHIDAE | |||||
Helicopsyche | 14 | 3 | 1 | 0 | 0 |
LEPTOCERIDAE | |||||
Adicella | 20 | 12 | 3 | 2 | 3 |
Leptocerus | 42 | 8 | 0 | 1 | 0 |
Setodes | 63 | 17 | 4 | 2 | 3 |
Trichosetodes | 7 | 3 | 1 | 0 | 0 |
Oecetis | 50 | 39 | 4 | 3 | 3 |
Tagalopsyche | 3 | 3 | 1 | 0 | 1 |
Triaenodes | 11 | 5 | 1 | 0 | 0 |
Parasetodes | 1 | 1 | 0 | 1 | 0 |
Triplectides | 1 | 1 | 1 | 0 | 1 |
CALAMOCERATIDAE | |||||
Anisocentropus | 10 | 5 | 3 | 0 | 0 |
Ganonema | 4 | 1 | 1 | 1 | 1 |
The caddisfly faunas of the three islands correspond quite well. It is evident from the
Surprises are also possible when species described from far distant regions will be found. For example, Adicella kanake Malicky & Chantaramongkol and Hydroptila rumpun Wells & Huisman found on Lombok were known previously from Sumatra, Peninsular Malaysia and Thailand, but were never collected on Java and Bali. The microcaddisfly Scelotrichia jari Wells & Huisman from Lombok lives on Borneo (or Kalimantan Island on some maps) and Peninsular Malaysia but was not found on Java and Bali. Similarly, Paduniella dendrobia Malicky & Chantaramongkol was described from high altitude of Doi Inthanon in northern Thailand and Phoupanpsyche caroli Malicky was described from the mountains of Laos, but both were later found in the higher elevations of Mount Kinabalu on Borneo, several thousands of kilometers away. There are some instances of species like Hydropsyche renschi Mey and Lepidostoma diehl (Weaver) found on both Lombok and Bali but not on Java Island.
Endemics of generic or even more-inclusive categories may scarcely exist on these islands. The genus Trawaspsyche with the single species T. weilgunii Malicky, which is an extremely derived form in relationship with Tinodes, is known only from Java. Similar cases are Temburongpsyche on Borneo and Padangpsyche and Edidiehlia on Sumatra. Neither an evolution center nor numerous centers can be recognized on the three islands. A relatively high number of Tinodes species may mean a rather active and recent regional speciation process.
Continuous impoverishment of the Asiatic mainland faunas in the direction of the Lesser Sunda Islands is obvious (
Collecting intensity plays a major role in the knowledge of a fauna. Of Thailand and (northern) Sumatra it is well known, of Western Java and Bali it is relatively well known, too. For Lombok, the results of the first visit are being presented here. Our experience shows that the first intensive collections in an unknown area may yield about 75% unknown species, followed by the second visit results constituting about 20%, while later the percentage of the new species decreases dramatically. We conclude that each of Bali and Lombok may have less than 100 species in total. Such a dramatic decrease of the species numbers from the continent to the islands is not a result of poor collections. Instead it is caused by the island impoverishment and remote position from the continent. The number of caddisfly species in an area of similar size in Thailand is three times larger than in Sumatra. Supposed extreme faunal richness of rainforests does not apply to the aquatic insects, like caddisflies, of this region. To compare with extratropical Central and Southern Europe: about 300 (Austria, Switzerland, Germany, European Russia) to 400 species (Italy, Turkey) are known from these countries.
The well-known Wallace’s line which runs between Borneo and Bali on one side and Sulawesi and Lombok on the other side (
It is obvious that there is not an absolute border and the division is rather based on the deep sea waters between Bali and Lombok which remained deep even during the Pleistocene glaciations when the sea level was much lower (
Which Trichoptera species or groups may be considered to be the elements of Asiatic or Australian origin? Many families and genera have wide areas in the region, overlapping the borders of the continents (Chimarra, Hydropsyche, Cheumatopsyche, Oecetis). Some groups are important members of the Asiatic fauna, though they may be represented by very few species in Australia or New Guinea (Agapetus, Tinodes). On the other hand, very few groups typical for the Australian fauna are present in Asia, and the species numbers are low in each of these instances. The Australian Trichoptera have been studied for a long time with comprehensive data summarized by
It is of highest zoogeographical interest to collect representative samples from the other Sunda Islands east of Lombok, and from the Moluccas. One may wonder that no such material is available in museums despite the intensive collecting activity of many other entomologists. The results of the faunal studies in Wallacea are also of high conservation importance. They can be used to steer both current and future efforts that try to preserve endemic flora and fauna of this uniquely diverse part of the biosphere.
The caddisfly fauna of the islands of Java, Bali and Lombok is largely homogenous, and there is no gap or border between Bali and Lombok which would be expected from the hypothesis of Wallace’s line. A continuous impoverishment of the caddisfly fauna from the Asiatic continent over the chain of islands is striking. This gradual impoverishment is observed in species number as well as in the numbers of genera or families. The Trichoptera fauna of the three islands is entirely Asiatic. There is no influence from the Australian fauna. The caddisflies of the Sunda Islands east of Lombok as well as those of the Moluccas are unknown, and their study is much required.
This research was supported by grants from the Russian Foundation for Basic Research, grants 11-04-00076 and the Federal Support Program for Leading Scientific Schools NSH-3332.2010.4. The authors are grateful to two reviewers for their valuable comments.