Odonata of Sungai Bebar, Pahang,
Malaysia, with four species recorded for the first time from mainland Asia
Rory A. Dow 1, Yong Foo Ng2 & Chee Yen Choong 3
1NCB Naturalis, P.O. Box 9517, 2300 RA
Leiden, The Netherlands
2,3Centre for Insect Systematics,
Faculty of Sciences and Technology, Universiti Kebangsaan Malaysia, 43600
Bangi, Selangor D.E. Malaysia
Email: 1 rory.dow230@yahoo.co.uk
(corresponding author), 2 ng_yf@ukm.my, 3 cychoong@ukm.my
Date of publication (online): 26 March 2012
Date of publication (print): 26 March 2012
ISSN 0974-7907 (online) | 0974-7893 (print)
Editor: Albert
Orr
Manuscript details:
Ms # o3041
Received 19 December 2011
Final received 06 January 2012
Finally accepted 13 February 2012
Citation:Dow, R.A., Y.F. Ng & C.Y. Choong (2012). Odonata of Sungai Bebar, Pahang,
Malaysia, with four species recorded for the first time from mainland Asia. Journal of Threatened Taxa4(3): 2417Ð2426.
Copyright: ©
Rory A. Dow, Yong Foo Ng & Chee Yen Choong 2012. Creative Commons
Attribution 3.0Unported License. JoTT allows unrestricted use of this article
in any medium for non-profit purposes, reproduction and distribution by
providing adequate credit to the authors and the source of publication.
Author Details: Rory A. Dow is a research associate at NCB Naturalis, Leiden,
the Netherlands. His research interests are in the faunistics and taxonomy of
Asian Odonata. He has extensive experience of working in south-east Asia,
especially in Malaysia.
Yong Foo Ng is an insect
taxonomist in the School of Environmental and Natural Resource Sciences,
Universiti Kebangsaan Malaysia (UKM) and a member of the Centre for Insect
Systematics, UKM. His research is focused on Asian Odonata and Thysanoptera. He
collaborates with researchers from CSIRO, Entomology Department, Canberra,
Australia and NCB Naturalis, Leiden, Netherlands
Chee Yen Choong is a lecturer of
School of Environmental and Natural Resource Sciences, Universiti Kebangsaan
Malaysia (UKM). He is an associate member of the Centre for Insect Systematics,
UKM, and has a profound interest in the dragonflies and damselflies of
Peninsular Malaysia.
Author Contribution: RAD
identification of, and information on, the Odonata collected, collection of
specimens. YFN information on the area sampled, and on peat swamp forest in
Peninsular Malaysia; organization of the sampling trip. CYC identification of,
and information on, the Odonata collected, collection of specimens,
photography.
Author
Contribution: RAD identification of, and information
on, the Odonata collected, collection of specimens. YFN information on the area
sampled, and on peat swamp forest in Peninsular Malaysia; organization of the
sampling trip. CYC identification of, and information on, the Odonata
collected, collection of specimens, photography.
Acknowledgements: The
authors wish to thank the Pahang Forestry Department for granting permission
for sampling of Odonata in the Sungai Bebar, Runchang, Pahang. This study was funded by research
grants UKM-GUP-ASPL-07-04-048 and UKM-ST-06-FRGS0184-2010. We also wish to thank Professor Yong
Hoi Sen for his company and stimulating conversation during our fieldwork at
Sungai Bebar, and Doctor Albert Orr for his continued support of our work. Thanks are also due to Mr Marcel
Silvius for allowing us to report his photographic record of Tyriobapta laidlawi here.
Abstract:Records are presented of Odonata collected in September
2009 from the Sungai Bebar and the surrounding area, in Pekan Forest Reserve,
southeastern Pahang, Peninsular Malaysia. A total of 50 species from nine families were collected. Two of the species listed, Amphicnemis bebar andA. hoisen,
were first discovered during this survey. Another four previously known species were recorded in mainland Asia for
the first time: Elattoneura
coomansi, Elattoneura
longispina, Brachygonia
ophelia and Tyriobapta
laidlawi.
Keywords:Damselflies, dragonflies, Malaysia, new records, Odonata, Pahang, peat swamp
forest, Pekan Forest Reserve, Sungai Bebar.
For figures, images, tables -- click here
Swamp forest in general,
and peat swamp forest in particular, has been little surveyed for Odonata in
Peninsular Malaysia. Norma-Rashid
et al. (2001) reported on odonate surveys at Tasek Bera, a lake in Pahang with
a large area of swamp forest around it, including peat swamp forest; however,
most of the collecting reported in that publication appears to have been made
on the lake and surrounding river channels; little sampling appears to have
taken place inside the swamp forest. HŠmŠlŠinen (2000) includes a number of records made in swamp forests of
various types. In 2006, CYC collected odonates from swamp
forests in Panti Forest Reserve, Johor (Choong 2009). Other records from swamp forest in Peninsular Malaysia are
scattered amongst the odonatological literature of the last century.
In the present survey,
six species not previously reported from Peninsular Malaysia were found. Two
were of the coenagrionoid genus Amphicnemisand new to science; these species (A.
bebar and A. hoisen) were described by Dow et al. (2010). The other four species, two members of
the Protoneuridae (Elattoneura
coomansi Lieftinck and E. longispina Lieftinck) and two from the
Libellulidae (Brachygonia
ophelia Ris and Tyriobapta
laidlawi Ris), had not previously been recorded from mainland
Asia but were known either from Borneo, or Borneo and the Indonesian Islands of
Belitung and Bangka. Here we list
all the species collected in the Sungai Bebar area, with details of specimens
collected and notes on species of particular interest.
MATERIALS
AND METHODS
Sampling was carried out
at the locations listed below (Fig. 1), from 20Ð24 September 2009:
(1) On the Sungai Bebar
(Image 1) between locations 4 and 6.
(2) Margin of the Sungai
Bebar with emergent vegetation, chiefly Pandanus, at the water margin and in disturbed
scrub inland, 3016.845ÕN & 103013.894ÕE and 3016.604ÕN
& 103014.446ÕE.
(3) Tributary of the
Sungai Bebar (Image 2) and surrounding highly disturbed swamp forest, 3017.134ÕN
& 103014.878ÕE.
(4) Highly disturbed
swamp forest at 3015.650ÕN & 103014.687ÕE.
(5) Less disturbed swamp
forest (Image 3) with stream, 3018.696ÕN & 103014.120ÕE.
(6) Highly disturbed
swamp forest (Image 4) at 3019.372ÕN & 103015.136ÕE.
(7) Black water drains
and a stream in a mosaic of highly disturbed forest and open meadow and road, 3017.078ÕN
& 103013.559ÕE.
(8) A pond at the edge
of degraded forest at 3017.173ÕN & 103013.368ÕE.
(9) Water filled wheel
ruts near location 2.
Adult specimens were
collected using handheld nets. Sampling on the Sungai Bebar was conducted from a boat. Specimens were preserved either by
treatment with acetone, drying or immersion in ethanol. The family level taxonomy used below follows
that in Orr (2005).
The material collected
is held in either the Centre for Insect Systematics at Universiti Kebangsaan
Malaysia (UKM), the Netherlands Centre for Biodiversity Naturalis (RMNH),
collection CYC or collection RAD. Material was identified to species using a stereomicroscope, with
reference to relevant literature, and direct comparison with material,
including type material, held in The Natural History Museum, London (BMNH) and
RMNH.
RESULTS
A total of 218 individual Odonata
specimens were collected, comprising 50 species in nine families. Species,
locations and number of specimens collected at each location on a given date
are listed below, together with notes on species of particular interest. For
species of Amphicnemis, details of specimens collected at
Sungai Bebar are given in Dow et al. (2010) and are not repeated here. The species recorded at each location
sampled are summarised in Table 1.
Zygoptera
(i) Podolestes buwaldai Lieftinck, 1940 Ñ There are few
published records of this species, originally described from Sumatra (Lieftinck
1940). HŠmŠlŠinen (2000) made the
first report for Peninsular Malaysia; Kalkman (2004) and Choong et al. (2008)
also recorded it from Malaysia. At
Sungai Bebar it was moderately common in the least disturbed swamp forest area
sampled. 5:3 male, 2 female, RAD,
22.ix; 3 male, 2 female, RAD, 23.ix; 2 males, 2 females, CYC, 23.ix; 6:1 male,
1 female, RAD, 24.ix; 1 female, CYC, 24.ix.
(i) Elattoneura aurantiaca (Selys, 1886) Ñ 2:5 male, 1
female, RAD, 20.ix; 1 male, 1 female (in tandem), CYC, 20.ix; 4:1 male, RAD,
21.ix; 5:3 male, RAD, 22.ix; 2 males, 1 female, RAD, 23.ix; 6:2 males, RAD,
23.ix.
(ii) Elattoneura coomansi Lieftinck, 1937 Ñ This is the
first record of this species from Peninsular Malaysia; it is otherwise known
from Kalimantan and Bangka and Belitung islands (Lieftinck 1954). Most of the specimens collected were
taken amongst Pandanusat the edge
of Sungai Bebar 2:4 male, RAD, 20.ix; 5:1 male, RAD, 23.ix; 6:1 female, RAD,
24.ix.
(iii) Elattoneura longispina Lieftinck, 1937 Ñ This species has
not been recorded from mainland Asia before; it was described from west
Kalimantan and is also known from Sarawak (Dow & Unggang 2010) and Belitung
(Lieftinck 1954). One male was
collected at Sungai Bebar. However, in 2006 CYC collected two tandem pairs of this species from
Pondok Tanjung Forest Reserve, northern Perak, a small peat swamp forest; these
specimens were misidentified as Elattoneura analis (Selys 1860) and the mistake was only
discovered in early 2010. This
species is expected to have wider distribution in Peninsular Malaysia and might
also occur in southern Thailand. 5:1 male, CYC, 22.ix.
(iv) Prodasineura humeralis (Selys, 1860) Ñ 5:1 male, CYC,
23.ix.
(i) Agriocnemis femina (Brauer, 1868) Ñ 6:1 female, RAD,
24.ix.
(ii) Agriocnemis minima (Selys, 1877) Ñ 9:1 male, 2
females (1 pair in tandem), RAD, 21.ix; 1 male, CYC, 21.ix.
(iii) Agriocnemis nana (Laidlaw, 1914) Ñ 7:1 male, 2
females, CYC, 20.ix.
(iv) Amphicnemis bebar Dow et al., 2010 Ñ See Dow et al. (2010) for a discussion
of this and the next two species. Locations 5 and 6 (Image 5).
(v) Amphicnemis gracilis KrŸger, 1898 Ñ Locations 3 and 6.
(vi) Amphicnemis hoisen Dow et al., 2010 Ñ Location 5 (Image 6).
(vii) Archibasis incisura Lieftinck, 1949 Ñ This is a rather
local species, and its preferred habitat is probably streams and rivers in low
pH swamp forest, for instance see Dow & Unggang (2010). 2:2 male, RAD, 20.ix; 1 male, CYC,
23.ix.
(viii) Archibasis melanocyana (Selys, 1877) Ñ 5:1 male, CYC,
23.ix; 1 male, CYC, 24.ix.
(ix) Ceriagrion cerinorubellum (Brauer, 1865) Ñ 7:1 male, RAD,
20.ix; 1 male, CYC, 20.ix.
(x) Ceriagrion species Ñ A single female, identical in general
appearance to C.
cerinorubellum,
collected in peat swamp forest. It
differs from C.
cerinorubellum,
and all other species of Ceriagrion, in having the central part of the
pronotal posterior lobe deeply and squarely excised; this does not appear to be
the result of damage to the specimen, but the possibility that it is simply an
abnormal individual of C.
cerinorubellum cannot
be ruled out unless further examples are collected. 5:1 female, RAD, 23.ix.
(xi) Ischnura senegalensis (Rambur, 1842) Ñ 7:1 male, CYC,
20.ix.
(xii) Pseudagrion rubriceps Selys, 1876 Ñ 1:1 male, RAD,
20.ix.
(xiii) Pseudagrion williamsoni Fraser, 1922 Ñ 1:1 male, RAD,
20.ix; 2:2 males, CYC, 20.ix; 8:1 male, RAD, 21.ix.
(i) Copera ciliata (Selys, 1863) Ñ 7:1 female, CYC,
20.ix.
(ii) Copera vittata (Selys, 1863) Ñ 6:1 male, RAD,
24.ix.
Gomphidae
(i) Gomphidia abbotti Williamson, 1907 Ñ 1:1 male, RAD,
22.ix.
(ii) Ictinogomphus acutus (Laidlaw, 1914) Ñ 1:1 male, RAD,
21.ix; 1 male, RAD, 22.ix; 2 males, CYC, 22.ix.
(iii) Ictinogomphus decoratus melaenops (Selys, 1858) Ñ 1:1 male, RAD,
22.ix.
(iv) Macrogomphus decemlineatus (Selys, 1878) Ñ 1:1 male, RAD,
21.ix; 1 male, CYC, 24.ix.
(i) Oligoaeschna species Ñ It has not proved possible to identify the
single female collected reliably to species. 4:1 female, RAD, 21.ix.
(i) Epophthalmia vittigera (Rambur, 1842) Ñ 1:1 male, CYC,
21.ix.
(ii) Macromia cincta Rambur, 1842 Ñ 1:1 male, RAD,
22.ix; 1 male, CYC, 21.ix; 1 male, CYC, 22.ix; 7:1 male, RAD, 20.ix.
(i) Brachydiplax chalybea Brauer, 1868 Ñ 7:1 male, CYC,
20.ix; 1 male, CYC, 22.ix; 8:1 male, RAD, 21.ix.
(ii) Brachygonia oculata (Brauer, 1878) Ñ 4:1 male, RAD,
21.ix; 5:1 female, CYC, 23.ix; 6:1 male, RAD, 24.ix; 7:1 male (in forest), RAD,
21.ix; 2 males (in forest), CYC, 21.ix.
(iii) Brachygonia ophelia Ris, 1910 Ñ This very local swamp
forest species has not been recorded from Peninsular Malaysia until now; it is
otherwise only known from scattered locations in Borneo (e.g. Lieftinck 1954,
Orr 2001 & 2003). Image 7. 5:2
males, RAD, 22.ix; 1 male, 1 female, RAD, 23.ix; 2 males, CYC, 23.ix.
(iv) Chalybeothemis fluviatilis Lieftinck, 1933 Ñ This species is
known from scattered locations across Borneo, Sumatra, Belitung, Singapore and
Peninsular Malaysia and southern Thailand (Dow et al. 2007). It often appears to prefer low pH
habitats, but occurs on MacRitchie Reservoir in Singapore (Tang et al.
2010). It was common on parts of
Sungai Bebar during the sampling period. Image 8. 1:1 male, RAD, 21.ix; 1 male, RAD, 22.ix; 2:1 male, RAD, 20.ix;
3:2 males (on the tributary); RAD, 20.ix; 2 males (on the tributary), CYC,
20.ix; 8:1 male, RAD, 21.ix.
(v) Nannophya pygmaea Rambur, 1842 Ñ 7:1 male, RAD,
20.ix; 1 male, CYC, 21.ix.
(vi) Nesoxenia lineata (Selys, 1879) Ñ 4:2 males, CYC,
21.ix.
(vii) Neurothemis fluctuans (Fabricius, 1793) Ñ 7:1 male, RAD,
20.ix; 1 male, CYC, 20.ix.
(viii) Onychothemis testacea Laidlaw, 1902 Ñ 1:1 male, CYC,
21.ix.
(ix) Orchithemis pruinans (Selys, 1878) Ñ 4:5 males, RAD,
21.ix; 5:1 female, RAD, 22.ix; 1 male, RAD, 23.ix; 2 males, CYC, 21.ix.
(x) Orchithemis pulcherrima Brauer, 1878 Ñ 3:1 male, CYC,
20.ix.
(xi) Orthetrum chrysis (Selys, 1891) Ñ 2:1 male, RAD,
20.ix; 7:1 male, CYC, 20.ix.
(xii) Pantala flavescens (Fabricius, 1798) Ñ 2:1 female,
RAD, 21.ix; 1 male, CYC, 20.ix; 1 male, CYC, 21.ix.
(xiii) Pornothemis serrata KrŸger, 1902 Ñ 4:2 males, RAD,
21.ix; 2 males, 1 female, CYC, 21.ix; 5:1 male, RAD, 22.ix.
(xiv) Potamarcha congener (Rambur, 1842) Ñ 9:1 male, RAD,
20.ix; 1 male, CYC, 20.ix.
(xv) Rhyothemis aterrima Selys, 1891 Ñ 2:1 male, RAD, 20.ix;
1 male, CYC, 21.ix.
(xvi) Rhyothemis obsolescens Kirby, 1889 Ñ 2:1 male, RAD,
20.ix; 1 male, CYC, 20.ix; 4: 1 male, RAD, 21.ix.
(xvii) Rhyothemis phyllis (Sulzer, 1776) Ñ 2:1 female, RAD,
20.ix; 1 female, CYC, 20.ix.
(xviii) Rhyothemis pygmaea (Brauer, 1867) Ñ 5:1 male, RAD,
22.ix; 1 male, CYC, 23.ix; 1 male, CYC, 24.ix.
(xix) Risiophlebia dohrni (KrŸger, 1902) Ñ 3:1 male, RAD,
20.ix.
(xx) Tyriobapta laidlawi Ris, 1919 Ñ This species,
otherwise known from Borneo, has not been recorded from Peninsular Malaysia
before. It appears to be most
common in low pH swamp forest. A
convincing photographic record was also made in Ayer Hitam Forest Reserve in
Johor by M. Silvius of Wetlands International on 26.xi.2010. Image 9. 5:2 males, RAD, 22.ix; 1 male,
RAD, 23.ix; 1 male, CYC, 23.ix.
(xxi) Urothemis signata insignata (Selys, 1872) Ñ 7:1 male, RAD, 20.ix.
(xxii) Zyxomma petiolatum Rambur, 1842 Ñ 4:1 female, RAD,
21.ix.
Although we had modest
hopes of making interesting
finds at Sungai Bebar, we were not expecting to make six new records for
Peninsular Malaysia and mainland Asia in just five days of fieldwork. These discoveries demonstrate how
poorly surveyed Odonata have been in low pH swamp forest habitats in mainland
Southeast Asia; more discoveries can be expected with further collecting
effort.
Many parts of the peat
swamp habitat around Sungai Bebar are only accessible by small boat. The riverbanks and shallow parts of the
river have an extensive growth of Pandanus,
which at some points completely clogs the waterway. The Jakun (indigenous people living around Sungai Bebar)
normally burn the overgrown Pandanusduring the dry season to clear a passage. The clear, low pH waters and vegetation structure of the river appear to
provide an ideal habitat for a number of Odonata: Ictinogomphus acutus, I. decoratus, Macromia cincta, Chalybeothemis fluviatilis,Elattoneura auranticaand Pseudagrion williamsoniwere abundant along the entire section of the river sampled.
Despite the new records
made at Sungai Bebar, there were also some surprising absences from our
sample. In Borneo, species of the
coenagrionoid generaÑMortonagrionand TeinobasisÑare
almost invariably found in such habitats. Members of these genera, especially the small Mortonagrion, are typically
inconspicuous, but the authors have considerable experience of collecting
Odonata, and were looking out for these genera. However, the three species currently placed in Mortonagrion and
known from Peninsular MalaysiaÑM.
aborense (Laidlaw 1914), M. arthuri Fraser, 1942 and M. falcatum Lieftinck,
1934Ñare not necessarily swamp forest species (see Dow 2011 for a
discussion of M. arthuri). Four species of Teinobasis are known
from Peninsular Malaysia (Dow 2010): T.
cryptica Dow, 2010, T.
kirbyi Laidlaw, 1902, T. rajah Laidlaw, 1912, T. ruficollis (Selys,
1877); of these all except T.
kirbyi would be expected in the habitats at Sungai Bebar, and
are likely to be found there with further collecting.
In other respects the
odonate fauna of Sungai Bebar is similar to that of low pH swamp forest in
Borneo: rich in coengrionoids, especially Amphicnemis, and libellulids, poorer in numbers
of species from other families, but including a number of specialist species
from some of these families. The
protoneurid genus Elattoneura is well represented at
Sungai Bebar, with three species. All the Amphicnemis andElattoneura(except E. analis)
species of Peninsular Malaysia are inhabitants of alluvial swamp or peat swamp
forest. All of the Amphicnemis(except A. ecornutaSelys, 1889) and Elattoneura(again except E.
analis) species that have so far been recorded for Peninsular
Malaysia were found at Sungai Bebar. This suggests that the Sungai Bebar area still has enough high quality
habitat to sustain a high diversity of specialist peat swamp forest
species. Several gomphids were
collected on the Sungai Bebar, and more can be expected there, and on smaller
streams in the swamp forest. Of the Gomphidae so far recorded at Sungai Bebar, Ictinogomphus acutus appears
to be a specialist of low pH habitats (see Dow & Unggang 2010). Additional members of the Corduliidae,
for instance Hemicordulia
tenera Lieftinck, 1930, are to be expected. Swamp forest in SE
Asia is sometimes rich in members of the Aeshnidae, in particular species of Gynacantha and Heliaeschna. However,
the Aeshnidae are typically difficult to collect so that their diversity in an
area is normally only revealed over longer sampling periods; more than the
single species recorded to-date must occur in the Sungai Bebar area.
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