Oryx Vol 40 No 1 January 2006
© 2006 FFI, Oryx, 40(1), 1–6 doi:10.1017/S0030605306000147 Printed in the United Kingdom
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The diversity and activity patterns of wild felids in a secondary forest
in Peninsular Malaysia
J. Mohd. Azlan and Dionysius S.K. Sharma
these relatively secretive mammals. The most frequently
photographed species was tiger (38.5% of records) fol-
lowed by leopard (26.3%) and leopard cat (21.9%). The
presence of charismatic flagship species such as tiger
in this unprotected lowland dipterocarp secondary forest
will be of help to local conservation organizations
and the Wildlife Department in any proposals for the
protection of these areas.
Keywords Camera trapping, Catopuma, disturbed
forest, Malaysia, Neofelis, oil palm estate, Panthera,
Pardofelis, Prionailurus.
J. Mohd. Azlan (Corresponding author) Faculty of Resource Science and
Technology, University Sarawak Malaysia, 94300, Kota Samarahan,
Sarawak, Malaysia. E-mail amazlan@frst.unimas.my
Dionysius S.K. Sharma WWF Malaysia, 49, Jalan SS23/15, Taman SEA,
47400 Petaling Jaya, Selangor, Malaysia.
Received 21 April 2004. Revision requested 9 September 2004.
Accepted 7 March 2005.
Abstact A study to describe the diversity of wild felids
was carried out in Jerangau Forest Reserve, Ulu Tereng-
ganu, Malaysia, using camera traps, over a period of 21
months. A total of 24 camera traps were used, with a total
of 5,972 trap days. Six species of wild cats in five genera
were recorded: tiger Panthera tigris, leopard Panthera
pardus, clouded leopard Neofelis nebulosa, leopard cat
Prionailurus bengalensis, golden cat Catopuma temminckii
and marbled cat Pardofelis marmorata. This represents all
but two of the felid species known to occur in Peninsular
Malaysia. The use of camera traps provided detailed
information on the occurrence and activity patterns of
Introduction
Peninsular Malaysia contains 72% of the wild cat diver-
sity of tropical Asia, with seven species in five genera:
tiger Panthera tigris, leopard Panthera pardus and clouded
leopard Neofelis nebulosa, the smaller leopard cat Prion-
ailurus bengalensis, flat-headed cat Prionailurus planiceps
and marbled cat Pardofelis marmorata, and the interme-
diate sized golden cat Catopuma temmincki (Medway,
1983; Lim, 1999, 2002). A further species, the fishing cat
Prionailurus viverrinus, is considered rare in Peninsular
Malaysia (Nowell & Jackson, 1996) and the only potential
recent record is from Taman Negara National Park
(Kawanishi & Sunquist, 2003). Although these seven
species occur throughout Peninsular Malaysia (Medway,
1983; Lim, 1999), their abundance and local diversity
has been little studied in this region due to their cryptic
behaviour and the shortage of resources and expertise
for research. Most research has concerned tigers
(Ellagupillay, 1984; Khan, 1987; Topani, 1990; Jasmi,
1998; Kawanishi, 2002).
These felid species, except for the fishing cat, are
listed under schedule one of the Protection of Wildlife
Act 1972, under which hunting and trade are prohibited.
However, under certain circumstances of conflict, indi-
vidual animals can be eradicated and the action reported
to the Department of Wildlife and National Parks under
section 55 of the Wildlife Act 1972. Tiger is categorized
as Endangered on the IUCN Red List (IUCN, 2004),
and clouded leopard, flat-headed, marbled, golden and
fishing cats as Vulnerable.
Approximately 45% of the total land area of Peninsular
Malaysia is covered by forest, including selectively
logged and otherwise secondary forest. However, only
1.6 million ha, c. 20% of the forested area, is designated
as protection forest. Currently, Peninsular Malaysia has
0.74 million ha of national parks and other wildlife con-
servation areas (Anon, 2000). With the rapid destruction
of natural habitats (Jackson, 1983) it is important to docu-
ment the presence, diversity and distribution of felids
in the various forest patches to facilitate monitoring
and conservation programmes and to focus management
efforts.
A camera trapping programme to determine the
relative abundance of tigers and potential prey species
in Peninsular Malaysia (Mohd. Azlan & Sharma, 2001)
provided extensive data on the occurrence of other
felid species. Using this data our aim is to discuss the
diversity, relative abundance and activity patterns of
felids and to provide baseline data to facilitate the
conservation of these species in secondary forest in
Peninsular Malaysia.
Study Area
The study was conducted in Jerangau Forest Reserve
(140,000 ha; 4°55.5’N, 103°5.7’E), which surrounds
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