William George J (2001) Preliminary survey of wildlife at Sungai Asam,
Samunsam Wildlife Sanctuary, Malaysia, Hornbill
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PRELIMINARY SURVEY OF WILDLIFE AT SUNGAI ASAM,
SAMUNSAM WILDLIFE SANCTUARY, MALAYSIA
WILLIAM GEORGE JEBRON1
SUMMARY
A wildlife survey was conducted at Sungai Asam in the
new extension to Samunsam Wildlife Sanctuary. The objectives of the
survey were to collect new data on wildlife presence and abundance for
comparison with the existing Samunsam Wildlife Sanctuary and also to
provide baseline reference materials on wildlife, particularly primates,
in the extension area.
By using line transects surveys, data on mammals
(arboreal and terrestrial) and birds were collected from two study
sites. Night surveys were conducted as well to look for nocturnal
animals. Thirteen species of mammals and twenty-six species of birds
were recorded.
My study shows that most of the species of mammals
and birds of Samunsam Wildlife Sanctuary are found in the extension, but
only in small numbers. Hunting is still a big problem in the area as
access is still easy for poachers to penetrate the sanctuary
INTRODUCTION
With effect from 29 May 2000, Gunung Pueh Forest
Reserve, with an area of 16,706 ha, was constituted as an extension to
Samunsam Wildlife Sanctuary. Rajanathan (1992) had studied diurnal
primates in the original Sanctuary in 1991-92, investigating the way in
which different species used the different forest types and correlating
this with flowering and fruiting patterns; the results of his transect
surveys are shown in Table 2.
However, no surveys had been done in the new
extension. This study aimed to collect new data on wildlife presence and
abundance for comparison with the existing Samunsam Wildlife Sanctuary.
It would also provide baseline reference material on wildlife in the
extension area. The survey concentrated primarily on primates, but other
species of mammals and birds were also recorded when seen.
METHODS
Study site
The Sungai Asam area lies within the new extension, and has been
extensively logged for many years. Access has been easy for poachers and
hunters, as well as other forms of encroachment.
Two 2000m transects about 600m apart were used, both
running approximately south from the Sungai Asam Camp. They cross
kerangas forest growing on unconsolidated sand dunes, lowland
dipterocarp and some emperan and riverine forest.
Morning surveys
The survey began at 7.00 a.m. Pairs of observers walked each
transect, equipped with binoculars and data sheets. They walked slowly
and quietly and stopped at each 25m mark for one minute to look and
listen. It took about four hours to survey each transect of 2,000 metres.
Night surveys
Only 1,000 metres of each transect was used for night surveys. Pairs
of observers went to the 1,000m mark well before dusk, waited until it
was dark at about 7.30 p.m., then walked slowly back, stopping for one
minute at each 25m mark. Torch lights were used to detect animals, often
picked up by their eye-shine.
Data Analysis
Index Counts were calculated for the main species observed. The
Index Count is the average number of animals seen per kilometre (Rabinowitz
1997). It is calculated from -
Index Count = Total number of animals (groups or individuals) seen
Total distance (km) of transect walked
Similar indices can be calculated for the number of
animals heard or for the number of signs seen. The population density
was not calculated as insufficient data were collected in the short
period of the survey for proper analysis.
RESULTS
The Survey
The two line transects were walked by day for six
consecutive days, making the total distance 24 km. Night surveys were
carried out on four nights for a total of 8 km.
Mammals and birds
The list of species recorded in the Sungai Assam area
is shown in Table 1, which includes those species seen or heard outside
the formal transect surveys. Table 1 also shows the number of animals
seen during the line transect surveys and the Index Counts (ie the
number of individual animals divided by 24km). For primates, the number
of groups seen and the Index Counts for groups are shown in Table
2.
A group of three black hornbills was seen on one
occasion, and Malay lorikeets were seen in two small groups and one
large group of twelve or more.
Very few animals were seen during the night surveys,
apart from unidentified bats. The Malay civet, which is normally a
nocturnal animal, was seen during the morning survey. Calls of brown
hawk-owl were heard during night surveys on four occasions.
Humans
Both transects cross old logging roads which still in
good condition and being used by intruders in vehicles. There were fresh
human foot prints and motorcycle tracks on the logging roads, and signs
of recent cooking and barbecuing at an old hut by a log depot.
We heard gunshots fired inside the sanctuary three
times during night surveys. The sound of the engines of the logging
trucks from a distance away was also heard on a few occasions at night.
During our transect walk in the morning, the distant sound of chainsaws
could be heard.
DISCUSSION
The Index Counts for groups of primates for the
present study and Rajanathan’s (1992) study are presented in Table
2.
Table 2 : Number of groups and Index Counts for
primates seen in Samunsam WS
|
Site |
Distance
Surveyed (km) |
Banded
langur |
Pig-tailed
macaque |
Gibbon |
Long-tailed
Macaque |
|
Rajanathan (1992) |
|
MDF |
107.70 |
23 |
0.214 |
6 |
0.055 |
17 |
0.158 |
0 |
0 |
|
RF |
99.60 |
19 |
0.191 |
1 |
0.01 |
18 |
0.181 |
12 |
0.120 |
|
MDSF |
78.10 |
19 |
0.243 |
0 |
0 |
14 |
0.179 |
14 |
0.179 |
|
THF |
135.00 |
1 |
0.007 |
1 |
0.007 |
1 |
0.007 |
0 |
0 |
|
Present study |
|
Sungai Assam |
24.00 |
1 |
0.04 |
0 |
0 |
2 |
0.08 |
1 |
0.04 |
|
MDF = Mixed Dipterocarp Forest; RF = Riverine
Forest; MDSF = Mixed Dipterocarp Secondary Forest; THF =
Tropical Heath Forest (or Kerangas) |
Comparing the data from this small survey, with only
24 km of transect walked over a short period, with Rajanathan’s (1992)
data should be done with caution. In particular, we did not lay out
transects in specific forest types, though they did include some
kerangas forest, where Rajanathan found very low densities of primates.
Most of the species expected in the area are present
but in a small numbers. Some may have been habituated to the disturbance
and the presence of humans in the area.
Animals change their behaviour in response to human
disturbance, in some cases becoming more nocturnal, which would affect
the results of a quantitative wildlife survey done in daytime. It was
surprising to record a Malay civet – normally a nocturnal animal –
during the morning survey. However, this is not the case for the
primates shown in table 2, which are strictly diurnal.
CONCLUSION
Hunting is still a big problem in this area and
access for hunters to the interior of the sanctuary is still easy.
My study shows that most of the species of mammals
and birds of Samunsam Wildlife Sanctuary were found in this area but
only in small numbers. Small populations can quickly disappear if action
is not taken immediately, but they can recover if all types of hunting
activities are stopped. Regular monitoring of wildlife species in the
area is essential because we know that small populations are vulnerable.
Legal protection must be backed up with enforcement and education.
To determine appropriate management strategies in
future, more research and wildlife surveys have to be carried out in the
area. The results will help identify population trends and the species
occurring in this area.
Table 1. List of species recorded in Sungai Assam
area, with numbers seen during morning transect surveys and Index Counts
where appropriate
Mammals
|
Family |
Species |
Common Name |
Number seen |
Index |
|
Hylobatidae |
Hylobates muelleri abbotti |
Borneo gibbon |
4 |
0.17 |
|
Cercopitecidae |
Presbytis melalophos |
Banded langur |
4 |
0.17 |
|
Cercopitecidae |
Macaca nemestrina |
Pig-tailed macaque |
|
|
|
Cercopitecidae |
Macaca fascicularis |
Long-tailed macaque |
3 |
0.12 |
|
Cercopitecidae |
Nasalis larvatus |
Proboscis monkey |
1 |
0.04 |
|
Viverridae |
Viverra tangalunga |
Malay civet |
2 |
0.08 |
|
Suidae |
Sus barbatus |
Bearded pig |
3 |
0.12 |
|
Tragulidae |
Tragulus napu |
Greater mouse deer |
|
|
|
Tupaiidae |
Callosciurus prevostii |
Provost’s squirrel |
1 |
0.04 |
|
Tupaiidae |
Callosciurus notatus |
Plantain squirrel |
2 |
0.08 |
|
Sciuridae |
Exilisciurus exilis |
Plain pigmy squirrel |
1 |
0.04 |
|
Sciuridae |
Ratufa affinis |
Giant squirrel |
1 |
0.04 |
|
Sciuridae |
Rheithrosciurus macrotis |
Tufted ground squirrel |
1 |
0.04 |
Birds
|
Family |
Species |
Common Name |
Number seen |
Index |
|
Alcedinidae |
Halcyon chloris |
White-collar kingfisher |
2 |
0.08 |
|
Apodidae |
Cypsisiurus sp. |
Swifts |
|
|
|
Bucerotidae |
Buceros rhinoceros |
Rhinoceros hornbill |
1 |
0.04 |
|
Bucerotidae |
Anthracoceros malayanus |
Black hornbill |
3 |
0.12 |
|
Phasianidae |
Argusianus argus |
Great Argus |
|
|
|
Phasianidae |
Rollulus rouloul |
Crested wood partridge |
1 |
0.04 |
|
Phasianidae |
Melanoperdix nigra |
Black wood partridge |
|
|
|
Nectariniidae |
Nectarina jagularis |
Yellow breasted sunbird |
|
|
|
Nectariniidae |
Anthreptes simplex |
Plain-throated sunbird |
|
|
|
Nectariniidae |
Arachnothera longirostra |
Little spider hunter |
|
|
|
Corridae |
Copyschus saularis |
Magpie robin |
|
|
|
Capitonidae |
Megalaima rafflesii |
Red-crowned bardet |
|
|
|
Caprimulgidae |
Eurostopodus sp. |
Nightjar |
2 |
0.08 |
|
Chloropseidae |
Aegithinia tiphia |
Common Iora |
|
|
|
Chloropseidae |
Irena puella |
Asia fairy bluebird |
|
|
|
Columbidae |
Ducula aenea |
Green imperial pigeon |
6 |
0.25 |
|
Columbidae |
Treron curvirostra |
Thick –billed pigeon |
1 |
0.04 |
|
Cuculidae |
Centropus sinensis |
Great coucal |
1 |
0.04 |
|
Dicruridar |
Dicrurus paradiseus |
Racket-tailed drango |
|
|
|
Syliviidae |
Orthotomus sutorius |
Common tailorbird |
|
|
|
Strigformes |
Ninox scutulata |
Brown hawk owl |
|
|
|
Sturinidae |
Gracula religiosa |
Hill myna |
1 |
0.04 |
|
Psittacidae |
Loriculus galaulus |
Malay lorikeet |
16 |
0.67 |
|
Podargides |
Batrachostomus sp. |
Frogmouth |
1 |
0.04 |
|
Pycnonotidae |
Pycnonotus goiavier |
Yellow vented bulbul |
|
|
|
Pividae |
Picus puniceus |
Crimson-winged woodpecker |
1 |
0.04 |
REFERENCES
Rabinowitz, A.(1997). Wildlife Field Research and
Conservation Training Manual. Wildlife Conservation Society, New York.
Rajanathan, R. (1992). Surveys at Samunsam WS.
Sarawak Forest Department and WCS.
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