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Southeastern Asia: Malaysia and the Kepulauan Anambas Islands in Indonesia

The Peninsular Malaysian Rain Forests [IM0146] ecoregion, with 195 mammal species, has the second most mammal species in the Indo-Pacific, behind the Borneo Lowland Rain Forests [IM0102]. Yet most of the wide-ranging or top carnivore species lead a tenuous existence in these biologically outstanding forests. The tiger, Asian elephant, Sumatran rhinoceros, Malayan tapir, gaur, and clouded leopard all fall into this category. As in many other tropical forests in this region, habitat loss and poaching are the two primary reasons for the decline in these and other species.

  • Scientific Code
    (IM0146)
  • Ecoregion Category
    Indo-Malayan
  • Size
    48,500 square miles
  • Status
    Vulnerable
  • Habitats

Description
Location and General Description
This ecoregion is made up of the lowland moist forests of peninsular Malaysia and the extreme southern part of Thailand. There are no clear seasons in peninsular Malaysia, and rainfall is plentiful year-round. Two monsoons punctuate the region. From October to March a northeastern monsoon brings extra rain to the eastern side of peninsular Malaysia. The southwest monsoon, which is more powerful, bathe the western side of peninsular Malaysia with rain from April to August. Based on the Köppen climate zone system, this ecoregion falls in the tropical wet climate zone (National Geographic Society 1999).

These majestic forests are dominated by the Dipterocarpaceae tree family, notably Anisoptera spp., Dipterocarpus spp., Dryobalanops spp., Hopea spp., and Shorea spp. (IUCN 1991). These forests contain a high diversity of tree species (an estimated 6,000 species), and dominant species are uncommon. The general characteristics of these forests are canopies of 24-36 m, with emergents reaching more than 45 m. Dipterocarpaceae is a dominant family in the emergent stratum (Whitmore 1984). In the richest forests, up to 80 percent of the emergent trees are dipterocarps. Of the dipterocarps, Dipterocarpus, Dryobalanops, and Shorea are the emergents, and Hopea and Vatica usually are found in the main canopy. Berseraceae and Sapotaceae are other common main canopy families (MacKinnon et al. 1996). The tallest tree species in these forests is not a dipterocarp but rather a legume. The Koompassia excelsa (known as tualang) can grow as tall as 76 m (250 feet) (Richards 1952). This tree is rarely felled when land is cleared because of its large size, hard wood, and huge buttresses. They are often laden with the wild honey-producing bees (Apis dorsata) and are therefore worth more money standing than being logged. Riverine forests are bordered by neram trees (Dipterocarpus oblongifolius), figs (Ficus racemosa), and kelat (Eugenia grandis) and are draped with numerous epiphytic orchids and ferns (Payne and Cubitt 1990). Below the canopy a layer of shade-tolerant species thrives. This layer includes many species from the Euphorbiaceae, Rubiaceae, Annonaceae, Lauraceae, and Myristicaceae families. Ground vegetation usually is sparse, mainly small trees, and herbs are uncommon.

This ecoregion also includes some karst limestone areas that are floristically rich. The limestone hills harbor more than 1,200 species of vascular plants, of which at least 129 are endemic to this habitat (IUCN 1991), most limited to one or a few isolated hills.

Biodiversity Features
Peninsular Malaysia shares many of its tremendous species diversity with Sumatra and Borneo. All three landmasses were once part of a single, larger landmass during the last ice age, when the sea level was more than 100 m lower than it is today. However, peninsular Malaysia retained a connection to Asian mainland, and the lowland forests have the greatest diversity of mammal species found in the Indo-Pacific region. Unfortunately for many of the wide-ranging or carnivorous species, survival in peninsular Malaysia is in doubt.

The tiger (Felis tigris) is peninsular Malaysia's largest predator. They exact estimate of the number of remaining tigers in peninsular Malaysia is not known, but estimates have ranged from 300 to 650 over the past decade. What is not in doubt is that Malaysia's tiger population is in danger of drifting toward extinction. As recent as the 1950s more than 3,000 tigers were estimated to live in Malaysia. However, poaching, habitat loss, and inadequate protection have drastically reduced the population. Taman Negara Nature Reserve remains one of the last refuges for the tiger and several other endangered species (Rabinowitz 1999). There are one Level I and two Level II TCUs in peninsular Malaysia that overlap this ecoregion (Dinerstein et al. 1997).

The Malayan tapir (Tapirus indicus) is the largest of the four living tapir species and only Old World representative. The population of the Malayan tapir has been drastically reduced, but they survive in protected areas. Tapirs can be seen in the Ampang Forest Reserve, and the largest surviving population probably lives around Taman Negara National Park (McClung 1997; Payne and Cubitt 1990). Peninsular Malaysia is also home to the world's smallest rhinoceros, the two-horned Sumatran rhinoceros (Didermocerus sumatrensis). It once ranged through much of southeast Asia, but today the entire population numbers about 500 individuals scattered in isolated populations from peninsular Malaysia to Sumatra and Borneo (McClung 1997). Populations of the rhinoceros survive at Sungai Dusun, Ulu Selama, and Endau-Rompin parks in peninsular Malaysia (Payne and Cubitt 1990).

Peninsular Malaysia's largest land animal, the Asian elephant (Elephas maximus), is also one of the most endangered. They range over vast tracts of land throughout peninsular Malaysia in search of food, and as habitat is destroyed the population has become fragmented and poached. The estimated population has varied widely from 600 to 6,000 elephants, demonstrating the poor knowledge of the actual status of this species in peninsular Malaysia (Sukumar 1989). The second largest mammal in these forests is wild cattle, the gaur (Bos gaurus), or seladang as it is known in Malaysia. Widespread poaching and habitat loss have drastically reduced gaur populations outside protected areas (Payne and Cubitt 1990).

Numerous other mammal species live in these forests and include squirrels, deer, otter, civet, primates, the rare sun bear (Ursus malayanus), the clouded leopard (Pardofelis nebulosa), and many bat species.

Birds species richness is also high, with more than 450 species attributed to the ecoregion. These include several pheasants: the crestless fireback pheasant (Lophura erythrophthalma), crested fireback (Lophura ignita), Malay peacock pheasant (Polyplectron malacense), great argus pheasant (Argusianus argus), and crested argus pheasant (Rheinardia ocellata). Hornbills, barbets, bulbuls, woodpeckers, pigeons, broadbills, and babblers are other highly speciose or characteristic groups.

Current Status
Most of these lowland forests have been converted to rice fields, rubber and oil palm plantations, and orchards, with the northwestern region being the most intensively cultivated (Cubitt and Payne and Cubitt 1990). Only about a fifth of the original forest cover now remains, scattered in fragments throughout the ecoregion. There are numerous protected areas that cover 3,875 km2 (3 percent) of this ecoregion (table 1). With the exception of Taman Negara, all are less than 500 km2, many less than 10 km2. None of the alluvial swamp forest in the ecoregion is protected in peninsular Malaysia (WWF and IUCN 1995).

Table 1. WCMC (1997) Protected Areas That Overlap with the Ecoregion.

  Protected Area Area (km2) IUCN Category
Unnamed 210 ?
Unnamed 160 ?
Pulau Redang 20 PRO
Taman Negara [IM0144] 2,770 II
Tasek Bera 270 PRO
Pulau Tioman 130 VIII
Mersing 110 PRO
Endau-Kota Tinggi (East) 50 IV
Sungei Buloh 1 V
Senko (Sungei Sembawang) 1 REC
Sungei Khatib Bongsu Heronry 1 REC
Kranji Heronry and Marshes 2 REC
Bukit Timah and Central catchment NR 30 IV
Nee Soon 1 IV
Bukit Timah extension 1 IV
Pasir Ris 1 V
Botanic Gardens 1 UA
Fort Canning 1 UA
Kent Ridge 1 REC
Labrador 1 V
Sentosa 1 REC
Pulau Bulan 100 PRO
Pulau Pasir Panjang 2 PRO
Pulau Penyengat 10 PRO
Total 3,875  

Ecoregion numbers of protected areas that overlap with additional ecoregions are listed in brackets.

Types and Severity of Threats
Logging began in the 1950s, and by the 1970s, 3,660 km2 of forests were being logged annually (IUCN 1991). But as the forest has been depleted of valuable timber trees, these rates have slowed. Logging is selective and therefore not a direct cause of forest loss but is often a preliminary to other forms of land use. The major cause of forest conversion in peninsular Malaysia is large-scale clearing for plantations and agriculture, especially of rubber, coconut, and oil palm for export production (IUCN 1991). Coffee and cocoa are minor crops. The threat of extensive plantations of pine trees for paper production (MacKinnon and MacKinnon 1986) has not materialized, but other quick-growing softwoods such as Acacia mangium are being favored. Hydropower and irrigation projects are a second major cause of forest loss, with mining and its associated road building and quarrying around limestone areas such as Perak and Selangor being the third (IUCN 1991). The losses in terms of forest area are slight but tend to have high impact at specific sites. In comparison to these high-impact activities, the forest conversion and degradation from shifting cultivation by indigenous people is slight (IUCN 1991). Some of the last remnants of coastal dipterocarp forest in the state of Perak, peninsular Malaysia, are at high risk from the expansion of nearby urban areas (WWF and IUCN 1995). Because more than 80 percent of the mammal species of peninsular Malaysia live only in the lowland forests of this ecoregion and 53 percent are confined to primary forest, the degradation in this ecoregion severely reduces species diversity and long-term population viability in peninsular Malaysia as a whole (IUCN 1991).

Justification of Ecoregion Delineation
The Peninsular Malaysian Rain Forests [IM0146] ecoregion represents the large extent of the lowland broadleaf rain forests extending south of the Kangar-Pattani line to Singapore.

This ecoregion approximates the spatial extent of MacKinnon's (1997) subunit 07a, but we also included the Lingga and Riau archipelagos. Although FAO (1974) indicates that these islands contain heath forests, both Whitmore (1984) and MacKinnon (1997) dispute this classification, and MacKinnon identified the vegetation as lowland moist forest. The tropical montane evergreen moist forests above 1,000 m were placed in the Peninsular Malaysian Montane Rain Forests [IM0144]. We also extracted the large areas of peat swamp forests along the coast of peninsular Malaysia into the Peninsular Malaysian Peat Swamp Forests [IM0145]. Thus, we created three ecoregions within MacKinnon's Malay Peninsular subunit (07a) and Udvardy's Malayan rain forests biogeographic province.

References
References for this ecoregion are currently consolidated in one document for the entire Indo-Pacific realm.
Indo-Pacific Reference List

Prepared by: Colby Loucks
Reviewed by:

 

The Global 200

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