Location and General Description
This ecoregion represents the band of temperate broadleaf forest between 2,000 and 3,000 m, stretching from the deep Kali Gandaki River gorge in central Nepal, eastward through Bhutan, into India's eastern states of Arunachal Pradesh and Nagaland. Champion and Seth (1968) identified a number of broadleaf forest types across the midelevations (1,500-3,000 m) of the Himalayas: the east Himalayan moist mixed deciduous forests, east Himalayan wet temperate forests, Naga Hills wet temperate forests, Alder forests, east Himalayan oak-rhododendron forests, and Himalayan temperate parkland.
The Himalayas themselves trace their origin to the collision between the Eurasian continent and the northward-drifting Deccan Plateau more than 50 million years ago. The northern edge of the Deccan Plateau pushed beneath the Eurasian continent to raise the latter from beneath the Tethys Sea to create what is now the Tibetan Plateau. During this and three subsequent periods of geologic upheaval and uplift, the Himalayas were thrust upward to form the highest mountain range in the world (Wadia 1966).
The Himalayan Mountain Range comprises three east-west-directed parallel zones. The southernmost outer Himalayas, or Siwaliks, lie alongside the Indo-Gangetic Plain and is composed of alluvial deposits that have washed down from the north. It is more recent in origin than the other ranges. The next is the Middle Himalayas, a highly folded system of ridges and valleys that rise to about 5,000 m. The third is the Inner Himalayas, which contain the tallest mountains in the world: Everest, Makalu, Dhaulagiri, and Jomalhari.
The monsoon rains provide about 2,000 mm of precipitation from May to September. Because these monsoons are funneled in from the Bay of Bengal, the eastern Himalayas receive the greatest rainfall, with a progressively drier trend toward the west. Thus, precipitation, topography, and temperature combine to influence the vegetation across this ecoregion.
Two distinct ecological formations of broadleaf forests can be distinguished in this ecoregion depending on the geology and slope (moisture regime): the temperate evergreen forests of oaks (Quercus spp.), especially Quercus lamellosa in association with Lithocarpus pachyphylla, Rhododendron arboreum, Rhododendron falconeri, Rhododendron thomsonii, Michelia excelsa, Michelia cathcartii, Bucklandia populnea, Symplocos cochinchinensis, and other species of Magnolia, Cinnamomum, and Machilus; and temperate deciduous forests dominated by Acer campbellii, Juglans regia, Alnus nepalensis, Betula alnoides, Betula utilis, and Echinocarpus dasycarpus (Rao 1994; Puri et al. 1989; Shrestha and Joshi 1997).
In the wetter parts of eastern Nepal, the forests are composed of a Magnolia-Acer-Osmanthus association, characterized by Magnolia campbellii, Acer campbellii, Osmanthus suavis, Schefflera impressa, and Corylus ferox (Chaudhary 1998). Common herbs the include Luculia gratissima, Lilium wallichianum, Pipanthus nepalensis, and Aster himalaicus, which form a ground cover. Shrestha and Joshi (1997) have reported that an understory of bamboo (Arundinaria spp. and Bambusa spp.) or species of Symplocos, Eurya, Rhododendron, Acer, Alnus, Carpinus, and Prunus can also be present in some areas in these elevations in eastern Nepal. In mature forests, the trees are draped with mosses, ferns, and other epiphytes.
The Eastern Himalayan Broadleaf Forests [IM0401] is globally outstanding for both species richness and endemism, especially for its flora. It contains several localized areas of floral richness and endemism-floral hotspots-which are especially rich in rhododendrons and oaks.
The 125 mammal species known to occur in here include four species that are endemic to the ecoregion (table 1).
Table 1. Endemic and Near-Endemic Mammal Species.
Cercopithecidae Semnopithecus geei
Sciuridae Petaurista magnificus
Sciuridae Biswamoyopterus biswasi*
Muridae Niviventer brahma
An asterisk signifies that the species' range is limited to this ecoregion.
Three of these species are shared with adjacent ecoregions, but the Namdapha flying squirrel, Biswamoyopterus biswasi, is a strict endemic whose range distribution is limited to the Eastern Himalayan Broadleaf Forests [IM0401] (from Corbet and Hill 1992). The golden langur is limited to the broadleaf forests to the north of the Brahmaputra River, which flows along the foothills and between the Sankosh and Manas rivers, which flow south from the mountains. Therefore, despite being shared between this ecoregion and the adjacent Himalayan Subtropical Broadleaf Forests [IM0115], the golden langur has a very limited range distribution.
The ecoregion also harbors several threatened species, including the endangered tiger (Panthera tigris), red panda (Ailurus fulgens), takin (Budorcas taxicolor), and serow (Capricornis sumatraensis) and the vulnerable Vespertilionidae bat (Myotis sicarius), Assamese macaque (Macaca assamensis), stump-tailed macaque (Macaca arctoides), wild dog (Cuon alpinus), back-striped weasel (Mustela strigidorsa), clouded leopard (Pardofelis nebulosa), and Irrawaddy squirrel (Callosciurus pygerythrus) (IUCN 2000).
The ecoregion overlaps with a high priority (Level I) TCU (Dinerstein et al. 1997), a landscape with the ecological resources to support a viable tiger population over the long term. It also represents the only opportunity to conserve a tiger population that is adapted to survive in these Himalayan temperate broadleaf forests, where, unlike the productive habitats in the Terai and Duar grasslands and tropical dry forests, the tiger's prey densities are much lower. Under these conditions, the tigers are considered to have adapted their territory size, reproductive strategies, and hunting strategies to these ecological conditions (Wikramanayake et al. 1998).
The red panda is more characteristic of the sub-alpine fir forest ecoregion adjacent to and above this temperate broadleaf forest ecoregion. In this broadleaf forest ecoregion, the red panda is limited to patches of mature fir (Abies) forests with a bamboo understory (Yonzon and Hunter 1991).
There are almost 500 bird species, among the highest across the ecoregions in this bioregion. Twelve species are endemic to the ecoregion (table 2). Of these, eleven are near-endemic species, and one, the rufous-throated wren-babbler, is a strict endemic that is restricted to the Eastern Himalayan Broadleaf Forests [IM0401].
Table 2. Endemic and Near-Endemic Bird Species.
Family Common Name Species
Phasianidae Chestnut-breasted partridge Arborophila mandellii
Timaliidae Hoary-throated barwing Actinodura nipalensis
Timaliidae Ludlow's fulvetta Alcippe ludlowi
Turdidae Rusty-bellied shortwing Brachypteryx hyperythra
Timaliidae Elliot's laughingthrush Garrulax elliotii
Paradoxornithidae Grey-headed parrotbill Paradoxornis gularis
Timaliidae Immaculate wren-babbler Pnoepyga immaculata
Sylviidae Grey-crowned prinia Prinia cinereocapilla
Timaliidae Mishmi wren-babbler Spelaeornis badeigularis
Timaliidae Rufous-throated wren-babbler Spelaeornis caudatus*
Timaliidae Snowy-throated babbler Stachyris oglei
Timaliidae Spiny babbler Turdoides nipalensis
An asterisk signifies that the species' range is limited to this ecoregion.
The bird assemblage also includes several threatened species of pheasants, tragopans, and hornbills that need mature forests and have low tolerances for disturbance. These species, namely the globally threatened rufous-necked hornbill (Aceros nipalensis) and Sclater's monal (Lophophorus sclateri), and the threatened white-bellied heron (Ardea insignis), Blyth's tragopan (Tragopan blythii) and Ward's trogon (Harpactes wardi) (IUCN 2000), therefore can be considered indicators of habitat integrity and deserve conservation attention. The ecoregion also overlaps with BirdLife International's EBA, Eastern Himalayas (130) (Stattersfield et al. 1998).
About two-thirds of this ecoregion's natural habitat is still intact, with most of the remaining large habitat blocks located in northeastern India and Bhutan. Even though the species-rich Quercus lamellosa forests are quite well represented within protected areas, the Quercus lanata forests in the lower elevations are not. Many of the small areas that remain are so badly degraded that restoration should be considered as a conservation option. Mt. Phulchowki, in the Kathmandu valley, represents an important area of habitat that is currently unprotected and highly threatened (Wikramanayake et al. 1998).
The fifteen protected areas that extend into the ecoregion cover about 5,800 km2 (7 percent) of the ecoregion (table 3). With the exception of Namdapha, none exceed 1,000 km2. However, there are several very large reserves that overlap across several ecoregions, although only parts of the reserves are represented in this one. Examples include Thrumsing La, Jigme Dorji, and Black Mountains national parks in Bhutan. The Jigme Dorji National Park exceeds 4,000 km2 and sprawls across three ecoregions to include the alpine meadows, sub-alpine conifer forests, and temperate broadleaf forests represented by this ecoregion. Two others, Kulong Chu and Black Mountains, exceed 1,000 km2, and Cha Yu, Makalu-Barun, Mehao, and Thrumsing La are more than 500 km2.
Table 3. WCMC (1997) Protected Areas That Overlap with the Ecoregion.
Protected Area Area (km2) IUCN Category
Eagle Nest [IM0301] 120 IV
Mouling [IM0301] 200 II
Mehao [IM0301], [IM0105] 110 IV
Royal Manas [IM0115] 410 II
Shivapuri Waters & Wildlife Reserve 90 IV
Makalu-Barun Conservation Area [IM0501], [PA1003] 70 II
Neora Valley 40 II
Torsa [IM0501], 39)] 240 I
Jigme Dorji [IM0501], [PA1003] 560 II
Thrumsing La [PA1003] 310 II
Kulung Chhu WS [IM0501] 390 IV
Black Mountain [IM0501], [PA1003] 600 II
Namdapha 1,580 PRO
Kamlang 780 IV
Cha Yu [IM0501] 320
Ecoregion numbers of protected areas that overlap with additional ecoregions are listed in brackets.
Bhutan recently revised its protected area system to link the existing reserves (Sherpa and Norbu 1999). Plans to develop similar linkages through conservation landscapes have been proposed in the other areas in the eastern Himalayas (WWF and ICIMOD 2001). These plans use ecoregions as basic conservation units for representation of biodiversity.
Types and Severity of Threats
The primary threat to this ecoregion's natural biodiversity is forest clearing for agriculture, plantations, and settlements. The upper elevation limit of cultivation in the eastern Himalayas is about 2,100 m, but the land above the agricultural areas is used for livestock grazing, especially during the summer, and exploited for wood and foliage. Pastoralists often clear and burn these forests to create grazing lands for livestock. Even in the well-represented Quercus lamellosa-dominated forests, the lower areas have been extensively cleared.
Because Bhutan is less densely populated than Nepal, habitat loss and degradation are not severe. Therefore, most of the large, intact habitat blocks are in Bhutan.
Chakma and Tibetan refugees and lamas from Bhutan have settled the area surrounding Namdapha National Park in northern India. These settlers have begun to clear forests for shifting cultivation, cut trees for timber and fuelwood, and illegally extract agar, dhoop, and other forest products (Davis et al. 1995).
A proposal to build a dam across the Noa-Dihing River at Burma Nala will result in inundation of land and increased human settlements, presenting serious threats to the natural biodiversity in this area of the ecoregion (Davis et al. 1995).
Priority Conservation Actions
Conservation actions in this ecoregion should be planned and implemented within the context of the larger Himalayan ecosystem. The long-term biological vision developed for the eastern Himalayas (WWF and ICIMOD 2001) should be the foundation for these conservation actions. The ecoregion's biodiversity and conservation needs will be represented in this plan. Some of the important conservation actions that should be addressed include the following.
Short-Term Conservation Actions (1-5 Years)
o Impose strict controls on illegal hunting of threatened species.
o Reforest and restore critical habitats, especially in the broadleaf forests in the lower elevations of this ecoregion.
o Stop livestock grazing within protected areas and regulate activities in buffer zones.
o Stop deforestation and agricultural expansion on steeper slopes. This is especially relevant in Nepal, where higher and steeper slopes are being cleared.
o Conduct biological inventories of many of the protected areas and conservation landscapes. These inventories should be designed with a conservation management focus and not with the intent of merely compiling species lists.
Longer-Term Conservation Actions (5-20 Years)
o Develop a long-term ecoregion-based conservation plan for the eastern Himalayas (WWF and ICIMOD 2001). Implement the priority actions identified in this plan.
Focal Species for Conservation Action
Habitat specialists: rufous-necked hornbill
Endangered endemic species: rufous-throated wren babbler, Myotis sicarius
Area-sensitive species: tiger, altitudinal migrant birds
Top predator species: tiger, leopard
Other: red panda, takin, southern serow, great Indian civet, stump-tailed macaque, wild dog, back-striped weasel, clouded leopard, Irrawaddy squirrel, Sclater's monal, white-bellied heron, Blyth's tragopan, Ward's trogon
Selected Conservation Contacts
Department of Forestry, Royal Government of Bhutan
Department of Wildlife Conservation, Government of Nepal
Forest Department, Government of Sikkim, India
Forest Departments of Uttar Pradesh, West Bengal, Assam, and Arunachal Pradesh, India
King Mahendra Trust for Nature Conservation, Nepal
Resources Himalaya, Kathmandu, Nepal
Royal Society for Nature Conservation, Bhutan
Justification of Ecoregion Delineation
MacKinnon (1997) identified four biounits along the Himalayas. Because these were based on longitudinal boundaries, each included the range of habitat types represented along the north-south axis of the Himalayas, from the lowlands to the alpine habitats. Because we define an ecoregion as an ecosystem of regional extent, in our analysis we sought to represent these distinct ecosystems in separate ecoregions.
We used the deep Kali Gandaki River gorge, an acknowledged biogeographic barrier, as a boundary to separate the band of temperate forests that run along the east-west-directed length of the Himalayas into eastern and western broadleaf forest ecoregions. We then used MacKinnon's (1997) digital map of the distribution of original vegetation to separate the temperate forests from the broadleaf subtropical forests to the south and the sub-alpine conifer forests to the north. Therefore, the temperate broadleaf forests to the east of the Kali Gandaki River are represented within the Eastern Himalayan Broadleaf Forests [IM0401]. All the Himalayan ecoregions are part of Udvardy's Himalayan highlands biogeographic province.
Prepared by: Gopal S. Rawat and Eric D. Wikramanayake, with contributions by Pralad Yonzon