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The tropical moist deciduous forests represented by this ecoregion once stretched along the lower reaches of the Ganges and Brahmaputra river plains across the Indian states of Bihar, West Bengal, Assam, Uttar Pradesh, and Orissa, and most of Bangladesh. The southwest monsoon that sweeps in from the Bay of Bengal deluges the ecoregion with more than 3,500 mm of rainfall during the four months from June to September. Devastating cyclones sweep in from the Bay of Bengal, causing widespread flooding. The alluvial substrate deposited by the rivers is clayey and drains poorly, but on the more stable but flood-prone riverine flats the soil tends to be more sandy, with only local clay patches. The vegetation is semi-deciduous; the upper canopy contains the deciduous species, and the second story is dominated by evergreen species (Puri et al. 1989). Open forests are dominated by Bombax ceiba in association with Albizzia procera, Duabanga sonneratioides, and Sterculia vilosa. These are early seral communities that will eventually become sal (Shorea robusta) forest if succession is allowed to proceed. But in most places the forests fail to reach a climax stage for various reasons-many human-caused-perpetuating the sub-climax community (Champion and Seth 1968). The riparian forests are characterized by an Acacia-Dalbergia association that includes Acacia catechu, Albizzia procera, Bombax ceiba, Sterculia villosa, and Dalbergia sisso. In the upper Assam areas of the ecoregion, the forests are made up of Duabanga-Pterospermum-Terminalia in association with Bombax ceiba, Pterspermum acerifolium, Laportea crenulata, Duabanga sonneratioides, Terminalia myriocarpa, and Calamus tenuis (Puri et al. 1989). In permanently wet or moist areas with fine, clayey soils and a rich humus layer, impenetrable canebrakes grow profusely in the understory. Annual fires are common, so fire-hardy species such as Zizyphus mauritiana, Madhuca latifolia, Aegle marmelos, Butea monosperma, Terminalia tomentosa, Ochna pumila, and several others also occur in these fire-prone areas (Puri et al. 1989).
The ecoregion does not exhibit high levels of endemism but does harbor several threatened species. The mammal fauna consists of 126 known species, including one near-endemic species, a bat, Tadarida teniotis (table 1). The mammal assemblage also includes several threatened species such as the tiger, Asian elephant, gaur, sloth bear (Melursus ursinus), smooth-coated otter (Lutrogale perspicillata), great Indian civet (Viverra zibetha), and four-horned antelope or chousingha (Tetracerus quadricornis). The ecoregion's large habitat blocks are an important contribution to conservation of the large, wide-ranging mammals on northeastern India and overlaps with three Level I TCUs (Dinerstein et al. 1997). The elephant population in Midnapur district is considered to be of high conservation importance (WII 1999). Table 1. Endemic and Near-Endemic Mammal Species.
There are more than 380 known bird species, although none are endemic. However, the ecoregion harbors two globally threatened species, the Bengal florican and the lesser florican (Eupodotis indica), as well as the threatened Pallas's fish-eagle (Haliaeetus leucoryphus) and swamp francolin (Francolinus gularis). The Indian grey hornbill (Ocyceros birostris) and Oriental pied-hornbill (Anthracoceros albirostris) are indicators of intact forests and deserve conservation attention.  Current Status
Despite hundreds of years of human settlement, much forest still remained until the early twentieth century. Since then deforestation has accelerated, and now the ecoregion's natural habitat borders on the verge of extinction. Only about 3 percent of the ecoregion is now under natural forest, and only one large block of intact habitat (south of Varanasi) remains in this ecoregion. Although more than forty protected areas are represented in the ecoregion, they cover only about 3 percent of the ecoregion, and more than half of these protected areas are small, being less than 100 km2 in area (table 2). Table 2. WCMC (1997) Protected Areas That Overlap with the Ecoregion.
The dense human population is still growing rapidly. The urbanization, industrialization, and agriculture associated with this growing population and its resource and economic needs pose serious threats to the remaining forest fragments. The small, protected areas are vulnerable to this tidal wave of human growth and are inadequate to conserve the ecoregion's biodiversity. Finding additional habitat for protection will be challenging. Therefore, the existing protected areas should be effectively managed and protected, and restoring critical habitat should be considered where necessary.
In previous analyses of conservation units in the region, Rodgers and Panwar (1988) and then MacKinnon (1997) placed these forests in one conservation unit but also included the freshwater swamp forests and mangroves with the moist deciduous forests. In keeping with our rules for defining ecoregions, we separated the freshwater swamp forests and mangroves into their own ecoregions and defined the moist forests as the Lower Gangetic Plains Moist Deciduous Forests [IM0120]. We used MacKinnon's (1997) map of original vegetation as a guide to delineate the spatial extents of the vegetation types. This ecoregion roughly corresponds to Udvardy's Bengalian rain forest biogeographic province but extends further westward into the Indus-Ganges monsoon forest biogeographic province and further east into the Burma monsoon forest biogeographic province.
References for this ecoregion are currently consolidated in one document for the entire Indo-Pacific realm. Reviewed by: This text was originally published in the book Terrestrial ecoregions of the Indo-Pacific: a conservation assessment from Island Press. This assessment offers an in-depth analysis of the biodiversity and conservation status of the Indo-Pacific's ecoregions. For more general information on this ecoregion, go to the WildWorld version of this description. All text by World Wildlife Fund © 2001 | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
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