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in Sri Lanka - Ministry of Environment

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Monaragala, Kokagala and Doluwakanda are examples <strong>of</strong> such isolated hills. Phalaenopsismysorensis is recorded <strong>in</strong> such hill sites.ThreatsOrchids have complex and critical relationships with some other species <strong>in</strong> their habitat, suchas mycorrhizal association <strong>in</strong> their roots and flower adaptations for the attraction <strong>of</strong> a specificpoll<strong>in</strong>ator. Thus, ma<strong>in</strong>ly habitat related threats affect orchid survival.Habitat destruction: Spread <strong>of</strong> lowland tea cultivation to natural forest habitats significantlyaffect many lowland orchid species <strong>in</strong> the South Western wet zone.In the montane and submontane areas, forests and grasslands are cleared for vegetablecultivation, this be<strong>in</strong>g the ma<strong>in</strong> agriculture-based threat. Forest fell<strong>in</strong>g for firewood is anotherma<strong>in</strong> issue for orchid survival. In the savannah forest <strong>of</strong> the Eastern Intermediate zone,encroachment for chena cultivation, illegal settlements and garbage dump<strong>in</strong>g are the ma<strong>in</strong>habitat related threats to native orchid survival.Direct exploitation: Many showy orchids are collected for their flowers Phaius wallichii (Starorchid), Dendrobium maccarthiae (Vesak orchid), Rhynchostylis retusa (Fox tail), and Vandatessellata are commonly collected by growers and flower enthusiasts. Habenaria cr<strong>in</strong>ifera(Naarilatha), Ipsea speciosa (Nagamaru ala), Anoectochilus spp. (Wanaraja), Zeux<strong>in</strong>e spp.(Iruraja), are subjected to removal from the wild for medic<strong>in</strong>al purposes and due variousmythological beliefs connected to each species.Impact <strong>of</strong> <strong>in</strong>vasive species: The spread <strong>of</strong> <strong>in</strong>vasive species has created a considerable impactfor many orchid-rich habitats. Impact <strong>of</strong> Clusia rosea has been demonstrated as a highlyeffective <strong>in</strong>vader threaten<strong>in</strong>g lower montane orchid habitats. Presently, around G<strong>in</strong>igathhena,Hantana and Dolosbage and part <strong>of</strong> Peak Wilderness can be considered as a high impactareas. Similarly, <strong>in</strong> Rakwana hills, Psidium cattleianum spread<strong>in</strong>g as monostands showssimilar habitat alternation. Invasion <strong>of</strong> Panicum maximum is one <strong>of</strong> the ma<strong>in</strong> threats fac<strong>in</strong>g thegrassland and savannah orchids.Pollution: Most species <strong>of</strong> the family are highly sensitive to environmental changes. Theexcessive use <strong>of</strong> agro chemicals is believed to have a considerable impact on the survival <strong>of</strong>the orchid populations. Ma<strong>in</strong>ly fungicides destroy the mycorrhizal fungi, and use <strong>of</strong> <strong>in</strong>secticide<strong>in</strong>creases harmful impact on orchid poll<strong>in</strong>ators.The present National Red List summarizes how orchids are affected by all <strong>of</strong> the abovecomb<strong>in</strong>ation <strong>of</strong> threats mentioned. Four species likely to be ext<strong>in</strong>ct (CR (PE)) have not beenrecorded for a considerable time but their possible habitats still rema<strong>in</strong> to some extent. 16species are critically endangered for future ext<strong>in</strong>ction (CR), 54 species are categorized asendangered (EN) <strong>in</strong> the wild, and 60 spp. fall <strong>in</strong> the vulnerable category (VU). Most importantly,12 species could not be assessed due to uncerta<strong>in</strong>ty <strong>of</strong> present taxonomic positions or lack <strong>of</strong>knowledge about their other ecological parameters (DD).202

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