The Wet Z<strong>on</strong>e rainforests harbour nearly all the country's woody endemic flora, about 75 per cent of the endemicfauna, and all the endemic genera (MOFE, 1999). They also provide refuge for the relict G<strong>on</strong>dwana-Deccan biota(Asht<strong>on</strong> and Gunatilleke, 1987). The level of endemism in Wet Z<strong>on</strong>e forests ranges from 37 - 64 % for woody plants and14 - 52 % for animals, compared with 10-16% for species in the Dry Z<strong>on</strong>e forests (MOFE, 1999).The NCR also revealed that 79 per cent of the woody plant diversity (including 88 per cent of endemic woody plantspecies) and 83 per cent of faunal diversity (including 85 per cent of endemic faunal species) are represented in justeight units of c<strong>on</strong>tiguous forests (IUCN/FAO/FD 1997). Six of these complexes are in the Wet Z<strong>on</strong>e, while theIntermediate and Dry Z<strong>on</strong>es c<strong>on</strong>tain <strong>on</strong>e complex each (MoFE, 1999). The fact that the biologically diverse lowland rainforests amount to less than 2% of the island’s total land area, with wet sub-m<strong>on</strong>tane and m<strong>on</strong>tane forests adding <strong>on</strong>ly afurther 1.01 % and 0.05% respectively (Forest Department data for 1999). This issue is compounded by the fact thatalthough 9,462 sq km of natural forest and scrubland, amounting to about 14% of the island are declared as Protected Areas(Nati<strong>on</strong>al Envir<strong>on</strong>mental Outlook, 2006), and <strong>on</strong>ly about 18% of this system falls within the Wet Z<strong>on</strong>e (MoENR, 2002).As a result of c<strong>on</strong>siderable anthropogenic factors, of which the main cause is deforestati<strong>on</strong> <strong>on</strong> a massive scale forestablishment of plantati<strong>on</strong> agriculture under col<strong>on</strong>ial rule, Sri Lanka’s rainforest biome is now represented mainly byisolated and very fragmented forest patches scattered over the Wet Z<strong>on</strong>e. Most individual forests amount to less than10,000 ha (IUCN/WCMC/FAO 1997), and many are suspected to be too small to sustain functi<strong>on</strong>al ecosystems in thel<strong>on</strong>g-term, or provide viable habitats for the mammalian macro-fauna of the Wet Z<strong>on</strong>e. C<strong>on</strong>sequently, forests thatc<strong>on</strong>tinue to harbour most of the endemic species are severely fragmented forest patches that are surrounded by a highhuman populati<strong>on</strong> density.Sri Lanka’s dipterocarp-dominated lowland forests are characterised bya dense canopy of trees reaching 30-40 m in height, with emergentsrising through the canopy to about 45 m. Due to the height of thecanopy trees and the straightness of their boles, these forests werec<strong>on</strong>sidered to be a viable source of timber around the 1940s, and thistrend c<strong>on</strong>tinued until 1989, resulting in their selective logging.Source: MoFE, 1999Due to intense public c<strong>on</strong>cern with regard to the loggingof the Sinharaja Forest Reserve, an AcceleratedC<strong>on</strong>servati<strong>on</strong> Review (ACR) of 31 Wet Z<strong>on</strong>e forests wascarried out in the 1990s by the Forest Department. Thefindings of this survey resulted in a moratorium <strong>on</strong>logging in all natural forests of Sri Lanka from 1990.Illegal timber felling has also been reduced, particularlyin Wet Z<strong>on</strong>e forests, as permits are now required fortransportati<strong>on</strong> of most species of timber value. However, illegal timber felling in forests is still a problem in someforests of the Dry Z<strong>on</strong>e, and more marginally in the Wet Z<strong>on</strong>e forests. The latter is mainly for pers<strong>on</strong>al use for housingc<strong>on</strong>structi<strong>on</strong>. Surveys such as the ACR, the NCR, and the recent Baseline Biodiversity Surveys in seven Protected Areasunder the Department of Wildlife C<strong>on</strong>servati<strong>on</strong>, have shown that the remaining rainforests have a rich biota, althoughfurther forest loss may well lead to species extincti<strong>on</strong>s <strong>on</strong> a massive scale. Already 33 Wet Z<strong>on</strong>e forests have beenidentified for strict c<strong>on</strong>servati<strong>on</strong>.During the period 1956-1983, nearly 12 percent of the Sinharaja wasdeforested almost entirely <strong>on</strong> the periphery, so that <strong>on</strong>ly 66 percentof the World Heritage site remains as primary forest (Barnyard andFernando, 1988).‘moderate’ or ‘poor’ (Gap Analysis final report, 2006).Despite these valuable c<strong>on</strong>servati<strong>on</strong> initiatives,assessment of the viability of natural vegetati<strong>on</strong> in SriLanka through the recently c<strong>on</strong>cluded ‘GAP analysis’ ofthe existing Protected Area system using GIS technology(Figure 1.9) showed that a c<strong>on</strong>siderable percentage offorests in the island are of the c<strong>on</strong>diti<strong>on</strong> categories ofDespite a slow regenerati<strong>on</strong> of logged forests, as dem<strong>on</strong>strated by poor representati<strong>on</strong> of endemic woody species inselectively logged areas in the Sinharaja eight years after logging was halted (de Zoysa et. al., 1990), a remarkableimprovement in ecosystem quality and forest regenerati<strong>on</strong> is now apparent in some of the larger Wet Z<strong>on</strong>e forests thatwere selectively logged in the 1970s (IUCN, 1993; Dela, 2003). This has been attributed to the ban <strong>on</strong> official logging ofnatural forests in the country, and the veering away of the Forest Department’s focus from producti<strong>on</strong> to forestc<strong>on</strong>servati<strong>on</strong>. The c<strong>on</strong>servati<strong>on</strong> value of Wet Z<strong>on</strong>e forests as the <strong>on</strong>ly refuge of some of the rarest faunal and floralspecies in the world is also now recognised, and there is a positive move by many Protected Area managers to engagelocal communities in forest c<strong>on</strong>servati<strong>on</strong> to preclude anthropogenic disturbances to forest ecosystems in all climaticz<strong>on</strong>es.Much of the remaining large tracts of forests in the country (Figure 1.3) as well as the larger Protected Areas (Figure10 a & b) c<strong>on</strong>sist of Dry Z<strong>on</strong>e forests. These forests, though less diverse than Wet Z<strong>on</strong>e forests, are n<strong>on</strong>etheless themain habitats for large mammals including the elephant; and carnivores, ungulates and primates show their highestspecies diversity in the Dry Z<strong>on</strong>e (MoFE, 1999). The Ruhuna Nati<strong>on</strong>al Park in the Dry Z<strong>on</strong>e is excepti<strong>on</strong>al in terms ofFourth Nati<strong>on</strong>al Report to the CBD: Sri Lanka 22
woody species and faunal diversity with regard to large herbivores and carnivores and the floodplains of the Mahaweliriver in the Dry Z<strong>on</strong>e are the most important habitats in the country with regard to wildlife biomass (ibid).Figure 1.8 Status of viability for natural vegetati<strong>on</strong>Sourse: Gap Analysis Report, MoENR, 2006Figure 1.10a: Protected Areas under the ForestFigure 1.10b: Protected Areas under the Department ofDepartmentWildlife C<strong>on</strong>servati<strong>on</strong>Sourse: Gap Analysis Report, MoENR, 2006Fourth Nati<strong>on</strong>al Report to the CBD: Sri Lanka 23
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the need for a mechanism to impleme
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Stockholm Convention</stron
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Chapter 44.1 Introduction4.1.1 The
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4.2.4. Evaluation of achieving targ
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for declaration of PAs, and adoptio
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• Programmes for ex-situ conserva
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The crop wild relatives projectThe
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WetlandsUnder the Wetland Conservat
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active in detecting such illegal ex
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egion for over a week (Arulpragrasa
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FOCAL AREA: MAINTAIN GOODS AND SERV
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FisheriesThe national marine fisher
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• Health and well being of rural
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• The MoENR has formulated a nati
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4.3 Impact of NBSAPs and related se
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Strategic goalsScale ofagreementSri
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Strategic goalsScale ofagreementSri
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Ministry of Environment & Natural R
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Appendix II - Further sources of in
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62. Fernando, N. (1997) A Personnal
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133. MoENR, 2007b. The Thematic Ass
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Appendix IIIProgress towards Target
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.2.1 Protected Areas under the DWLC
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National Target (NCSA 3 5.7, 2007)I
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disturbance by over-visitation and
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PoWPA Target: By 2008, sufficient f
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Project (2001-2008)Other Policies,
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There is no overall policy to guide
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The ADB funded Forest Resources Man
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Status of actions taken/in progress
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The Community Participation Project
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B.4.8 PoWPA Goal 3.2 - To build cap
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B.5 Overview of obstacles for imple