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In situ gap analysis of genetic diversity of wild Coffea species from Mauritius Ehsan Dulloo IPGRI Coffea macrocarpa, a wild coffee relative 27-30 April 2005 Workshop 2: Threat and conservation assessment Overview Background Steps on target taxa and region in Gap analysis Ecogeographic Genetic survey diversity analysis Conservation Lessons Priorities learnt Background on Coffee Important beverage world wide Family : Rubiaceae Sub Family: Ixoroideae Tribe: Coffeeae Sections: Paracoffea, Argocoffea, Mascarocoffea and Eucoffea >100 species world wide; endemic to Africa All species are diploid (2n=22) and outcrossing except C. arabica (allotetraploid) and is self sterile Natural Distribution of coffee species in Africa and Madagascar Mascarene islands Mascarenes islands 3 Volcanic islands SW of Indian oceanMauritius, Reunion, Rodrigues Uninhabited Rich diversity of endemic plants – 955 native flowering plant taxa (73% endemic) Mauritius- 685 natives; 311 endemics With human colonisation-rapid deforestation Threats Deforestation Land clearing for agriculture Habitat alteration Invasive alien species (introduced animals & plants) Conservation history Pioneering ecological studies in 1930’s – Native vegetation: Palm savannah, Lowland dry forest, Upland wet montane rainforest 1950’s- Creation of protected areas- Nature Reserves 1970s- conservation reports on Mauritius; focus on CR endemic avifauna 1980’s – IUCN/WWF Plant programme- rescue critically endangered plants through ex situ conservation, Red data book In situ conservation Species Ecosystem Establishment of Conservation Management areas within PAs Elimination of invasives, active restoration, permanent quadrats 1990s – Creation of first National Park on Mauritius Target taxa Coffea mauritiana Coffea macrocarpa Coffea myrtifolia Target Coffea taxa Coffea mauritiana Lam. Mauritius & La Reunion endemic Conservation status: Threats: Mauritius: CR (B 1,2a); La Reunion VU (C 2a) alien species People picking wild fruits Seed predation by pigs, birds Ecology: Mid to high altitude wet montane rainforest Target taxa Coffea macrocarpa A. Rich Endemic to Mauritius Conservation status: VU (C 2a) Threats: Aliens species, deer grazing, people picking wild fruits Ecology: Widespread distribution in the upland climax montane rain forest to lowland moist forest and open dwarf Sideroxylon forest Target taxa Coffea myrtifolia (A. Rich ex DC) leroy Endemic to Mauritius Conservation status: EN (B 1,2ciii; D) CR – AOO <10km2 and a total population of 150 indiv. known from at least 5 pop and one has >50 individuals Threats: alien species, browsing by deer, habitat alteration, low genetic variability, seed predation Ecology: Evergreen dry forest Objective of the study Gap analysis of wild Coffea of Mauritius to ensure that genetic diversity is effectively and efficiently conserved in protected areas Gap Analysis Gap analysis is a method for identifying gaps in network of conservation areas. Analysis should allow identification of hotspots which might offer efficient conservation opportunities Allows setting of priorities Helping in reserve selection and design Steps in Gap analysis Identify and classify biodiversity Locate areas managed primarily for biodiversity Area of occurrence within native vegetation areas and protected areas or under management Identify biodiversity that is unrepresented in those managed areas Focus in on wild coffea species and the extent and distribution of its genetic diversity Compare distribution of Coffea spp. with protected areas Set priorities for conservation actions Recommendation for protected areas or other conservation actions Ecogeographic survey Purpose was to map distribution of wild Coffea spp. in the Mascarene Herbarium survey- 248 specimen were examined Field work- based on C. mauritiana: 6 localities in MRU & 25 in REU C. macrocarpa: 18 localities C. myrtifolia: 8 localities Herbarium survey Information from specialists, local field workers 26 localities were surveyed in MRU & REU Distribution maps containing historical & actual sites Table 1: Main herbarium collection of Mascarene Coffea taxa. (Codes from Holmgren et al. 1990) Code Herbarium Specialist consulted MAU Herbarium, Mauritius Sugar Industry Research Mr. J. Guého Institute, Réduit, Mauritius K Herbarium, Royal Botanic Gardens Richmond, Surrey TW9 3AB, U.K P Herbier, Laboratoire de Phanérogamie, Museum Dr. M. Bosser National d’Histoire Naturelle, 16 Rue Buffon F75005, Paris, France. REU Herbier de La Réunion, Laboratoire de Biologie Dr. D. Strasberg Végétale, Université de La Réunion, B.P 5, 97490 Sainte Clotilde, Réunion. Kew, Dr D. Bridson Distribution maps of wild coffee were produced C. mauritiana Genetic diversity studies Purpose was to determine the genetic relationships between coffee species and to study the distribution of genetic diversity in wild populations and compare with existing conservation areas Allows to define which areas have highest genetic diversity i.e. genetic hotspots areas (within population diversity) 16 populations were studied using RAPD markers RAPD 20 different primers were screened 12 produced clear and discrete bands Of these, two primers (OPA-04 and OPI-20), were selected for the RAPD assay of all the Coffea accessions (5 indiv. per population). 85 polymorphic bands were used for the analysis Similarity index matrix was generated using simple matching coefficient with NTSYS-pc software to construct dendrograms using the UPGMA Genetic analysis 25 of 85 polymorphic bands were unique to one of the four clusters Within population genetic diversity (Hj) is more important at looking for GD hotspots High diversity in MDR, PCH, FLO, MDC and MLO Low diversity in C. myrtifolia (small population sizes) Population % of polymorphic markers Diversity index (Hj) BBL 27.1 0.106 BOM 15.3 0.066 MLO 32.9 0.125 PER 23.5 0.098 MAC 18.8 0.076 MDR 42.4 0.160 FLO 32.9 0.131 PET 32.9 0.117 MDC 32.9 0.126 PCH 37.6 0.139 MCO 25.9 0.093 BV 28.2 0.105 COL 27.1 0.098 CIT 16.5 0.072 MAG 17.6 0.074 MBR 14.1 0.061 Cluster analysis Taxonomic confirmation about three species + One cluster for MDC population C. mauritiana: Clear distinction between accessions Mru & Reu Gaps in protected areas Important populations of C. macrocarpa are not located in PA – MDC, MDR, BBL Many populations within PA are also in Conservation Management Areas C. mauritiana: No PA in Reunion; No CMA at Plaine Champagne (Mru) Population of C. myrtifolia are outside PA Priorities for in situ conservation Criteria Conservation threat highest Are not in PA and/or managed areas Populations which have high GD Socio-economic and political factors Priority Montagne des Creoles (MDC) C. myrtifolia population: Magenta C. mauritiana in Reu PCH pop in Mru Lessons learnt Value of ecogeographic surveys Conservation threats assessment Value of genetic analysis and determination of genetic diversity hotspots Helps in validating taxonomic relatedness among species Effectiveness of protected areas Setting up of priorities for conservation Thank you