Swietenia Macrophylla), Assessed Using Rapds

Swietenia Macrophylla), Assessed Using Rapds

Heredity 83 (1999) 722±732 Received 29 April 1999, accepted 17 August 1999 Genetic diversity in Mesoamerican populations of mahogany (Swietenia macrophylla), assessed using RAPDs A. C. M. GILLIES *, C. NAVARROà, A. J. LOWE , A. C. NEWTON§, M. HERNAÂ NDEZà, J. WILSON & J. P. CORNELIUSà Institute of Terrestrial Ecology, Bush Estate, Penicuik, Midlothian EH26 0QB, Scotland, UK, àTropical Agricultural Center for Research and Higher Education (CATIE), Turrialba 7170, Costa Rica and §Institute of Ecology and Resource Management, University of Edinburgh, Darwin Building, May®eld Road, Edinburgh EH9 3JU, Scotland, UK Swietenia macrophylla King, a timber species native to tropical America, is threatened by selective logging and deforestation. To quantify genetic diversity within the species and monitor the impact of selective logging, populations were sampled across Mesoamerica, from Mexico to Panama, and analysed for RAPD DNA variation. Ten decamer primers generated 102 polymorphic RAPD bands and pairwise distances were calculated between populations according to Nei, then used to construct a radial neighbour-joining dendrogram and examine intra- and interpopulation variance coecients, by analysis of molecular variation (AMOVA). Populations from Mexico clustered closely together in the dendrogram and were distinct from the rest of the populations. Those from Belize also clustered closely together. Populations from Panama, Guatemala, Costa Rica, Nicaragua and Honduras, however, did not cluster closely by country but were more widely scattered throughout the dendrogram. This result was also re¯ected by an autocorrelation analysis of genetic and geographical distance. Genetic diversity estimates indicated that 80% of detected variation was maintained within populations and regression analysis demonstrated that logging signi®cantly decreased population diversity (P 0.034). This study represents one of the most wide-ranging surveys of molecular variation within a tropical tree species to date. It oers practical information for the future conservation of mahogany and highlights some factors that may have in¯uenced the partitioning of genetic diversity in this species across Mesoamerica. Keywords: conservation, genetic diversity, logging, RAPDs, Swietenia. Introduction Appendix II of the Convention on International Trade in Endangered Species (CITES), where the other species Mahogany (Swietenia macrophylla King) (Meliaceae, in the genus (S. humilis Zucc. and S. mahagoni (L.) Swietenioideae), is one of the most important timber Jacq.) are already listed (Rodan & Campbell, 1996). species in world trade. It is principally used for making Rates of mahogany overexploitation have been partic- furniture and interior ®ttings and has been an important ularly alarming for Mesoamerica, where overall defor- component in construction and ship building (Lamb, estation is estimated at around 4% annually (Myers, 1966). Its high economic value has resulted in over- 1989) and a large proportion of the mahogany-contain- exploitation across its natural range and this, coupled ing forests have already been lost. Thus, there is an with high deforestation rates, has led to the species urgent need for development of sustainable management becoming the focus of increasing concern (Newton et al., and conservation strategies for the remaining fragmen- 1996). Recently, it has been proposed for inclusion in ted populations of S. macrophylla. Swietenia macrophylla is a large, deciduous, tropical *Correspondence and Present address: Sir Harold Mitchell Building, tree, with a broad and often emergent crown. It is able School of Environmental and Evolutionary Biology, University of to reach a height of 40 m, a diameter at breast height of St. Andrews, St. Andrews, Fife, KY16 9TH, Scotland, UK. over 2 m and may live for several centuries. The species E-mail: [email protected] 722 Ó 1999 The Genetical Society of Great Britain. GENETIC DIVERSITY IN MAHOGANY 723 is very widely distributed, stretching from southern the wide availability of universal primers (Gillies et al., Mexico to the southern Amazon basin in Brazil (Mayhew 1997). Despite these practical advantages, however, its & Newton, 1998). It inhabits both wet and dry forests value in diversity studies has been questioned, owing to (rainfall typically 1000±2500 mm) and is found on a the dominant nature of the bands, which can lead to the range of soils up to 1400 m altitude (Whitmore, 1983). underestimation of recessive allele frequencies (Szmidt As with many tropical tree species, the density of et al., 1996). This potential skewing can be reduced by mahogany trees is typically fewer than one individual examining a large number of RAPD loci (more than 30) per hectare, although densities of up to eight trees per and using data analysis techniques, such as that hectare have also been recorded. Mahogany is monoe- described by Lynch & Milligan (1994), that compensate cious, with insect-pollinated (bees, moths and thrips), for the underestimation of the recessive allele when unisexual ¯owers. Pollination experiments indicate calculating allele frequencies. that it may be self-incompatible and a likely obligate The aim of the present investigation was to use RAPD outbreeder (Mayhew & Newton, 1998). Seeds are to quantify intraspeci®c genetic variation in S. macro- winged, but relatively heavy and tend to fall close to phylla populations across Mesoamerica. Results were the maternal tree (32±36 m median distance), although a also used in an attempt to identify factors that may have maximum dispersal distance of over 80 m has been in¯uenced the partitioning of genetic diversity within the estimated by Gullison et al. (1996) for trees in a Bolivian species across this region. population. Genetic diversity is essential to the long-term Materials and methods survival of tree species. Without it there may be a risk of extinction because of lack of adaptive ability Plant material (Hamrick, 1994). In the light of the 1992 UNCED Rio conference (Harper & Hawksworth, 1995), and Leaf material was collected from 420 mature mahog- general increased awareness of high deforestation rates any trees from 20 populations located in seven Meso- in the tropics, considerable eort is being channelled american countries and three geographical regions into increasing our understanding of the extent and (Table 1, Fig. 1). Selected populations were heteroge- distribution of genetic diversity within tree species, for neous for habitat type, population density and degree eective conservation and management strategies. of exploitation (Tables 1 and 2), and populations Most analyses have been based on allozyme data located within the same geographical region did not and concentrate on temperate and boreal species, necessarily share environmental attributes. Populations particularly conifers. In a recent review, Hamrick were located using local knowledge and previous (1994) outlined a number of life-history traits that reconnaissance. A neighbourhood size of 2.5 km radius aect the partitioning of genetic diversity in tree was adopted as a working de®nition of a population species. Four general observations are apparent from and populations within similar areas were separated by his ®ndings. First, tropical tree species, on average, a minimum of 5 km. Trees were sampled along a linear display lower levels of variation than temperate trees. transect within each population, until a maximum Secondly, species with a widespread geographical sample size of 65, or the end of the forest block, was distribution tend to display greater diversity than reached. Only mature trees (d.b.h. > 80 cm) were those of a more limited range. Thirdly, predominantly selected and the minimum distance between sampled outcrossing taxa maintain higher levels of genetic trees was set as 100 m, to reduce the chance of diversity than those that are primarily autogamous. sampling closely related individuals. One of the sam- Finally, sel®ng species tend to show a high degree of pled populations was a planted botanic garden (Lance- population substructuring, with diversity maintained tilla, Honduras). Data from this site were included only among rather than within populations. The opposite is in the diversity analysis to assess the merits of generally observed in outcrossing taxa. arti®cially planting mahogany for the conservation of In recent years, a variety of DNA-based techniques diversity within the genus. have been employed to study genetic variation in tree Leaf samples were silica-gel dried, then air-freighted species (e.g. RAPD, AFLPs, SSRs and CAPS). Advant- to Scotland for analysis. Herbarium specimens were ages of these methods over isozymes include their prepared for a subset of the individuals and deposited increased saturation of the genome and therefore better in herbaria at CATIE, the National Museum of Costa representation of the variation present within species Rica and the Pan-American Agricultural School in (Storfar, 1996). RAPD is a very useful DNA-based Zamorano, Honduras. Collection numbers of herbar- method for initial assessment of genetic diversity in ium specimens are available from the authors on plant species, owing to its technical ease and speed and request. Ó The Genetical Society of Great Britain, Heredity, 83, 722±732. 724 A. C. M. GILLIES Table 1 Swietenia macrophylla populations in the analysis Distance between ET AL Mean Mean population and point annual annual of reference for . Latitude Longitude Altitude precipitation temperature Sample meteorological

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