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Diameter increment patterns among 106 tree species in a logged and silviculturally treated Costa Rican rain forest
Institution:1. Tropical Agricultural Centre for Research and Higher Education (CATIE), Apartado 93, Turrialba 7170, Costa Rica;2. National Biodiversity Institute (INBio), Apartado 2300, Santo Domingo de Heredia, Costa Rica;1. Department of Industrial Engineering DII, University of Padua, Via Marzolo 9, 35131 Padua, Italy;2. National Center for Agricultural Utilization Research, Functional Foods Research Unit,1815 North University Street, Peoria, IL 61604, United States;3. National Center for Agricultural Utilization Research, Plant Polymer Research Unit,1815 North University Street, Peoria, IL 61604, United States;1. The Nature Conservancy, 4245 Fairfax Avenue, Suite 100, Arlington, VA 22203-1606, USA;2. Woodrow Wilson School of Public and International Affairs & Department of Ecology and Evolutionary Biology, Princeton University, Princeton 08540 NJ, USA;3. US Agency for International Development, US Embassy Jakarta, Jl. Medan Merdeka, Selatan 3-5, Jakarta 10110, Indonesia;4. Governor’s Climate and Forests Task Force, Jakarta, Indonesia;5. School of Earth and Environmental Sciences, The University of Queensland, Brisbane, Australia;6. School of Geography, The University of Melbourne, Parkville, Australia;7. The Nature Conservancy, Graha Iskandarsyah 3rd Floor Jl. Iskandarsyah Raya No. 66C Kebayoran Baru, Jakarta 12160, Indonesia;8. Terracarbon LLC, 707 E Jefferson Street, Charlottesville, VA 22902, USA;9. Department of Biology, University of Florida, P.O. Box 118526, Gainesville, FL 32611-8526, USA;1. Centre for Ecology and Hydrology, Benson Lane, Wallingford, Oxfordshire OX10 8BB, UK;2. Centre for Conservation, Ecology and Environmental Science, Faculty of Science and Technology, Bournemouth University, Poole BH12 5BB, UK;3. Forest Ecology and Conservation Research Group, Imperial College London, Silwood Park, Buckhurst Road, Ascot, Berkshire SL5 7PY, UK;1. INRA, UMR “Ecologie des Forêts de Guyane” AgroParisTech-CIRAD-INRA-CNRS-Université de Guyane-Université des Antilles, Campus Agronomique, 97387 Kourou, Guyane Française, France;2. CIRAD, UMR “Ecologie des Forêts de Guyane” AgroParisTech-CIRAD-INRA-CNRS-Université de Guyane-Université des Antilles, Campus Agronomique, Kourou, Guyane Française, France;3. INPHB Institut National Polytechnique Félix Houphouët-Boigny, BP 1093, Yamoussoukro, Cote d’Ivoire;4. National Institute for Space Research (INPE), São José dos Campos, SP 12227-010, Brazil;5. Université de Lorraine, AgroParisTech, INRA, UMR Silva, 54000, Nancy, France;1. CarboForExpert, Hermance, 1248, Switzerland;2. UR BSEF, CIRAD, Montpellier, 34398, France;3. UMR Ecofog, CIRAD, Kourou, 97310, France;4. UMR Ecofog, Inra, Kourou, 97310, France;5. International Center for Tropical Botany, Florida International University, Miami, Florida, 33199, USA;6. ONF-Guyane, Cayenne, 97300, France;7. EMBRAPA, Macapá, Amapá, 68903, Brazil;8. EMBRAPA, Belém, Pará, 66095, Brazil;9. EMBRAPA, Rio Branco, Acre, 69900, Brazil;10. Forest Ecology and Forest Management Group, Wageningen University, Wageningen, 6700AA, the Netherlands;11. Instituto Boliviano de Investigación Forestal, Santa Cruz de la Sierra, 10260, Bolivia;12. Biology Department, University of Florida, Gainesville, Florida, FL 32611-8525, USA;13. Iwokrama, Hight St, Georgetown, Guyana;14. Environmental Change Institute, Oxford University Centre for the Environment, University of Oxford, Oxford, OX1 3QY, UK;15. EMBRAPA, Manaus, Amazonas, 69011, Brazil;16. Escola Superior de Agricultura Luiz de Queiroz, University of São Paulo, São Paulo, 01002, Brazil;17. Biodiversity Department, CELOS, Paramaribo, Paramaribo, Suriname
Abstract:Studies of growth rates of trees in managed neotropical forests have rarely employed complete botanical identification of all species, while published information for Central American lowland rain forests largely concerns forests free of recent disturbance. We studied diameter increments of trees in a managed Costa Rican rain forest. The Pentaclethra macroloba-dominated forest was located on low hills with Ultisols in Holdridge's Tropical Wet Forest life zone. The 540 m × 540 m (29.2 ha) experimental area was lightly logged during 1989–1990. The 180 m × 180 m (3.24 ha) experimental plots comprised a 100 m × 100 m (1.0 ha) central permanent sample plot (PSP) with a 40-m wide buffer strip. Post-harvest silvicultural treatments were liberation/refinement (in 1991) and shelterwood (in 1992), applied under a complete randomized block design with three replicates, using logged but untreated plots as controls. All live trees ≥10 cm DBH in the PSPs, were identified to species; data reported are for 1993–1996. Cluster analysis was used to group species on the basis of the median and quartiles of their diameter increment distributions, separating data by silvicultural treatments; five diameter increment groups were established and subdivided on the basis of the adult height of each species (four categories), giving 17 species groups in the final classification. Adult height and silvicultural treatment made a significant contribution to growth rate variation. Median annual increments of the slowest-growing species groups, which featured many under- and middle story species, were ca. 1 mm; those for the fastest growing species, which were mainly canopy and emergents, were ca. 16 mm. All species in the groups of very fast growth were pioneers, whether short or long-lived, though many other pioneer species did not show fast growth. The proportions of species found in groups of moderate, fast or very fast growth were greater in the silviculturally treated plots than in the controls, and one complete diameter increment group, of fast growth, was only represented in the treated plots. Crown form, crown illumination and presence of lianas in the crown, showed significant correlations with diameter increments, though the importance of these latter two variables varied with silvicultural treatment. The very fast growth groups differed from the others in having higher proportions of trees with well-formed, well-illuminated crowns and an irregular diameter distribution with relatively few individuals in the smallest DBH class. Comparison with data from other neotropical forest sites shows that long-lived pioneers such as Vochysia ferruginea and Jacaranda copaia grow fast or very fast at all sites, while non-commercial canopy and emergent species of Chrysobalanaceae and Sapotaceae appear to be uniformly slow-growing. Growth data for the majority of species are, however, published for the first time.
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