Abstract
A recent vegetation study [Palacio-Prieto et al. (2000) Bol Inst Geogr UNAM 43:183–203] showed that Mexico’s forest area has declined to 33.3%, from originally 52.0% of the country’s land area. In order to assess strategies for tree diversity conservation, we compiled a list of 846 tree species native to Mexico, and determined for each the presence or absence in 234 geographical squares of 1° latitude by 1° longitude (approximately 106 × 106 km). On the average, any two squares shared only 6% of their species composition. Using a standard optimization method from engineering and economics [Dantzig (1963) Linear programming and extensions. Princeton University Press, Princeton, NJ, USA, 625 p], we determined the minimally necessary land area in Mexico to conserve the 846 tree species, while securing that each species is found in an area of (approximately) 1,100 km2 of currently existing forest vegetation. Furthermore, we took into account 15 existing protected areas with a size of at least 1,100 km2 each. With these constraints, the total minimum area needed to conserve all 846 tree species is 45,136 km2 of currently existing forest vegetation, or 2.3% of Mexico’s surface. While this analysis can be refined with subsequent field work, the proposed reserve network indicates that efficient land use planning on a national scale may be able to conserve tree species diversity in a relatively small portion of Mexico, even after severe deforestation has taken place.
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Acknowledgements
This project was initiated with funding from Petróleos Mexicanos (PEMEX) in 1998, and we are grateful for their support. Furthermore, we thank Laura Arriaga and the team from CONABIO for providing data on tree species distributions. Eladio Velasco Sinaca helped with the data processing. Finally, several anonymous reviewers made observations that led to improvements in the manuscript.
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Appendices
Appendix 1: List of 846 tree species and their distributions in 234 geographical squares
The appendix is too extensive to be published here, and therefore is available upon request from the authors (mricker@ibiologia.unam.mx, gibarra@oikos.unam.mx, ems@ibiologia.unam.mx, hmhm@ibiologia.unam.mx). In addition to the sources of the information, it lists the species alphabetically including the plant family, species author, some (important) synonyms, maximum tree height, and the code numbers (as in the maps of Figs. 1, 2, and 5) for the squares in which the species was detected.
Appendix 2: Formulation of the linear optimization problem
MINIMIZE
SUBJECT TO
{DISTRIBUTION CONSTRAINTS:}
{Acacia acatlensis}
...826 constraint inequalities in accordance with the distributions in Appendix 1...
{Zygia stevensonii}
{CONSTRAINTS FOR SPECIES WITH A TOTAL EXTENSION SMALLER THAN 10% OF A SQUARE:}
{CONSTRAINTS FOR FORCING LARGE EXISTISTING CONSERVATION AREAS INTO THE OPTIMAL SOLUTION:}
{CONSTRAINTS THAT THE COEFFICIENTS SHALL BE PROPORTIONS, TAKING ON VALUES ONLY BETWEEN 0 AND 1:}
Appendix 3: Tree species with restricted south-north range (1 square only)
Amphitecna regalis, A. steyermarkii, Anisocereus gaumeri, Antirhea lucida, Attalea butyracea, Bernardia spongiosa, B. wilburi, Bunchosia mcvaughii, Carpodiptera ameliae, Cassia hintonii, Ceiba grandiflora, Cordia bicolor, C. salvadorensis, Cyphomandra rojasiana, Ebenopsis ebano, Eremosis oolepis, Erythrina caribaea, Erythroxylum panamense, Esenbeckia flava, Eugenia sotoesparzae, Eupatorium galeottii, Hamelia longipes, Jacquinia arborea, Jatropha bullockii, Licania gonzalezii, L. mexicana, L. sparsipilis, Lonchocarpus cochleatus, L. hintonii, L. mutans, L. unifoliolatus, Malpighia novogaliciana, Mappia racemosa, Micropholis melinoniana, Mosiera contrerasii, Nectandra leucocome, N. purpurea, Nopalea inaperta, Opuntia excelsa, Parathesis conzattii, P. psychotrioides, Parmentiera parviflora, Pereskia lychnidiflora, Phyllanthus grandifolius, Pilosocereus gaumeri, Pinus jaliscana, P. maximartinezii, P. muricata, P. nelsoni, native germplasm of P. radiata, P. rzedowskii, Piranhea mexicana, Pourouma bicolor, Pouteria rhynchocarpa, P. squamosa, Prosopis glandulosa, Psychotria sarapiquensis, Quararibea fieldii, Rhacoma puberula, Rinorea deflexiflora, R. uxpanapana, Sebastiania tikalana, Sideroxylon eucoriaceum, S. excavatum, S. lanuginosum, S. peninsulare, Sloanea medusula, S. petenensis, Stenocereus eichlamii, S. laevigatus, and Xylosma velutinum.
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Ricker, M., Ramírez-Krauss, I., Ibarra-Manríquez, G. et al. Optimizing conservation of forest diversity: a country-wide approach in Mexico. Biodivers Conserv 16, 1927–1957 (2007). https://doi.org/10.1007/s10531-006-9112-z
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DOI: https://doi.org/10.1007/s10531-006-9112-z