Master in Biodiversity and Conservation in Tropical Regions
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Master in Biodiversity and Conservation in Tropical Regions Biogeography and Conservation Status of Diurnal Raptors in Venezuela By Adrian Naveda-Rodríguez A thesis submitted In partial fulfillment of the requirements for the degree of Master of Science Advisor: Keith L. Bildstein, Ph.D. Academic year 2012 – 2013 ACKNOWLEDGMENTS This work was possible thanks to logistical and financial support provided by the Spanish Research Council (CSIC), Hawk Mountain Sanctuary, The Peregrine Fund and Wild4Ever. I wish to thank all those who contributed throughout the course of this work. I am absolutely indebted to my lovely wife Gabriela Lugo, my parents Maritza Rodriguez and Rafael Naveda who supported me in this process. I am very grateful to Dr. Keith Bildstein for introducing me to raptor conservation sciences and for all the opportunities he has given me since 2006. I am also grateful to Dr. Hernán Vargas and Dr. Gary Riggs for their confidence and support for this project. Marcial Quiroga-Carmona, José Gustavo León, Tony Crease, Alan Highton and Christian Olaciregui provided valuable information on raptors of Venezuela and Colombia. I sincerely appreciate the efforts of Marcial Quiroga-Carmona, Jorge Peralta and Bayron Calles for their help with statistical analyses. I appreciate the improvements in English usage made by Phillip Schwabl I kindly appreciate Francisco Bisbal, Alexis Araujo, Miguel Lentino, Jurahimar Gamboa, Marcos Salcedo, Carlos Rengifo and Rosana Calchi for providing information on voucher specimens in ornithological collections under their care. ABSTRACT Aim: Natural history data is crucial to monitor the vulnerability of birds of prey. In Venezuela, this information is non-existent for almost all species of raptors. Here, I examine the biogeography and conservation status of birds of prey of the order Cathartiformes, Acciptriformes and Falconiformes in Venezuela. Location: Venezuela, northern South America. Method: By means of ecological niche modeling, the geographic distribution (SDM) of 65 species of diurnal raptors was described. Nine climatic and seven landscape metrics were used as environmental predictors. In a GIS environment the extent of occurrence (EOO) was estimated for each species using the minimum presence training threshold. SDM were stacked to examine species richness (S) patterns. Predictors of S were investigated using a regression model. The EOO was used to re-evaluate the conservation status of diurnal raptors in Venezuela, applying the criterion B1 of the IUCN Red List. Furthermore, a gap analysis was performed to evaluate the effectiveness of strict protected areas in the conservation of raptor diversity. Results: The EOO ranged from 1,072 km2 to 881,918 km2. 40 species showed a continuous distribution, while a disjunct distribution was observed in 25 species. S differed among bioregions. However, six pairwise compared bioregions did not show differences. Highest S values were located in the Guiana Shield and the mountains ranges of northern Venezuela. S was explained mainly by landscape features, specifically forest canopy height, land cover and terrain slope. Five species met the B1 criterion and were re-classified. Main conclusions: Environmental heterogeneity affects the configuration of EOO areas and the distribution of S and is therefore an important aspect to consider in conservation planning for neotropical birds of prey. The computation of EOO areas is susceptible to the applied estimation methods, and responses from environmental variables used to predict S are scale-dependent; therefore, it is necessary to standardize methods and experimental design to study the biogeography of raptor species. Priority-setting for the conservation of raptor species in Venezuela must consider rare species, even if they are not threatened. A territorial re-ordering is urgent to improve the protection of this group of birds. 1 INTRODUCTION The Neotropic, an area of more than 20 million km2 comprising South and Central America, the Caribbean islands, parts of Mexico and southern Florida, is the richest biogeographic region in the world (Ojasti 2000, García-Moreno et al. 2007, Rodríguez & Rojas- Suárez 2008). In this context, Venezuela holds a special ecological significance due to its geography, which includes part of the Cordillera de Los Andes, the Guiana Shield, the Llanos, the Caribbean Sea and the Atlantic Ocean. These locations give the country a wide diversity of biomes along 27 climatic zones, giving rise to 650 natural vegetation types, 23 landforms and 37 major geological units. In consequence, Venezuela is among the 17 countries with the greatest biological diversity in the world (megadiverse countries), with 15,000 higher plant species, 351 mammal species, 1,400 bird species, 340 reptile species, 315 amphibian species and over 1,800 fish species (Mittermeier et al. 1997, MARN 2000, Aguilera et al. 2003, Rodríguez & Rojas- Suárez 2008). Birds are the best known vertebrate group in Venezuela due to the interest of the scientific community (Lentino 2003); nevertheless, the development of the ornithological knowledge in the country is still incipient, particularly in specific cases such as with birds of prey, which include about 90 species of diurnal and nocturnal raptors (Ferguson-Lees & Christie 2001, König & Weick 2008). The diurnal raptors of Venezuela are comprised of 68 species distributed in four families of the order Cathartiformes, Accipitriformes and Falconiformes (Ascanio et al. 2012, Hilty 2003). As are other tropical raptors species, they are confronting threatening factors such as habitat loss and destruction, environmental pollution and human persecution (Bierregaard 1998, Bildstein et al. 1998). Thus, conservation action is required to prevent species loss. In the last evaluation of extinction risk of Venezuelan wildlife, six species of diurnal raptors were included (Rodríguez & Rojas-Suarez 2008), one species was listed as critically endangered, two species as vulnerable, three species as near threatened and six species as data deficient. The conservation status assessment of Venezuelan raptors has been in some cases underestimated whereas in others overestimated. According to IUCN (2012), the evaluation of the global conservation status of any species is based on any of the following five criteria: (A) 2 Reduction in population size, (B) Geographic range in the form of Extent of Occurrence or Area of Occupancy, (C, D) Population size estimates and (E) Quantitative analysis showing the probability of extinction in the wild. The information required to apply any of these criteria is not available in Venezuela due to the lack of biological information on birds of prey. The natural history of diurnal raptors in Venezuela has been poorly studied, and only a few species have been subject of detailed description and analysis of their autoecology (Alvarez- Cordero 1996, Balgooyen, 1989, Beissinger et al. 1988, Mader 1982); basic (but not less important) aspects such as species richness and geographic distribution patterns and the factors determining them, remain unstudied for most species. Consequently, little is known about how the number of species varies among the biogeographic regions of Venezuela. Available distribution maps in field guides and in Ridgely et al. (2007) lack metadata and incur omission/commission errors. The deficiency in knowledge of the natural history and population biology of birds of prey do not allow the correct assessment of the conservation status, as well as the design and implementation of effective conservation strategies. Sound scientific evidence based on a number of biological factors, the knowledge of geographic distribution and population density (Bierregaard 1998) as well as species richness patterns are crucial in monitoring and mitigating the vulnerability of raptors species. In an attempt to fill this gap, I performed biogeographic analysis and an evaluation of conservation status by means of geographic distribution of the Cathartiformes, Accipitrifomes and Falconiformes of Venezuela. I addressed my effort by: (1) describing the geographic distribution of diurnal raptors, (2) describing patterns of species richness, (3) determining the environmental variables that shape species richness patterns, (4) assessing the current conservation status of diurnal raptors in Venezuela. MATERIALS AND METHODS Study area Venezuela is in northern South America, between latitudes 00º45’ North and 15º40’ North and between meridians 59º45’ West and 73º25’ West. Its total land mass occupies 916,445 km2 and its maritime territory covers around 900,000 km2. Venezuela is bordered in the south by 3 Colombia and Brazil, in the west by Colombia and in the east by Guyana. The Dominican Republic, Netherlands Antilles and United States of America (Puerto Rico and Virgin Island) lie to the north and France (Martinique and Guadalupe Islands) and Trinidad and Tobago lie to the East (MARN 2000). Delimitations of natural regions or bioregions of Venezuela vary according to the author and definition criteria. Nonetheless, there is a general consensus in recognizing at least nine spatial units with distinct environmental and geographical characteristics (PDVSA 1992, Linares 1998). In this work I included the 13 bioregions defined by Huber & Alarcón (1988). These include: Insular, Coastal, Central Coastal Range, Eastern Coastal Range, Orinoco Delta, Maracaibo Lake Basin, Llanos, Mountain Range of Mérida, Mountain Range of Perijá, Lara- Falcón Hill System, Guayana Massif,