Ecological Assessment of the Flamingo Mangroves, Guanacaste, Costa Rica

Total Page:16

File Type:pdf, Size:1020Kb

Ecological Assessment of the Flamingo Mangroves, Guanacaste, Costa Rica Ecological Assessment of the Flamingo Mangroves, Guanacaste, Costa Rica Derek A. Fedak & Marie Windstein Advisors: Curtis J. Richardson & Charlotte R. Clark Nicholas School of the Environment Duke University Spring 2011 Abstract Mangroves are tropical and subtropical ecosystems found in intertidal zones that provide vital ecosystem services including sustenance of commercially important fishery species, improvement of coastal water quality through nutrient cycling and sediment interception, and protection of coastal communities from storm surge and erosion. However, land use conversion and water pollution are threatening these ecosystems and their associated services worldwide. This master’s project conducted an ecological assessment on a mangrove forest adjoining the property of the Flamingo Beach Resort and Spa in Playa Flamingo, located in the Guanacaste province of Costa Rica. The project analyzed vegetation health, water and soil quality, bird species richness, and identified threats to the forest. It also assessed several options for the resort’s development of ecotourism, such as community involvement, the construction of an educational boardwalk, and the creation of a vegetation buffer adjoining the mangroves. The results indicate that the Flamingo Mangroves are generally in a healthy state. Vegetation structure like canopy height, biomass, vegetation importance values, and species distribution compares well with previous ecological studies on mature tidal mangroves. The ecosystem supports 42 resident bird species and likely up to 30 migratory species. However, water quality is a major concern, which reported elevated levels of nitrogen and phosphorus through runoff and discharged wastewater in the northern section of the forest. Additionally, the western edge of the forest adjoining the beach road is frequently disturbed by automotive traffic and runoff, displaying reduced or stunted vegetation and sandy soil. This report contains several recommendations on how to preserve the mangroves by improving water quality, reducing physical and chemical disturbances, and engaging the community. The results of the project will be incorporated into our client‘s and Flamingo community‘s future management practices to conserve the Flamingo Mangroves and emphasize the value of this ecosystem. II Table of Contents Introduction ................................................................................................................................................ 1 Study Site ................................................................................................................................................. 2 Client’s Objectives ................................................................................................................................... 3 Study’s Objectives .................................................................................................................................... 4 Chapter I: Vegetation Survey ...................................................................................................................... 6 Objectives ................................................................................................................................................ 6 Background .............................................................................................................................................. 6 Methods .................................................................................................................................................. 9 Results and Discussion ........................................................................................................................... 12 Overall Picture ....................................................................................................................................... 20 Chapter II: Analysis of Water Samples ..................................................................................................... 21 Objectives .............................................................................................................................................. 21 Background ............................................................................................................................................ 21 Methods ................................................................................................................................................ 25 Results and Discussion ........................................................................................................................... 27 Salinity ............................................................................................................................................... 27 Total Nitrogen .................................................................................................................................... 28 Total Phosphorus ............................................................................................................................... 31 N:P ratio ............................................................................................................................................. 33 Overall Picture ....................................................................................................................................... 33 Chapter III: Analysis of Soil Samples ......................................................................................................... 35 Objectives .............................................................................................................................................. 35 Background ............................................................................................................................................ 35 Methods ................................................................................................................................................ 39 Results and Discussion ........................................................................................................................... 43 Transects ............................................................................................................................................ 43 Total Carbon, Nitrogen, and Phosphorus Along the Two Transects and in the Tidal Channels ......... 47 Overall Picture ....................................................................................................................................... 52 III Chapter IV: Birds ....................................................................................................................................... 53 Objectives .............................................................................................................................................. 53 Background ............................................................................................................................................ 53 Methods ................................................................................................................................................ 54 Results and Discussion ........................................................................................................................... 56 Overall Picture ....................................................................................................................................... 58 Chapter V: Community Involvement ........................................................................................................ 62 Goals ...................................................................................................................................................... 62 Mangrove Cleanup ................................................................................................................................ 62 Presentation to La Paz School ................................................................................................................ 63 Youth Involvement in Conservation of Flamingo Mangroves ................................................................ 64 Chapter VI: Recommendations and Conclusions ..................................................................................... 65 Water Quality ........................................................................................................................................ 65 Boardwalk .............................................................................................................................................. 66 Beach Road ............................................................................................................................................ 69 Community Involvement ....................................................................................................................... 71 Ramsar Listing ........................................................................................................................................ 72 Appendix ................................................................................................................................................... 76 Bibliography .............................................................................................................................................. 83 IV List of Figures Figure 1: Map of Flamingo Mangrove Area in NW Costa Rica ....................................................................
Recommended publications
  • Environmental Sensitivity Index Guidelines Version 2.0
    NOAA Technical Memorandum NOS ORCA 115 Environmental Sensitivity Index Guidelines Version 2.0 October 1997 Seattle, Washington noaa NATIONAL OCEANIC AND ATMOSPHERIC ADMINISTRATION National Ocean Service Office of Ocean Resources Conservation and Assessment National Ocean Service National Oceanic and Atmospheric Administration U.S. Department of Commerce The Office of Ocean Resources Conservation and Assessment (ORCA) provides decisionmakers comprehensive, scientific information on characteristics of the oceans, coastal areas, and estuaries of the United States of America. The information ranges from strategic, national assessments of coastal and estuarine environmental quality to real-time information for navigation or hazardous materials spill response. Through its National Status and Trends (NS&T) Program, ORCA uses uniform techniques to monitor toxic chemical contamination of bottom-feeding fish, mussels and oysters, and sediments at about 300 locations throughout the United States. A related NS&T Program of directed research examines the relationships between contaminant exposure and indicators of biological responses in fish and shellfish. Through the Hazardous Materials Response and Assessment Division (HAZMAT) Scientific Support Coordination program, ORCA provides critical scientific support for planning and responding to spills of oil or hazardous materials into coastal environments. Technical guidance includes spill trajectory predictions, chemical hazard analyses, and assessments of the sensitivity of marine and estuarine environments to spills. To fulfill the responsibilities of the Secretary of Commerce as a trustee for living marine resources, HAZMAT’s Coastal Resource Coordination program provides technical support to the U.S. Environmental Protection Agency during all phases of the remedial process to protect the environment and restore natural resources at hundreds of waste sites each year.
    [Show full text]
  • Spectral Characterization of Mangrove Leaves in the Brazilian Amazonian Coast: Turiaçu Bay, Maranhão State
    Anais da Academia Brasileira de Ciências (2007) 79(4): 683-692 (Annals of the Brazilian Academy of Sciences) ISSN 0001-3765 www.scielo.br/aabc Spectral characterization of mangrove leaves in the Brazilian Amazonian Coast: Turiaçu Bay, Maranhão State FLÁVIA REBELO-MOCHEL1 and FLÁVIO J. PONZONI2 1Departamento de Oceanografia e Limnologia, Universidade Federal do Maranhão, Campus Universitário, Bacanga 65080-240 São Luís, MA, Brasil 2Instituto Nacional de Pesquisas Espaciais, Divisão de Sensoriamento Remoto, Av. dos Astronautas, 1758 12227-010 São José dos Campos, SP, Brasil Manuscript received on February 2, 2006; accepted for publication on December 12, 2006; presented by ALCIDES N. SIAL ABSTRACT Mangrove communities are tropical systems which have fewer species than tropical forests, especially in Latin Amer- ica and display a single architecture, usually lacking the various strata commonly found in other forest ecosystems. The identification of mangrove communities by orbital data is not a difficult task but the most interesting challenge is to identify themselves by the dominant species. The first step toward that floristic identification is the spectral character- ization of detached leaves. Leaves from four species of mangrove trees were spectrally characterized considering the Directional Hemispherical Reflectance Factor (DHRF) determined through radiometric measurements using an inte- grating sphere LICOR 1800 attached to a spectroradiometer SPECTRON SE-590. In the visible bands (0.45-0.69 µm) the button-shaped mangrove Conocarpus erectus was brighter and the red mangrove Rhizophora mangle was darker than the other two species which shows very close DHRF values. Otherwise the black mangrove Avicennia germinans and the white mangrove Laguncularia racemosa can be distinguished from one another in the Near Infra Red (NIR) region (0.76-0.90 µm and in this region of the spectrum the DHRF of C.
    [Show full text]
  • Species Composition and Diversity of Mangrove Swamp Forest in Southern Nigeria
    International Journal of Avian & Wildlife Biology Research Article Open Access Species composition and diversity of mangrove swamp forest in southern Nigeria Abstract Volume 3 Issue 2 - 2018 The study was conducted to assess the species composition and diversity of Anantigha Sijeh Agbor Asuk, Eric Etim Offiong , Nzube Mangrove Swamp Forest in southern Nigeria. Systematic line transect technique was adopted for the study. From the total mangrove area of 47.5312 ha, four rectangular plots Michael Ifebueme, Emediong Okokon Akpaso of 10 by 1000m representing sampling intensity of 8.42 percent were demarcated. Total University of Calabar, Nigeria identification and inventory was conducted and data on plant species name, family and number of stands were collected and used to compute the species importance value and Correspondence: Sijeh Agbor Asuk, Department of Forestry and Wildlife Resources Management, University of Calabar, PMB family importance values. Simpson’s diversity index and richness as well as Shannon- 1115, Calabar, Nigeria, Email [email protected] Weiner index and evenness were used to assess the species diversity and richness of the forest. Results revealed that the forest was characterized by few families represented by few Received: October 23, 2017 | Published: April 13, 2018 species dominated by Rhizophora racemosa, Nypa fructicans, Avicennia germinans and Acrostichum aureum which were also most important in the study and a few other species. Furthermore, presence of Nypa palm (Nypa fructicans) as the second most abundant species in the study area was indicative of the adverse effect of human activities on the ecosystem. The Simpson’s diversity index and richness of 0.83 and 5.896, and Shannon- Weiner diversity and evenness of 2.054 and 0.801 respectively were low, compared to mangrove forests in similar locations thus, making these species prone to extinction and further colonization of Nypa fructicans in the forest.
    [Show full text]
  • Abstract Resumen
    BIOTROPICA 23(4a): 488-496 1991 Effects of Hurricane Gilbert on Birds in a Dry Tropical Forest in the Yucatan Peninsula 1 James F. Lynch Smithsonian Environmental Research Center, P.O. Box 28, Edgewater, Maryland 21037, U.S.A. ABSTRACT On 14 September 1988 Hurricane Gilbert, the strongest tropical storm ever recorded in the Western Hemisphere, passed through an area oftropical forest in Quintana Roo, Mexico, where I had been studying winter bird populations since 1984. The hurricane defoliated the forest, and created a nearly impenetrable tangle of fallen branches and vines at ground level. Point counts and mist-netting conducted 5-6 mo after the storm revealed an influx of field- and shrub-associated bird species. Most previously common insectivores and feeding generalists were present in February­ March 1989, but many had declined significantly in abundance. Resident frugivores and nectarivores were especially scarce after the hurricane. Wildfires that swept through northeastern Quintana Roo in the summer of 1989 had a greater effect on birds than did the storm itself. By late winter 1990 the bird community within unburned forest was clearly converging toward its prehurricane composition. In contrast, the bird community in burned forest resembled that associated with recently abandoned agricultural fields and pastures. As a group, overwintering nearctic migrants appeared to be more resilient than year-round residents to the effects of both the hurricane and the associated fires. RESUMEN El 14 de septiembre de 1988 de huracan Gilberto, la tormenta tropical mas fuerte registrada hasta ahora en el hemisferio occidental, paso a traves de un area de bosque tropical en Quintana Roo, Mexico, donde se habian estado estudiando poblaciones de pajaros de invierno desde 1984.
    [Show full text]
  • Environmental Impact Assessment
    ENVIRONMENTAL IMPACT ASSESSMENT For ARA MACAO Resort & Marina To be located in: Placencia, Stann Creek District Prepared by: Volume 1 January 2006 Table of Contents 1.0 Project Description & Layout Plan 1-1 1.01 Project Location and Description 1-1 1.02 The Physical Development Plans and the Description of the Facilities. 1-2 1.03 Plan Layout 1-5 1.04 Specifications for the Facilities and Forecast of Activities 1-7 1.05 Phases of Project Implementation 1-7 2.0 The Physical Environment 2-1 2.01 Topography 2-1 2.02 Climate 2-5 2.03 Geology 2-6 2.2 Project Facilities 2-10 3.0 Policy and Legal Administrative Framework 3-1 3.1 Policy 3-1 3.2 Legal Framework 3-2 3.3 Administrative Framework 3-4 3.4 The EIA Process 3-6 3.5 Permits and approvals required by the project 3-7 3.6 International And Regional Environmental Agreements 3-8 4.0 Flora and Fauna 4-1 4.1 Introduction 4-1 4.1.1 Mangrove Swamp 4-1 4.1.2 Freshwater Marsh and Swamps 4-1 4.1.3 Transitional Low Broadleaf Forest 4-1 4.2 Flora Survey 4-2 4.3 Avifaunal Survey 4-6 4.3.1 Results of bird census 4-6 4.4 Species of Key Conservation Concern 4-10 4.4.1 Reptiles 4-10 4.4.1.1 Crocodiles (Family Crocodylidae) 4-10 4.4.1.2 Spiny Tailed Iguana 4-11 4.4.1.3 Boa Constrictor 4-11 4.4.1.4 Mammals 4-11 4.5 Estimated Alteration of Vegetation 4-12 4.6 Impacts and Mitigation Measures 4-12 5.0 Water Resource 5-1 5.1 Occupancy Rate 5-1 5.2 Potable Water Demand 5-1 5.3 Water Source 5-3 5.3.1 Preferred Option 5-3 5.4 Water Supply Description 5-5 5.5 Ground and Surface Waters Analysis 5-5 5.5.1 Water Quality
    [Show full text]
  • Yucatan Peninsula Independent Budget Birding August 11-20, 2016
    Mexico: Yucatan Peninsula Independent Budget Birding August 11-20, 2016 Ross and Melissa Gallardy ww.budgetbirders.com Summary: Birding the Yucatan Peninsula is very straight forward. All of the birding spots are easily accessible, the roads are wide, paved, and in great condition, and people (away from the super touristy areas) are very friendly. Although it took us 10 days to cover this area, a dedicated birding trip covering all areas could be completed in a few less days. My itinerary was a bit complicated as I spent a few days birding before returning to the Cancun area for a wedding and then resumed birding for a few more days. This report covers the main birding areas we visited discussing directions/access, general birding advice/strategy for each location, and any additional logistics with regards to costs. August isn’t an ideal time to visit this area of Mexico due to the lack of neotropical migrants and hot weather, but overall I was very pleased with the bird activity. The biggest inconvenience was the number of mosquitos, which were very prevalent at most locations. At the end of the report I’ve included a list of the “better” birds encountered on the Yucatan Peninsula and where to find them. I finished the 10 day trip with 181 species including almost all of the regional endemics. Overall, the total cost (including international airfare) for my wife and I was $1,554.83 Resources: Websites: As usual, xeno-canto, cloudbirders, and eBird were extremely valuable resources in researching and preparing for the trip.
    [Show full text]
  • YUCATAN, MEXICO - 2018 Th Th 27 Jan – 4 Feb 2018 HIGHLIGHTS Either for Rarity Value, Excellent Views Or Simply a Group Favorite
    YUCATAN, MEXICO - 2018 th th 27 Jan – 4 Feb 2018 HIGHLIGHTS Either for rarity value, excellent views or simply a group favorite. Yucatan Wren Ocellated Turkey Bare-throated Tiger Heron Lesser Roadrunner Yucatan Bobwhite American Flamingo Mexican Sheartail Gray-throated Chat Buff-bellied Hummingbird Rose-throated Tanager Black Catbird Black-headed Trogon White-bellied Emerald White-bellied Wren Lesson’s Motmot Eye-ringed Flatbill Blue Bunting Pale-billed Woodpecker Keel-billed Toucan Bat Falcon White-necked Puffbird Laughing Falcon Collared Aracari Tawny-winged Woodcreeper Cozumel Emerald Cozumel Vireo Yellow-tailed Oriole Ruddy Crake Yucatan Woodpecker Turquoise-browed Motmot Yucatan Jay Couch’s Kingbird Rufous-tailed Jacamar King Vulture Green Jay Velasquez’s Woodpecker Leaders: Rose-throated Steve Bird, Becard Gina Nichol Black Skimmers Yellow-throated Warbler Bright-rumped Attila “Golden” Warbler Magnificent Frigatebirds Vermilion Flycatcher Yucatan Vireo Red-legged Honeycreepers Ferruginous Pygmy-Owl Morelet’s Crocodile Yucatan Black Howler SUMMARY: Our winter getaway to the Yucatan in Mexico enjoyed some lovely warm, not too hot weather and some fabulous birds. The dinners and picnic lunches were excellent and our two superb drivers helped things run smoothly. Our local guide knew many of the key birding spots and we soon racked up a great list of sought after species. One of the real highlights was going out on a boat trip from Rio Lagartos where we enjoyed superb views of many water birds, including American Flamingos, Reddish Egrets darting around, terns, pelicans, a Morelet’s Crocodile and even Common Black Hawks sat around looking for a hand out. The dry thorny scrub produced many more species and a special treat was visiting Muyil Ruins where we not only enjoyed some excellent archaeology but also some great wildlife which including 6 Ocellated Turkeys, many other nice birds and an amazing experience with the loudest Yucatan Black Howler monkey in existence.
    [Show full text]
  • Mapping of Africa's Mangrove Forest Extent, Height and Biomass With
    1 Height and biomass of mangroves in Africa from ICEsat/GLAS and 2 SRTM 3 4 TEMILOLA E. FATOYINBO*†, MARC SIMARD‡, 5 6 †NASA Goddard Space Flight Center, 8800 Greenbelt Road, Mail Code 618, 7 Greenbelt, MD 20771,USA 8 9 ‡ NASA Jet Propulsion Laboratory, 4800 Oak Grove Drive, MS 300-235E, Pasadena, 10 CA, USA 11 12 Abstract 13 14 The accurate quantification of forest 3-D structure is of great importance for studies of the 15 global carbon cycle and biodiversity. These studies are especially relevant in Africa, where 16 deforestation rates are high and the lack of background data is great. Mangrove forests are 17 ecologically significant and it is important to measure mangrove canopy heights and biomass. 18 The objectives of this study are to estimate: 1. The total area, 2. Canopy height distributions and 19 3. Aboveground biomass of mangrove forests in Africa. To derive mangrove 3-D structure and 20 biomass maps, we used a combination of mangrove maps derived from Landsat ETM+, LiDAR 21 canopy height estimates from ICEsat/GLAS (Ice, Cloud, and land Elevation Satellite/Geoscience 22 Laser Altimeter System) and elevation data from SRTM (Shuttle Radar Topography Mission) for 23 the African continent. More specifically, we extracted mangrove forest areas on the SRTM DEM 24 using Landsat based landcover maps. The LiDAR (Light Detection and Ranging) measurements 25 from the large footprint GLAS sensor were used to derive local estimates of canopy height and 26 calibrate the Interferometric Synthetic Aperture Radar (InSAR) data from SRTM. We then 27 applied allometric equations relating canopy height to biomass in order to estimate above ground 28 biomass (AGB) from the canopy height product.
    [Show full text]
  • Chapter 4. Africa
    15 Chapter 4 Africa VEGETATION AND SPECIES COMPOSITION Mangroves are found in almost all countries along the west and east coasts of Africa, spreading from Mauritania to Angola on the west coast, and from Egypt to South Africa on the east coast, including Madagascar and several other islands. They are absent from Namibia, probably due to the semi-arid, desert-like climate, with low and irregular rainfall, a lack of warming currents and of favourable topographical features. Forest structure and species composition differ significantly from one coast to the other, as is described in the following paragraphs. On the east coast they generally form narrow fringe communities along the shores or small patches in estuaries, along seasonal creeks or in lagoons. The trees do not usually grow to more than 10 m in height, with a minimum height of 0.7–2 m in the Sudan and 1–2 m in South Africa. Madagascar (especially the northwest region), Mozambique and the United Republic of Tanzania represent the few exceptions: the extensive deltas and estuaries found in these countries allow the development of well- extended communities, with tree heights reaching 25–30 m. The Messalo and Zambezi river deltas (Mozambique) are home to some of the most extensive mangrove forests in the region. On the west coast well-developed mangroves are often found in large river deltas, in lagoons, along sheltered coastlines and on tidal flats. These forests may extend several kilometres inland, as happens in the Gambia and Guinea-Bissau, where major forests are found even 100–160 km upstream (e.g.
    [Show full text]
  • Rotenberg, J. A. Et Al. P 493-507
    Proceedings of the Fourth International Partners in Flight Conference: Tundra to Tropics 493–507 AN INTEGRATED COMMUNITY-BASED HARPY EAGLE AND AVIAN CONSERVATION PROGRAM FOR THE MAYA MOUNTAINS MASSIF, BELIZE JAMES A. ROTENBERG,1,4 JACOB MARLIN,2 SAM MEACHAM,3 AND SHARNA TOLFREE2 1Department of Environmental Studies, University of North Carolina Wilmington, Wilmington, North Carolina, USA; 2Belize Foundation for Research and Environmental Education (BFREE), P.O. Box 129, Punta Gorda, Belize; and 3El Centro Investigador del Sistema Aquífero de Quintana Roo (CINDAQ), Retorno Copan Lote 85, Manzana 22, Playacar Fase 2, Playa del Carmen, Quintana Roo, Mexico 77710 Abstract. Historically, research and monitoring of fl ora and fauna in the protected areas of the Maya Mountains Massif (MMM) of Belize have been conducted primarily by foreign scientists. This is par- ticularly true in areas such as the Bladen Nature Reserve (BNR) where its strict category of protection prevents even tourism as a means of alternative livelihoods for locals. Past studies have had little to no direct benefi ts (economic or educational) to buffer zone villages that border the BNR. What benefi ts that have been received are short-term in nature, and have had a strong negative impact on the local population’s appreciation of the protected areas themselves. Locals perceive the parks as a benefi t only for non-Belizeans. Our goal is to build capacity for avian conservation in the Maya Mountains by enhancing the links between protected areas and their surrounding communities. To achieve this goal, our project begins with a community-based alternative livelihood strengthening program for the development of a core group of avian technicians from buffer zone villages, and provides the tools for the acquisition of science based skills related to their work as parabiologists.
    [Show full text]
  • Running Head 'Biology of Mangroves'
    BIOLOGY OF MANGROVES AND MANGROVE ECOSYSTEMS 1 Biology of Mangroves and Mangrove Ecosystems ADVANCES IN MARINE BIOLOGY VOL 40: 81-251 (2001) K. Kathiresan1 and B.L. Bingham2 1Centre of Advanced Study in Marine Biology, Annamalai University, Parangipettai 608 502, India 2Huxley College of Environmental Studies, Western Washington University, Bellingham, WA 98225, USA e-mail [email protected] (correponding author) 1. Introduction.............................................................................................. 4 1.1. Preface........................................................................................ 4 1.2. Definition ................................................................................... 5 1.3. Global distribution ..................................................................... 5 2. History and Evolution ............................................................................. 10 2.1. Historical background ................................................................ 10 2.2. Evolution.................................................................................... 11 3. Biology of mangroves 3.1. Taxonomy and genetics.............................................................. 12 3.2. Anatomy..................................................................................... 15 3.3. Physiology ................................................................................. 18 3.4. Biochemistry ............................................................................. 20 3.5. Pollination
    [Show full text]
  • Evaluación Vireo Providencia .Pdf (1.842Mb)
    Facultad de Ingenieria y Ciencias Acta de Correcciones al Proyecto de Grado Biología Fecha: 31 de marzo de 2021 Autores: Jessica Paola Burbano Hernandez Nombre del Proyecto de Grado: Evaluación del estatus taxonómico del Vireo de Providencia (Vireo crassirostris approximans). Director: Felipe Estela Como indica el artículo 2.27 de las Directrices de Trabajo de Grado, he verificado que los estudiantes indicados arriba han implementado todas las correcciones que los Jurados del Proyecto de Grado definieron que se efectuaran, como consta en el Acta de Calificación correspondiente. ________________________________________ Firma del Director del Proyecto de Grado Nota de Aceptación Aprobado por el Comité de Trabajo de Grado en cumplimiento de los requisitos exigidos por la Pontificia Universidad Javeriana para optar el título de Biólogo. _______________________________________ Dr. HERNAN CAMILO ROCHA NIÑO Decano Facultad de Ingeniería ___________________________________ DR. MATEO LOPEZ VICTORIA Director Carrera Biología ___________________________________ Felipe Estela Director Trabajo de Grado ______________________________ ______________________________ Luis Eduardo Tobón Noemi Moreno Jurado 1 Jurado 2 Santiago de Cali, 8 de marzo de 2021 Mateo Lopez Victoria, Dr rer nat. Director programa de Biología Pontificia Universidad Javeriana Cali Cordial saludo, Por medio de la presente certifico que el trabajo de grado titulado “EVALUACIÓN DEL ESTATUS TAXONÓMICO DEL VIREO DE PROVIDENCIA (Vireo crassirostris apporximans)” realizado por la estudiante Jessica Paola Burbano Hernandez con el código de estudiante 8924351, estudiante de la carrera de Biología de la Facultad de Ingeniería y Ciencias de la Pontificia Universidad Javeriana Cali, se encuentra terminado y puede ser presentado para sustentación Atentamente, ____________________________ Felipe Estela Profesor Departamento de Ciencias Naturales y Matemáticas Facultad de Ingeniería y Ciencias Pontificia Universidad Javeriana Cali Santiago de Cali, 8 de marzo de 2021 Mateo Lopez Victoria, Dr rer nat.
    [Show full text]