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Distribution, Natural History and Conservation Status of Two
Bird Conservation International (2008) 18:331–348. ª BirdLife International 2008 doi:10.1017/S0959270908007491 Printed in the United Kingdom Distribution, natural history and conservation status of two endemics of the Bolivian Yungas, Bolivian Recurvebill Simoxenops striatus and Yungas Antwren Myrmotherula grisea SEBASTIAN K. HERZOG, A. BENNETT HENNESSEY, MICHAEL KESSLER and VI´CTOR H. GARCI´A-SOLI´Z Summary Since their description in the first half of the 20th century by M. A. Carriker, Bolivian Recurvebill Simoxenops striatus and Yungas Antwren Myrmotherula grisea have been regarded as extremely poorly known endemics of the Bolivian Yungas and adjacent humid foothill forests. They are considered ‘Vulnerable’ under the IUCN criteria of small population, predicted population decline (criterion C2a) and, in the case of Bolivian Recurvebill, small extent of occurrence (criteria B1a+b). Here we summarise the information published to date and present extensive new data on the distribution (including the first records for extreme southeast Peru), natural history, population size and conservation status of both species based on field work in the Bolivian Andes over the past 12 years. Both species primarily inhabit the understorey of primary and mid-aged to older regenerating forest and regularly join mixed-species foraging flocks of insectivorous birds. Bolivian Recurvebill has a strong preference for Guadua bamboo, but it is not an obligate bamboo specialist and persists at often much lower densities in forests without Guadua. Yungas Antwren seems to have a preference for dense, structurally complex under- storey, often with Chusquea bamboo. Both species are distributed much more continuously at altitudes of mostly 600–1,500 m, occupy a greater variety of forest types (wet, humid, semi- deciduous forest) and have a much greater population size than previously thought. -
Northeast Brazil Supreme Tour 28 Days
(Ceará, Bahia, Alagoas, Pernambuco, Sergipe, Tocantins, Goiás, Minas Gerais) Guide: To Be Defined… Day Location (state) Comments 1 Fortaleza – Icapuí (200Km) Arrival and transfer. 2 Icapuí – Quixadá (240Km) AM Birding and transfer 3 Quixadá – Guaramiranga (120Km) AM Birding. Transfer. PM Birding. 4 Guaramiranga – Sobral (250Km) AM Birding. Transfer. PM Birding. 5 Sobral – Potengi (520Km) AM Birding and transfer. 6 Potengi – Crato – Canudos (430Km) Transfer. AM Birding. Transfer. 7 Canudos – União dos Palmares (500Km) AM Birding and transfer. 8 Murici Full Day Birding. 9 U. Palmares – Jaqueira - Tamandaré (200Km) AM Birding. Transfer. PM Birding. 10 Tamandaré – Estância (500Km) Transfer and PM Birding. 11 Estância – Lençóis (540Km) AM Birding and transfer. 12 Chapada Diamantina Full Day Birding. 13 Lençóis – Barreiras (470KmKm) AM Birding and transfer. 14 Barreiras – São Desidério – Palmas (580Km) AM Birding and transfer. 15 Palmas – Miranorte – Pium (300Km) AM Birding and transfer. 16 Canguçu Research Center (Pium) Full Day Birding. 17 Pium – São Domingos (700Km) Transfer and PM Birding. 18 São Domingos – Januária (600Km) AM Birding and transfer. 19 Januária – Botumirim (370Km) AM Birding and transfer. 20 Botumirim Full Day Birding. 21 Botumirim – Boa Nova (600Km) Transfer and PM Birding. 22 Boa Nova Full Day Birding. 23 Boa Nova – Itacaré (200Km) AM Birding and transfer. 24 Itacaré – Camacan (200Km) AM Birding and transfer. 25 Serra Bonita Reserve (Camacan) Full Day Birding. 26 Camacan – Porto Seguro (220Km) AM Birding and transfer. 27 Porto Seguro Full Day Birding. 28 Departure Departure Suggested period: From September to January Fortaleza (A), Icapuí (B), Quixadá (C) Guaramiranga (D), Sobral (E), Potengi (F), Crato (G), Canudos (H), União dos Palmares (I), Tamandaré (J), Estância (K), Lençóis (L), Barreiras (M), São Desidério (N), Palmas (O), Miranorte (P), Pium (Q), São Domingos (R), Januária (S), Botumirim (T), Boa Nova (U), Itacaré (V) , Camacan (W), Porto Seguro (X). -
Bird Ecology, Conservation, and Community Responses
BIRD ECOLOGY, CONSERVATION, AND COMMUNITY RESPONSES TO LOGGING IN THE NORTHERN PERUVIAN AMAZON by NICO SUZANNE DAUPHINÉ (Under the Direction of Robert J. Cooper) ABSTRACT Understanding the responses of wildlife communities to logging and other human impacts in tropical forests is critical to the conservation of global biodiversity. I examined understory forest bird community responses to different intensities of non-mechanized commercial logging in two areas of the northern Peruvian Amazon: white-sand forest in the Allpahuayo-Mishana Reserve, and humid tropical forest in the Cordillera de Colán. I quantified vegetation structure using a modified circular plot method. I sampled birds using mist nets at a total of 21 lowland forest stands, comparing birds in logged forests 1, 5, and 9 years postharvest with those in unlogged forests using a sample effort of 4439 net-hours. I assumed not all species were detected and used sampling data to generate estimates of bird species richness and local extinction and turnover probabilities. During the course of fieldwork, I also made a preliminary inventory of birds in the northwest Cordillera de Colán and incidental observations of new nest and distributional records as well as threats and conservation measures for birds in the region. In both study areas, canopy cover was significantly higher in unlogged forest stands compared to logged forest stands. In Allpahuayo-Mishana, estimated bird species richness was highest in unlogged forest and lowest in forest regenerating 1-2 years post-logging. An estimated 24-80% of bird species in unlogged forest were absent from logged forest stands between 1 and 10 years postharvest. -
Bird List Column A: 1 = 70-90% Chance Column B: 2 = 30-70% Chance Column C: 3 = 10-30% Chance
Colombia: Chocó Prospective Bird List Column A: 1 = 70-90% chance Column B: 2 = 30-70% chance Column C: 3 = 10-30% chance A B C Tawny-breasted Tinamou 2 Nothocercus julius Highland Tinamou 3 Nothocercus bonapartei Great Tinamou 2 Tinamus major Berlepsch's Tinamou 3 Crypturellus berlepschi Little Tinamou 1 Crypturellus soui Choco Tinamou 3 Crypturellus kerriae Horned Screamer 2 Anhima cornuta Black-bellied Whistling-Duck 1 Dendrocygna autumnalis Fulvous Whistling-Duck 1 Dendrocygna bicolor Comb Duck 3 Sarkidiornis melanotos Muscovy Duck 3 Cairina moschata Torrent Duck 3 Merganetta armata Blue-winged Teal 3 Spatula discors Cinnamon Teal 2 Spatula cyanoptera Masked Duck 3 Nomonyx dominicus Gray-headed Chachalaca 1 Ortalis cinereiceps Colombian Chachalaca 1 Ortalis columbiana Baudo Guan 2 Penelope ortoni Crested Guan 3 Penelope purpurascens Cauca Guan 2 Penelope perspicax Wattled Guan 2 Aburria aburri Sickle-winged Guan 1 Chamaepetes goudotii Great Curassow 3 Crax rubra Tawny-faced Quail 3 Rhynchortyx cinctus Crested Bobwhite 2 Colinus cristatus Rufous-fronted Wood-Quail 2 Odontophorus erythrops Chestnut Wood-Quail 1 Odontophorus hyperythrus Least Grebe 2 Tachybaptus dominicus Pied-billed Grebe 1 Podilymbus podiceps Magnificent Frigatebird 1 Fregata magnificens Brown Booby 2 Sula leucogaster ________________________________________________________________________________________________________ WINGS ● 1643 N. Alvernon Way Ste. 109 ● Tucson ● AZ ● 85712 ● www.wingsbirds.com (866) 547 9868 Toll free US + Canada ● Tel (520) 320-9868 ● Fax (520) -
Juvenile Resilience and Adult Longevity Explain Residual Populations of the Andean Wax Palm Ceroxylon Quindiuense After Deforestation
Juvenile Resilience and Adult Longevity Explain Residual Populations of the Andean Wax Palm Ceroxylon quindiuense after Deforestation María José Sanín1*, Fabien Anthelme2,3, Jean-Christophe Pintaud3, Gloria Galeano1, Rodrigo Bernal1 1 Instituto de Ciencias Naturales, Universidad Nacional de Colombia, Bogotá, Distrito Capital, Colombia, 2 Botanique et Bioinformatique de l’Architecture des Plantes, Recherche Agronomique pour Le Développement, Institut de recherche pour le développement, Montpellier, Hérault, France, 3 Botanique et Bioinformatique de l’Architecture des Plantes and Diversité Adaptation et Développement des plantes, Institut de recherche pour le développement, Montpellier, Hérault, France Abstract Wax palms are an important element of the cloud forests in the tropical Andes. Despite heavy deforestation, the density of adults seems to be similar in deforested pastures as in forests. We aimed to infer the mechanisms responsible for this apparent resilience in pastures and we tested two hypotheses to explain it: 1) adult palms survived in pastures because they were spared from logging, and 2) adults occurred in pastures through the resilience of large juvenile rosettes, which survived through subterranean meristems and later developed into adults. For this purpose, we characterized the demographic structure of C. quindiuense in a total of 122 plots of 400 m2 in forests and pastures at two sites with contrasted land use histories in Colombia and Peru. Additionally, we implemented growth models that allowed us to estimate the age of individuals at four sites. These data were combined with information collected from local land managers in order to complete our knowledge on the land use history at each site. At two sites, the presence of old individuals up to 169 years and a wide age range evidenced that, at least, a portion of current adults in pastures were spared from logging at the time of deforestation. -
Publication Information
PUBLICATION INFORMATION This is the author’s version of a work that was accepted for publication in the Oryx journal. Changes resulting from the publishing process, such as peer review, editing, corrections, structural formatting, and other quality control mechanisms may not be reflected in this document. Changes may have been made to this work since it was submitted for publication. A definitive version was subsequently published in http://dx.doi.org/10.1017/S0030605315001118. Digital reproduction on this site is provided to CIFOR staff and other researchers who visit this site for research consultation and scholarly purposes. Further distribution and/or any further use of the works from this site is strictly forbidden without the permission of the Oryx journal. You may download, copy and distribute this manuscript for non-commercial purposes. Your license is limited by the following restrictions: 1. The integrity of the work and identification of the author, copyright owner and publisher must be preserved in any copy. 2. You must attribute this manuscript in the following format: This is an accepted version of an article by Nathalie Van Vliet, Maria Quiceno, Jessica Moreno, Daniel Cruz, John E. Fa And Robert Nasi. 2016. Is urban bushmeat trade in Colombia really insignificant?. Oryx. DOI http://dx.doi.org/10.1017/S0030605315001118 Accepted Oryx Urban bushmeat trade in different ecoregions in Colombia NATHALIE VAN VLIET, MARIA QUICENO, JESSICA MORENO, DANIEL CRUZ, JOHN E. FA and ROBERT NASI NATHALIE VAN VLIET (corresponding author), and ROBERT NASI, Center for International Forestry Research (CIFOR), CIFOR Headquarters, Bogor 16115, Indonesia E-mail [email protected] JOHN E. -
REGUA Bird List July 2020.Xlsx
Birds of REGUA/Aves da REGUA Updated July 2020. The taxonomy and nomenclature follows the Comitê Brasileiro de Registros Ornitológicos (CBRO), Annotated checklist of the birds of Brazil by the Brazilian Ornithological Records Committee, updated June 2015 - based on the checklist of the South American Classification Committee (SACC). Atualizado julho de 2020. A taxonomia e nomenclatura seguem o Comitê Brasileiro de Registros Ornitológicos (CBRO), Lista anotada das aves do Brasil pelo Comitê Brasileiro de Registros Ornitológicos, atualizada em junho de 2015 - fundamentada na lista do Comitê de Classificação da América do Sul (SACC). -
Diversity and Population Genetic Structure of the Wax Palm Ceroxylon
bioRxiv preprint doi: https://doi.org/10.1101/443960; this version posted October 15, 2018. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY 4.0 International license. 1 Diversity and population genetic structure of the wax palm 2 Ceroxylon quindiuense in the Colombian Coffee Region 3 Natalia González-Rivillas1-2, Adriana Bohórquez3, Janeth Patricia Gutierrez3, Víctor Hugo García- 4 Merchán1-2 5 6 1Grupo de Investigación en Evolución, Ecología y Conservación (EECO), Programa de Biología, 7 Universidad del Quindío, Carrera 15 Calle 12 Norte, Armenia, Quindío, Colombia. 8 2 Grupo de Investigación y Asesoría en Estadística, Universidad del Quindío. 9 3 International Center for Tropical Agriculture (CIAT), Km 17, recta Cali-Palmira, Colombia. 10 11 [email protected] (NGR), [email protected] (AB), [email protected] (JPG) & 12 [email protected] (VHGM). 13 14 The authors mentioned contributed equally to this work. 15 16 Abstract 17 The wax palm from Quindío (Ceroxylon quindiuense) is an icon of the cultural identity of the coffee growing 18 eco-region and of all Colombia. Processes of urbanization, expansion of the agricultural and livestock area, among 19 others, have increased its level of threat. Protecting this palm from extinction is important at an ecological level, given 20 its function as a key species in Andean ecosystems. This work evaluated the diversity and population genetic structure 21 of the wax palm from Quindío in five populations of the Colombian coffee region eco-region (Andean zone) by using 22 ten microsatellite molecular markers. -
Reference File
References added since publication of 2007 CRC Handbook of Avian Body Masses Abadie, K. B., J. Pérez Z., and M. Valverde. 2006. Primer reporte de colonias del Martín Peruano Progne murphyi. Cotinga 24:99-101. Ackerman, J. T., J. Y. Takekawa, J. D. Bluso, J. L. Yee, and C. A. Eagles-Smith. 2008. Gender identification of Caspian Terns using external morphology and discriminant function analysis. Wilson Journal of Ornithology 120:378-383. Alarcos, S., C. de la Cruz, E. Solís, J. Valencia, and M. J. García-Baquero. 2007. Sex determination of Iberian Azure-winged Magpies Cyanopica cyanus cooki by discriminant analysis of external measurements. Ringing & Migration 23:211-216. Albayrak, T., A. Besnard, and A. Erdoğan. 2011. Morphometric variation and population relationships of Krüeper’s Nuthatch (Sitta krueperi) in Turkey. Wilson Journal of Ornithology 123:734-740. Aleixo, A., C. E. B. Portes, A. Whittaker, J. D. Weckstein, L. Pedreira Gonzaga, K. J. Zimmer, C. C. Ribas, and J. M. Bates. 2013. Molecular systematics and taxonomic revision of the Curve-billed Scythebill complex (Campylorhamphus procurvoides: Dendrocolaptidae), with description of a new species from western Amazonian Brazil. Pp. 253-257, In: del Hoyo, J., A Elliott, J. Sargatal, and D.A. Christie (eds). Handbook of the birds of the world. Special volume: new species and global index. Lynx Edicions, Barcelona, Spain. Volume 1. Alfano, A. 2014. Pygmy Nightjar (Nyctopolus hirundinaeus). Neotropical Birds Online (T.S. Schulenberg, ed.). Cornell Laboratory of Ornithology, Ithaca, NY. Alvarenga, H. M. F., E. Höfling, and L. F. Silveira. 2002. Notharchus swainsoni (Gray, 1846) é uma espécie válida. -
Predation of Birds Trapped in Mist Nets by Raptors in the Brazilian Caatinga
Predation of Birds Trapped in Mist Nets by Raptors in the Brazilian Caatinga 1 2 5 Juan Ruiz-Esparza • • Resumen: 1 3 Patricio Adriano da Rocha • La red de neb/ina es una tecnica de captura de Adauto de Souza Ribeiro4 vertebrados voladores como aves y murcielagos. Una Stephen F. Ferrari4 vez capturados e inmovilizados, los animates son 1 Graduate Program in Ecology and Conservation, vulnerables a ataques par predadores hasta su extracci6n. Ataques de animates atrapados han sido Universidade Federal de Sergipe, Avenida registrados en diferentes lugares, aunque los datos son Marechal Rondon s/n, 49.100-000 Sao poco sistematicos, tales como clasificaci6n de la Crist6vao - Sergipe, Brazil. depredaci6n estrin disponibles. Analizamos ataques 2 PR D MA , Universidade Federal de Sergipe, contra las aves capturadas en redes de neblina en la Av. Marechal Rondon s/n, 49.100-000 Caatinga y regiones aledafias en el nordeste de Brasil. Sao Crist6vao-Sergipe, Brazil. Un total de 979 aves fueron capturadas durante 6, 000 horas-red de muestreo, donde 18 (1, 8%) fueron 3 Graduate Program in Zoot gy, U n:i versidade encontradas muertas en Ia red de neblina con senates de Federal da Paraiba, Joao Pessoa-Paraiba, Brazil. Ia depredaci6n. En Ia mayoria de los casas no fue posible identificar el predador, un Gavilan de los 4 Department of Biology, Unjversidade Fed ral d Caminos (Rupomis magnirostris) fue capturado junto S r0 ipe, A venida Marechal Rondon con un Chivi Amarillento (Basileuterus flaveolus) /n 49.100-000 Sao Crist6vao- Sergipe Brazil. depredado, heridas simi/ares fueron observadas en las 5 orresponding author; e-maiJ: otras aves, sugiriendo que rapaces pudieron haber sido juanco lorad 2 1@ h tmail.com responsables par los otros ataques. -
COLOMBIA 2019 Ned Brinkley Departments of Vaupés, Chocó, Risaralda, Santander, Antioquia, Magdalena, Tolima, Atlántico, La Gu
COLOMBIA 2019 Ned Brinkley Departments of Vaupés, Chocó, Risaralda, Santander, Antioquia, Magdalena, Tolima, Atlántico, La Guajira, Boyacá, Distrito Capital de Bogotá, Caldas These comments are provided to help independent birders traveling in Colombia, particularly people who want to drive themselves to birding sites rather than taking public transportation and also want to book reservations directly with lodgings and reserves rather than using a ground agent or tour company. Many trip reports provide GPS waypoints for navigation. I used GoogleEarth/ Maps, which worked fine for most locations (not for El Paujil reserve). I paid $10/day for AT&T to hook me up to Claro, Movistar, or Tigo through their Passport program. Others get a local SIM card so that they have a Colombian number (cheaper, for sure); still others use GooglePhones, which provide connection through other providers with better or worse success, depending on the location in Colombia. For transportation, I used a rental 4x4 SUV to reach places with bad roads but also, in northern Colombia, a subcompact rental car as far as Minca (hiked in higher elevations, with one moto-taxi to reach El Dorado lodge) and for La Guajira. I used regular taxis on few occasions. The only roads to sites for Fuertes’s Parrot and Yellow-eared Parrot could not have been traversed without four-wheel drive and high clearance, and this is important to emphasize: vehicles without these attributes would have been useless, or become damaged or stranded. Note that large cities in Colombia (at least Medellín, Santa Marta, and Cartagena) have restrictions on driving during rush hours with certain license plate numbers (they base restrictions on the plate’s final numeral). -
Federal Register/Vol. 81, No. 200/Monday, October 17, 2016
Federal Register / Vol. 81, No. 200 / Monday, October 17, 2016 / Proposed Rules 71457 for the relevant maintenance period in attainment of the 2008 ozone NAAQS Technology Transfer and Advancement with mobile source emissions at the through 2030. Finally, EPA finds Act of 1995 (15 U.S.C. 272 note) because levels of the MVEBs. adequate and is proposing to approve application of those requirements would the newly-established 2020 and 2030 be inconsistent with the CAA; and C. What is a safety margin? MVEBs for the Cleveland area. • Does not provide EPA with the A ‘‘safety margin’’ is the difference discretionary authority to address, as VII. Statutory and Executive Order between the attainment level of appropriate, disproportionate human Reviews emissions (from all sources) and the health or environmental effects, using projected level of emissions (from all Under the CAA, redesignation of an practicable and legally permissible sources) in the maintenance plan. As area to attainment and the methods, under Executive Order 12898 noted in Table 11, the emissions in the accompanying approval of a (59 FR 7629, February 16, 1994). Cleveland area are projected to have maintenance plan under section In addition, the SIP is not approved safety margins of 117.22 TPSD for NOX 107(d)(3)(E) are actions that affect the to apply on any Indian reservation land and 28.48 TPSD for VOC in 2030 (the status of a geographical area and do not or in any other area where EPA or an total net change between the attainment impose any additional regulatory Indian tribe has demonstrated that a year, 2014, emissions and the projected requirements on sources beyond those tribe has jurisdiction.