2018 De Brazza Monkey EAZA Best Practice Guidelines Approved
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Arxiv:2101.10390V1 [Cs.LG] 25 Jan 2021 Terms of Quality, Increasing the Comparability and Reproducibil- Conservation and Education Initiatives
Introducing a Central African Primate Vocalisation Dataset for Automated Species Classification Joeri A. Zwerts1, Jelle Treep2, Casper S. Kaandorp2, Floor Meewis1, Amparo C. Koot1, Heysem Kaya3 1 Department of Biology, Utrecht University, Utrecht, The Netherlands 2 Information and Technology Services, Utrecht University, Utrecht, The Netherlands 3 Department of Information and Computing Sciences, Utrecht University, Utrecht, The Netherlands [email protected], [email protected] Abstract classifier capable of detecting species in the wild. This may also provide insights into whether this approach, of using sanctuary Automated classification of animal vocalisations is a poten- recordings, can be used to train classifiers for other species as tially powerful wildlife monitoring tool. Training robust clas- well, to aid in the development of cost-effective monitoring to sifiers requires sizable annotated datasets, which are not eas- meet modern conservation challenges. ily recorded in the wild. To circumvent this problem, we In this paper, we present the dataset, the semi-automatic an- recorded four primate species under semi-natural conditions in notation process that we used to speed up the manual annotation a wildlife sanctuary in Cameroon with the objective to train a process, and a benchmark species classification system. classifier capable of detecting species in the wild. Here, we introduce the collected dataset, describe our approach and ini- tial results of classifier development. To increase the efficiency 1.1. Related Work of the annotation process, we condensed the recordings with Multiple studies have applied automatic acoustic monitoring for an energy/change based automatic vocalisation detection. Seg- a variety of taxa including cetaceans [4], birds [5], bats [6], menting the annotated chunks into training, validation and test insects [7], amphibians [8], and forest elephants [9]. -
Pest Risk Assessment
PEST RISK ASSESSMENT De Brazza‟s Monkey Cercopithecus neglectus Photo: Aaron Logan from Wikimedia Commons under the Creative Commons Attribution 1.0 Generic license June 2011 Department of Primary Industries, Parks, Water and Environment Resource Management and Conservation Division Department of Primary Industries, Parks, Water and Environment 2011 Information in this publication may be reproduced provided that any extracts are acknowledged. This publication should be cited as: DPIPWE (2011) Pest Risk Assessment: De Brazza’s Monkey (Cercopithecus neglectus). Department of Primary Industries, Parks, Water and Environment. Hobart, Tasmania. About this Pest Risk Assessment This pest risk assessment is developed in accordance with the Policy and Procedures for the Import, Movement and Keeping of Vertebrate Wildlife in Tasmania (DPIPWE 2011). The policy and procedures set out conditions and restrictions for the importation of mammals, birds, reptiles and amphibians pursuant to s32 of the Nature Conservation Act 2002. This pest risk assessment is prepared by DPIPWE for the use within the Department. For more information about this Pest Risk Assessment, please contact: Wildlife Management Branch Department of Primary Industries, Parks, Water and Environment Address: GPO Box 44, Hobart, TAS. 7001, Australia. Phone: 1300 386 550 Email: [email protected] Visit: www.dpipwe.tas.gov.au Disclaimer The information provided in this Pest Risk Assessment is provided in good faith. The Crown, its officers, employees and agents do not accept liability however arising, including liability for negligence, for any loss resulting from the use of or reliance upon the information in this Pest Risk Assessment and/or reliance on its availability at any time. -
World's Most Endangered Primates
Primates in Peril The World’s 25 Most Endangered Primates 2016–2018 Edited by Christoph Schwitzer, Russell A. Mittermeier, Anthony B. Rylands, Federica Chiozza, Elizabeth A. Williamson, Elizabeth J. Macfie, Janette Wallis and Alison Cotton Illustrations by Stephen D. Nash IUCN SSC Primate Specialist Group (PSG) International Primatological Society (IPS) Conservation International (CI) Bristol Zoological Society (BZS) Published by: IUCN SSC Primate Specialist Group (PSG), International Primatological Society (IPS), Conservation International (CI), Bristol Zoological Society (BZS) Copyright: ©2017 Conservation International All rights reserved. No part of this report may be reproduced in any form or by any means without permission in writing from the publisher. Inquiries to the publisher should be directed to the following address: Russell A. Mittermeier, Chair, IUCN SSC Primate Specialist Group, Conservation International, 2011 Crystal Drive, Suite 500, Arlington, VA 22202, USA. Citation (report): Schwitzer, C., Mittermeier, R.A., Rylands, A.B., Chiozza, F., Williamson, E.A., Macfie, E.J., Wallis, J. and Cotton, A. (eds.). 2017. Primates in Peril: The World’s 25 Most Endangered Primates 2016–2018. IUCN SSC Primate Specialist Group (PSG), International Primatological Society (IPS), Conservation International (CI), and Bristol Zoological Society, Arlington, VA. 99 pp. Citation (species): Salmona, J., Patel, E.R., Chikhi, L. and Banks, M.A. 2017. Propithecus perrieri (Lavauden, 1931). In: C. Schwitzer, R.A. Mittermeier, A.B. Rylands, F. Chiozza, E.A. Williamson, E.J. Macfie, J. Wallis and A. Cotton (eds.), Primates in Peril: The World’s 25 Most Endangered Primates 2016–2018, pp. 40-43. IUCN SSC Primate Specialist Group (PSG), International Primatological Society (IPS), Conservation International (CI), and Bristol Zoological Society, Arlington, VA. -
Mandrillus Leucophaeus Poensis)
Ecology and Behavior of the Bioko Island Drill (Mandrillus leucophaeus poensis) A Thesis Submitted to the Faculty of Drexel University by Jacob Robert Owens in partial fulfillment of the requirements for the degree of Doctor of Philosophy December 2013 i © Copyright 2013 Jacob Robert Owens. All Rights Reserved ii Dedications To my wife, Jen. iii Acknowledgments The research presented herein was made possible by the financial support provided by Primate Conservation Inc., ExxonMobil Foundation, Mobil Equatorial Guinea, Inc., Margo Marsh Biodiversity Fund, and the Los Angeles Zoo. I would also like to express my gratitude to Dr. Teck-Kah Lim and the Drexel University Office of Graduate Studies for the Dissertation Fellowship and the invaluable time it provided me during the writing process. I thank the Government of Equatorial Guinea, the Ministry of Fisheries and the Environment, Ministry of Information, Press, and Radio, and the Ministry of Culture and Tourism for the opportunity to work and live in one of the most beautiful and unique places in the world. I am grateful to the faculty and staff of the National University of Equatorial Guinea who helped me navigate the geographic and bureaucratic landscape of Bioko Island. I would especially like to thank Jose Manuel Esara Echube, Claudio Posa Bohome, Maximilliano Fero Meñe, Eusebio Ondo Nguema, and Mariano Obama Bibang. The journey to my Ph.D. has been considerably more taxing than I expected, and I would not have been able to complete it without the assistance of an expansive list of people. I would like to thank all of you who have helped me through this process, many of whom I lack the space to do so specifically here. -
The Consequences of Habitat Loss and Fragmentation on the Distribution, Population Size, Habitat Preferences, Feeding and Rangin
The consequences of habitat loss and fragmentation on the distribution, population size, habitat preferences, feeding and ranging Ecology of grivet monkey (Cercopithecus aethiopes aethiops) on the human dominated habitats of north Shoa, Amhara, Ethiopia: A Study of human-grivet monkey conflict 1 Table of contents Page 1. Introduction 1 1.1. Background And Justifications 3 1.2. Statement Of The Problem 6 1.3. Objectives 7 1.3.1. General Objective 7 1.3.2. Specific Objectives 8 1.4. Research Hypotheses Under Investigation 8 2. Description Of The Study Area 8 3. Methodology 11 3.1. Habitat Stratification, Vegetation Mapping And Land Use Cover 11 Change 3.2. Distribution Pattern And Population Estimate Of Grivet Monkey 11 3.3. Behavioral Data 12 3.4. Human Grivet Monkey Conflict 15 3.5. Habitat Loss And Fragmentation 15 4. Expected Output 16 5. Challenges Of The Project 16 6. References 17 i 1. Introduction World mammals status analysis on global scale shows that primates are the most threatened mammals (Schipper et al., 2008) making them indicators for investigating vulnerability to threats. Habitat loss and destruction are often considered to be the most serious threat to many tropical primate populations because of agricultural expansion, livestock grazing, logging, and human settlement (Cowlishaw and Dunbar, 2000). Deforestation and forest fragmentation have marched together with the expansion of agricultural frontiers, resulting in both habitat loss and subdivision of the remaining habitat (Michalski and Peres, 2005). This forest degradation results in reduction in size or fragmentation of the original forest habitat (Fahrig, 2003). Habitat fragmentation is often defined as a process during which “a large expanse of habitat is transformed into a number of smaller patches of smaller total area, isolated from each other by a matrix of habitats unlike the original”. -
Hunting Behavior of Wild Chimpanzees in the Taï National Park
AMERICAN JOURNAL OF PHYSICAL ANTHROPOLOGY 78547-573 (1989) Hunting Behavior of Wild Chimpanzees in the Tai’ National Park CHRISTOPHE BOESCH AND HEDWIGE BOESCH Department of Ethology and Wildlife Research, University of Zurich, CH-8057 Zurich, Switzerland KEY WORDS Cooperation, Sharing, Traditions ABSTRACT Hunting is often considered one of the major behaviors that shaped early hominids’ evolution, along with the shift toward a drier and more open habitat. We suggest that a precise comparison of the hunting behavior of a species closely related to man might help us understand which aspects of hunting could be affected by environmental conditions. The hunting behavior of wild chimpanzees is discussed, and new observations on a population living in the tropical rain forest of the TaY National Park, Ivory Coast, are presented. Some of the forest chimpanzees’ hunting performances are similar to those of savanna-woodlands populations; others are different. Forest chimpanzees have a more specialized prey image, intentionally search for more adult prey, and hunt in larger groups and with a more elaborate cooperative level than sa- vanna-woodlands chimpanzees. In addition, forest chimpanzees tend to share meat more actively and more frequently. These findings are related to some theories on aspects of hunting behavior in early hominids and discussed in order to understand some factors influencing the hunting behavior of wild chimpanzees. Finally, the hunting behavior of primates is compared with that of social carnivores. Hunting is generally -
Crop Raiding by Wild Vertebrates in the Illubabor Zone, Ethiopia
C rop Raiding by Wild Vertebrates in the Illubabor Zone, Ethiopia Courtney Quirin A report submitted in partial fulfilment of the Post-graduate Diploma in Wildlife Management University of Otago 2005 University of Otago Department of Zoology P.O. Box 56, Dunedin New Zealand WLM Report Number: 206 C rop Raiding by Wild Vertebrates in the Illubabor Zone, Ethiopia By Courtney Quirin May 4, 2005 2 Table of Contents Executive Summary . iii Acknowledgements . vii Table of Contents . i List of Tables . viii List of Figures. ix 1. Introduction. 1 2. Methods . 3 3. Results . 5 3.1 Farm Composition and Crop Loss . 6 3.2 Pest Profiles . .. 6 3.3 Dominant Foragers by Crop . 12 3.4 Dominant Foragers by Area . 15 3.5 Analysis of the Likelihood of Crop Loss. 16 3.6 Seasonal Calendars: Raiding Intensity, Animal Activity, and Human Cultivation Activity . 17 3.7 Guarding Strategies . .. 22 3.8 Predictions and Future Management Solutions . 26 4. Summary of Results . 27 4.1 Total crop loss by daytime and nighttime foragers . 27 4.2 Summary of Sites . 27 5. Discussion . 29 5.1 Research and Site Overview . 29 5.2 Top Four Pests and Ranking . 29 5.3 Habitat Restrictions and Social Behaviour of Pests . 31 3 5.4 Impact of Top Four Pests in Wetland and Upland Areas . 32 5.5 Dominant Foragers by Crop Type . 33 5.6 Guarding Strategies . 35 5.7 Raiding Intensity, Seasonal Animal Activity and Cultivation Activity. 39 5.8 Predictions and Future Management Solutions . 40 6. Conclusion . 42 7. References . 44 4 Executive Summary Investigation Title Crop Raiding by Wild Vertebrates in the Illubabor Zone, Ethiopia Study Sites Upland and wetland farming communities in the Wichi wetland catchment, Metu Wereda, Illubabor Zone, Ethiopia. -
A Rapid Assessment of Hunting and Bushmeat Trade Along the Roadside Between Five Angolan Major Towns
A peer-reviewed open-access journal Nature Conservation 37: 151–160Bushmeat (2019) trade assessment in five Angolan povinces 151 doi: 10.3897/natureconservation.37.37590 SHORT COMMUNICATION http://natureconservation.pensoft.net Launched to accelerate biodiversity conservation A rapid assessment of hunting and bushmeat trade along the roadside between five Angolan major towns Francisco M. P. Gonçalves1,2, José C. Luís1,3, José J. Tchamba1, Manuel J. Cachissapa1, António Valter Chisingui1 1 Herbário do Lubango, ISCED-Huíla, Rua Sarmento Rodrigues No. 2, C.P. 230 Lubango, Angola 2 Institute for Plant Science and Microbiology (BEE), University of Hamburg, Ohnhorststr. 22609 Hamburg, Germany 3 Instituto de Geografia e Ordenamento do Território, Universidade de Lisboa, Rua Branca Edmée Marques 1600-276 Lisboa, Portugal Corresponding author: Francisco M. P. Gonçalves ([email protected]) Academic editor: Mark Auliya | Received 21 June 2019 | Accepted 8 November 2019 | Published 16 December 2019 http://zoobank.org/E82010C2-5D52-4BA4-8605-36D453D78C51 Citation: Gonçalves FMP, Luís JC, Tchamba JJ, Cachissapa MJ, Chisingui AV (2019) A rapid assessment of hunting and bushmeat trade along the roadside between five Angolan major towns. Nature Conservation 37: 151–160.https://doi. org/10.3897/natureconservation.37.37590 Abstract Hunting and related bushmeat trade are activities which negatively impact wildlife worldwide, with serious implications for biodiversity conservation. Angola’s fauna was severely decimated during the long-lasting civil war following the country’s independence. During a round trip from Lubango (Huíla province), pass- ing through the provinces of Benguela, Cuanza sul, Luanda, Bengo and finally to Uíge, we documented a variety of bushmeat trade, mainly along the roadside. -
Emergence of Unique Primate T-Lymphotropic Viruses Among Central African Bushmeat Hunters
Emergence of unique primate T-lymphotropic viruses among central African bushmeat hunters Nathan D. Wolfe*†‡, Walid Heneine§, Jean K. Carr¶, Albert D. Garcia§, Vedapuri Shanmugam§, Ubald Tamoufe*ʈ, Judith N. Torimiroʈ, A. Tassy Prosser†, Matthew LeBretonʈ, Eitel Mpoudi-Ngoleʈ, Francine E. McCutchan*¶, Deborah L. Birx**, Thomas M. Folks§, Donald S. Burke*†, and William M. Switzer§†† Departments of *Epidemiology, †International Health, and ‡Molecular Microbiology and Immunology, Bloomberg School of Public Health, The Johns Hopkins University, Baltimore, MD 21205; §Laboratory Branch, Division of HIV͞AIDS Prevention, National Center for HIV, STD, and TB Prevention, Centers for Disease Control and Prevention, Atlanta, GA 30333; ¶Henry M. Jackson Foundation, Rockville, MD 20850; ʈArmy Health Research Center, Yaounde, Cameroon; and **Walter Reed Army Institute of Research, Rockville, MD 20850 Edited by John M. Coffin, Tufts University School of Medicine, Boston, and approved April 11, 2005 (received for review March 2, 2005) The human T-lymphotropic viruses (HTLVs) types 1 and 2 origi- There has been no evidence that STLVs cross into people nated independently and are related to distinct lineages of simian occupationally exposed to NHPs in laboratories and primate T-lymphotropic viruses (STLV-1 and STLV-2, respectively). These centers, as has been documented for other primate retroviruses, facts, along with the finding that HTLV-1 diversity appears to have including simian immunodeficiency virus, simian foamy virus resulted from multiple cross-species transmissions of STLV-1, sug- (SFV), and simian type D retrovirus (12–15). Nevertheless, gest that contact between humans and infected nonhuman pri- zoonotic transmission of STLV to human populations naturally mates (NHPs) may result in HTLV emergence. -
Widespread Treponema Pallidum Infection in Nonhuman Primates, Tanzania Idrissa S
RESEARCH Widespread Treponema pallidum Infection in Nonhuman Primates, Tanzania Idrissa S. Chuma, Emmanuel K. Batamuzi,1 D. Anthony Collins, Robert D. Fyumagwa, Luisa K. Hallmaier-Wacker, Rudovick R. Kazwala, Julius D. Keyyu, Inyasi A. Lejora, Iddi F. Lipende, Simone Lüert, Filipa M.D. Paciência, Alexander Piel, Fiona A. Stewart, Dietmar Zinner, Christian Roos, Sascha Knauf We investigated Treponema pallidum infection in 8 nonhu- S. Knauf et al., unpub. data, https://www.biorxiv.org/ man primate species (289 animals) in Tanzania during 2015– content/early/2017/05/10/135491) and thus make NHP in- 2017. We used a serologic treponemal test to detect anti- fection an important issue for a One Health approach. bodies against the bacterium. Infection was further confirmed The first published report of T. pallidum infection in from tissue samples of skin-ulcerated animals by 3 indepen- Tanzanian NHPs came from anogenital ulcerated olive dent PCRs (polA, tp47, and TP_0619). Our findings indicate baboons (Papio anubis) at Gombe National Park (GNP) that T. pallidum infection is geographically widespread in Tanzania and occurs in several species (olive baboons, yel- in the late 1980s (5), followed by cases reported from low baboons, vervet monkeys, and blue monkeys). We found olive baboons at Lake Manyara National Park (LMNP) the bacterium at 11 of 14 investigated geographic locations. (3,6,7) and Serengeti National Park (SNP) (3). Clinical Anogenital ulceration was the most common clinical manifes- manifestations of T. pallidum infection in NHPs ranged tation; orofacial lesions also were observed. Molecular data from asymptomatic to severe skin ulceration mainly af- show that nonhuman primates in Tanzania are most likely fecting the face or genitalia (8). -
From Monkeys to Humans: What Do We Now Know About Brain Homologies? Martin I Sereno and Roger BH Tootell
From monkeys to humans: what do we now know about brain homologies? Martin I Sereno and Roger BH Tootell Different primate species, including humans, have evolved by a most closely related to humans; thus, they are the natural repeated branching of lineages, some of which have become model system for humans. However, the last common extinct. The problem of determining the relationships among ancestor of humans and macaques dates back to more cortical areas within the brains of the surviving branches (e.g. than 30 million years ago [1]. Since that time, New and humans, macaque monkeys, owl monkeys) is difficult for Old World monkey brains have evolved independently several reasons. First, evolutionary intermediates are missing, from the brains of apes and humans, resulting in a com- second, measurement techniques are different in different plex mix of shared and unique features of the brain in primate species, third, species differ in body size, and fourth, each group [2]. brain areas can duplicate, fuse, or reorganize between and within lineages. Evolutionary biologists are often interested in shared derived characters — i.e. specializations that have Addresses diverged from a basal condition that are peculiar to a Department of Cognitive Sciences, University of California, species or grouping of species. Such divergent features San Diego, La Jolla, CA 92093-0515, USA are important for classification (e.g. a brain area that is Corresponding author: Sereno, MI ([email protected]) unique to macaque-like monkeys, but not found in any other primate group). Evolutionary biologists also distin- guish similarities caused by inheritance (homology), from Current Opinion in Neurobiology 2005, 15:135–144 similarities caused by parallel or convergent evolution (homoplasy — a similar feature that evolved in parallel in This review comes from a themed issue on Cognitive neuroscience two lineages, but that was not present in their last Edited by Angela D Friederici and Leslie G Ungerleider common ancestor). -
Ancestral Facial Morphology of Old World Higher Primates (Anthropoidea/Catarrhini/Miocene/Cranium/Anatomy) BRENDA R
Proc. Natl. Acad. Sci. USA Vol. 88, pp. 5267-5271, June 1991 Evolution Ancestral facial morphology of Old World higher primates (Anthropoidea/Catarrhini/Miocene/cranium/anatomy) BRENDA R. BENEFIT* AND MONTE L. MCCROSSINt *Department of Anthropology, Southern Illinois University, Carbondale, IL 62901; and tDepartment of Anthropology, University of California, Berkeley, CA 94720 Communicated by F. Clark Howell, March 11, 1991 ABSTRACT Fossil remains of the cercopithecoid Victoia- (1, 5, 6). Contrasting craniofacial configurations of cercopithe- pithecus recently recovered from middle Miocene deposits of cines and great apes are, in consequence, held to be indepen- Maboko Island (Kenya) provide evidence ofthe cranial anatomy dently derived with regard to the ancestral catarrhine condition of Old World monkeys prior to the evolutionary divergence of (1, 5, 6). This reconstruction has formed the basis of influential the extant subfamilies Colobinae and Cercopithecinae. Victoria- cladistic assessments ofthe phylogenetic relationships between pithecus shares a suite ofcraniofacial features with the Oligocene extant and extinct catarrhines (1, 2). catarrhine Aegyptopithecus and early Miocene hominoid Afro- Reconstructions of the ancestral catarrhine morphotype pithecus. AU three genera manifest supraorbital costae, anteri- are based on commonalities of subordinate morphotypes for orly convergent temporal lines, the absence of a postglabellar Cercopithecoidea and Hominoidea (1, 5, 6). Broadly distrib- fossa, a moderate to long snout, great facial