Seasonal Changes in Behavior and Exhibit Use of Captive African Elephants ( Loxodonta Africana ) and Black Rhinoceroses ( Diceros Bicornis )

Total Page:16

File Type:pdf, Size:1020Kb

Seasonal Changes in Behavior and Exhibit Use of Captive African Elephants ( Loxodonta Africana ) and Black Rhinoceroses ( Diceros Bicornis ) SEASONAL CHANGES IN BEHAVIOR AND EXHIBIT USE OF CAPTIVE AFRICAN ELEPHANTS ( LOXODONTA AFRICANA ) AND BLACK RHINOCEROSES ( DICEROS BICORNIS ) by JENNI ELIZABETH MUELLER Submitted in partial fulfillment of the requirements For the Degree of Master of Science Department of Biology CASE WESTERN RESERVE UNIVERSITY August, 2008 CASE WESTERN RESERVE UNIVERSITY SCHOOL OF GRADUATE STUDIES We hereby approve the thesis/dissertation of ____________________Jenni E. Mueller____________________ candidate for the _________Master of Science_________degree *. (signed)__________Julia Brown____________________________ (chair of the committee) __________Kristen E. Lukas_________________________ __________Mark A. Willis__________________________ __________Pam Dennis_____________________________ ________________________________________________ ________________________________________________ (date) ________June 26, 2008________ *We also certify that written approval has been obtained for any proprietary material contained therein. ii Table of Contents Page No. List of Tables…………………………………………………………………………….iv List of Figures…………………………………………………………………………....v Abstract………………………………………………………………………………….vi Introduction……………………………………………………………………………...1 Natural History of the Species …………………………………………………….4 Social Behavior …………………………………………………………………...13 African Elephants and Black Rhinoceroses in Captivity ………………………...17 Abnormal Behavior ………………………………………………………………22 The Current Study ………………………………………………………………27 Chapter 1 : The Behavior of Captive African Elephants and Black Rhinoceroses Introduction ……………………………………………………………………..29 Methods and Materials ………………………………………………………….31 Results …………………………………………………………………………...36 Discussion ……………………………………………………………………….44 Chapter 2 : Exhibit Use and Object Preferences of Captive African Elephants and Black Rhinoceroses Introduction ……………………………………………………………………...55 Methods and Mater ials………………………………………………………….57 Results …………………………………………………………………………...58 Discussion ……………………………………………………………………….66 Chapter 3 : Social Dynamics and Abnormal Behaviors in African Elephants and Black Rhinoceroses Housed at Cleveland Metroparks Zoo Introduction ……………………………………………………………………...83 Methods and Materials ………………………………………………………......86 Results …………………………………………………………………………...86 Discussion ………………………………………………………………………..94 Chapter 4 : Behavioral Changes Associated with Disease in a Captive Black Rhinoceros Introduction ………………………………………………………………….....110 Methods and Materials …………………………………………………………112 Results ………………………………………………………………………….114 Discussion ……………………………………………………………………....117 Conclusion…………………………………………………………………………….121 Appendices……………………………………………………………………………125 Works Cited…………………………………………………………………………...132 iii List of Tables Introduction Page No. 1: Captive Populations of African Elephant and Black Rhinoceros…………………………2 Chapter 1 1: African Elephants and Black Rhinoceroses at Cleveland Metroparks Zoo…………….32 2: Types and Examples of Enrichment Items Presented to Subjects……………………….32 3: Months Averaged to Calculate Seasonal Totals…………………………………………..36 Chapter 3 1: Individual Performances of Abnormal Behavior in African Elephants………………...90 2: Individual Performance of Abnormal Behavior in the Rhinos………………….............93 iv List of Figures Chapter 1 Page No. 1. Mean levels of activity and inactivity in African elephants and black rhinos…………37 2. Mean time performing active behaviors…………………………………………………...38 3. Mean resting behavior in relation to time of day…………………………………………39 4. Seasonal trends in mean locomotion……………………………………………………….39 5. Seasonal changes in mean investigatory and environmentally-oriented behaviors in African elephants……………………………………………………………………………….40 6. Temperature-related trends in dusting behavior in African elephants………………...41 7. Temperature-related trends in average resting behavior………………………………..41 8. Mean time spent in social proximity……………………………………………………….42 9. Mean occurrence of social interactions in each enclosure in the elephants (A) and rhinos (B)………………………………………………………………………………………...43 Chapter 2 1. Changes in behavior in the indoor versus outdoor enclosure in elephants (A) and rhinos (B)………………………………………………………………………………………...58 2. Occurrence of urine spraying in the male and female rhinos…………………………...59 3. Object preferences for rubbing in elephants (A) and rhinos (B)………………………...60 4. Mean enrichment use by species (A) and based upon age in rhinos (B)……………….61 5. Mean investigatory bouts of different categories of enrichment………………………..62 6. Actual versus expected use of exhibit areas……………………………………………….63 7. Mean bouts spent in each exhibit area (A) and by each species (B)…………………….64 8. Temperature-related trends in exhibit location in elephants……………………………65 9. Temperature-related trends in exhibit location in rhinos………………………………..66 Chapter 3 1. Mean time displaying social behaviors…………………………………………………….87 2. Social behavior in Jo in relation to enclosure (A) and indoor social housing (B)……...88 3. Effects of housing companion on social behavior (A) and eating (B) in Tika………….88 4. Rate of social interactions (A) and approaches/leaves (B) when housed outside…….90 5. Performance of abnormal behaviors in relation to enclosure (A) and social housing in Jo (B)……………………………………………………………………………………………...91 6. Mean time spent displaying social behavior in relation to sex (A) and age (B)……….92 7. Rate of social interactions (A) and approaches/leaves (B) when housed outside…….93 8. Performance of abnormal behaviors in relation to enclosure in all rhinos (A) and Jimma (B)………………………………………………………………………………………...94 Chapter 4 1. Monthly trends in mean resting behavior………………………………………………..115 2. Monthly trends in mean investigatory and locomotory behavior……………………..115 3. Comparisons of active behaviors pre- and post-diagnosis……………………………..116 4. Monthly trends in mean rate of urine spraying…………………………………………117 v Seasonal Changes in Behavior and Exhibit Use of Captive African Elephants (Loxodonta africana ) and Black Rhinoceroses ( Diceros bicornis ) Abstract by JENNI ELIZABETH MUELLER Despite living in the same habitat and sharing many physiologic characteristics, African elephants and black rhinoceroses are behaviorally very diverse. Each species therefore copes with the challenges of a captive environment in different ways. This study examined the behavior and exhibit use of three African elephants and three black rhinoceroses over a one-year period to determine how each species adapted its natural behavior to captivity in a northern climate. In both species, total time spent active was similar to that seen in the wild. Increased time housed indoors resulted in decreased investigatory behavior and increased abnormal behavior in elephants, and decreased locomotion in rhinos. Both species utilized all areas of the outdoor enclosures, but spent more time than expected near the Building and Door areas. Elephants also favored the Trees, while rhinos favored the Mud Wallow. Individual differences within each species were most prevalent in abnormal and social behaviors. vi Introduction Species-typical behavior patterns are shaped by evolution to correspond to the animal’s physical, ecological, and social needs, forming behavioral repertoires that function specifically in that natural environment. Even within one species, however, different populations may encounter variations in environmental factors and hence species retain some ability to adapt their behavior as a method of coping with a given situation (Carlstead, 1996; Hutchins, 2006; Mason & Mendl, 1993). It is this adaptability and natural coping response that allows wild animals to be held successfully in captivity, as captive environments present new stimuli, expunge other stimuli and require an animal to adjust to an unnatural environment (Carlstead, 1996; Schulte, 2000). Not every individual or species can cope with every situation, however, as species and even individual differences in genetics, development, and previous experience can affect how an animal adapts to either barren or naturalistic captive environments (Carlstead, 1996; Freeman et al, 2004). Additionally, the more an individual is required to cope the more compromised its welfare may be (Veasey, 2006). One important aspect of zoo research is therefore determining whether an animal has successfully adapted to its captive environment, and a vital component of this adaptation is behavior. Proper care in captivity requires evidence-based husbandry and management standards of environmental, social, and behavioral needs (Hutchins, 2006; Veasey, 2006). Natural conditions cannot be precisely recreated, 1 but to determine what is sufficient necessitates research on captive animals. With large mammals especially, research requiring physiological measurements or experimental manipulations are not often feasible and hence behavior is an important aspect in determining well-being (Veasey, 2006). While some deviation from natural behavior is not necessarily problematic, ideally behavior in captivity should overall closely resemble that seen in the wild (Hutchins, 2006). Meeting the behavioral and biological needs of animals becomes especially important with intelligent and social species, as they are more psychologically vulnerable to improper environments (Douglas-Hamilton et al, 2006; Veasey, 2006). Many mammals have demonstrated degrees of intelligence and self-consciousness, and the ability to maintain competent societies additionally requires an understanding of the behaviors and intentions of conspecifics (Mench & Kreger, 1996;
Recommended publications
  • The Interspecific Relationships of Black Rhinoceros (Diceros Bicornis) in Hluhluwe-Imfolozi Park
    The interspecific relationships of black rhinoceros (Diceros bicornis) in Hluhluwe-iMfolozi Park Roan David Plotz B.Sc. (ConsBiolEcol) (Hons1); GradDipEd (Sec) A thesis submitted to Victoria University of Wellington in fulfilment of the requirement for the degree of Doctor of Philosophy in Ecology and Biodiversity 2014 1 “To Ryker, may the wild places of this world long remain protected to captivate and inspire you” Black rhino near the Black iMfolozi River in Hluhluwe-iMfolozi Park, Zululand, South Africa (Photograph by Dale Morris). “We learn more by looking for the answer to a question and not finding it than we do from learning the answer itself.” Lloyd Alexander 2 ABSTRACT As habitat loss, predators (human and non-human) and disease epidemics threaten species worldwide, protected sanctuaries have become vital to species conservation. Hluhluwe-iMfolozi Park (HiP) in South Africa is at the centre of one of the world’s greatest conservation success stories. The formal proclamation of HiP in 1895 prevented the extinction of the south-central black rhino (Diceros bicornis minor) population. In recent times HiP has been a strategic source population for the D. b. minor range expansion program, facilitating an 18-fold population increase across southern Africa. However, HiP’s own black rhino population appears to be in decline. Evidence for decline is most often attributed to overpopulation and poor habitat quality that is driving apparently significant increases in the average home range sizes, poor growth rates (i.e., low calf recruitment) and poor body condition of black rhino. Other factors such as non-human calf predation and parasitism have also been raised as potential causes of decline but remain untested.
    [Show full text]
  • Bill Analysis for File Copy
    OLR Bill Analysis sSB 925 AN ACT PROHIBITING THE IMPORT, SALE AND POSSESSION OF AFRICAN ELEPHANTS, LIONS, LEOPARDS, BLACK RHINOCEROS, WHITE RHINOCEROS AND GIRAFFES. SUMMARY This bill generally bans importing, possessing, selling, offering for sale, or transporting in Connecticut a specimen (dead or alive) of any of six types of African animals, which the bill collectively refers to as the “big six African species.” It applies to certain elephants, lions, leopards, giraffes, and two rhinoceros species. The bill establishes a graduated penalty structure for violations, ranging from no penalty for someone who, unaware and in good faith, violates the ban, to a class D felony for someone with at least two prior violations subject to penalty. In all cases, the bill requires seizing the specimen and any other property or item used in connection with the violation. The specimen, property, or item is then forfeited and, unless the specimen is alive, destroyed. The bill contains several exemptions, including for a specimen that is already legally in the state or distributed to a beneficiary or heir, as long as the owner or distributee timely obtains a certificate of possession from the Department of Energy and Environmental Protection (DEEP). The ban also does not apply to fossils and ivory and the following under certain conditions: circuses; museums; zoological institutions; and motion picture, television, or digital media production companies. Lastly, the bill specifies that the ban does not prohibit transporting through the state endangered or threatened species subject to the terms of another state’s permit, which existing law allows. The United States regulates the trade of the species covered by the Researcher: KLM Page 1 5/8/21 2021SB-00925-R010637-BA.DOCX bill, except the African giraffe, through the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) and laws such as the Endangered Species Act (16 U.S.C.
    [Show full text]
  • The Interspecific Relationships of Black Rhinoceros (Diceros Bicornis) in Hluhluwe-Imfolozi Park
    The interspecific relationships of black rhinoceros (Diceros bicornis) in Hluhluwe-iMfolozi Park Roan David Plotz B.Sc. (ConsBiolEcol) (Hons1); GradDipEd (Sec) A thesis submitted to Victoria University of Wellington in fulfilment of the requirement for the degree of Doctor of Philosophy in Ecology and Biodiversity 2014 1 2 “To Ryker, may the wild places of this world long remain protected to captivate and inspire you” Black rhino near the Black iMfolozi River in Hluhluwe-iMfolozi Park, Zululand, South Africa (Photograph by Dale Morris). “We learn more by looking for the answer to a question and not finding it than we do from learning the answer itself.” Lloyd Alexander 3 4 ABSTRACT As habitat loss, predators (human and non-human) and disease epidemics threaten species worldwide, protected sanctuaries have become vital to species conservation. Hluhluwe-iMfolozi Park (HiP) in South Africa is at the centre of one of the world’s greatest conservation success stories. The formal proclamation of HiP in 1895 prevented the extinction of the south-central black rhino (Diceros bicornis minor) population. In recent times HiP has been a strategic source population for the D. b. minor range expansion program, facilitating an 18-fold population increase across southern Africa. However, HiP’s own black rhino population appears to be in decline. Evidence for decline is most often attributed to overpopulation and poor habitat quality that is driving apparently significant increases in the average home range sizes, poor growth rates (i.e., low calf recruitment) and poor body condition of black rhino. Other factors such as non-human calf predation and parasitism have also been raised as potential causes of decline but remain untested.
    [Show full text]
  • The Decline of Elephant and Black Rhinoceros in Ethiopia M
    The decline of elephant and black rhinoceros in Ethiopia M. J. Largen and D. W. Yalden From the authors' review of the mammals of Ethiopia, undertaken during the last 14 years, it is clear that Ethiopia's elephants and rhinoceroses have suffered massive declines since the beginning of the century. There are perhaps 9000 elephants left, but poaching for ivory and agricultural encroachment continue to threaten them, and only a few rhinoceroses still survive. Ethiopia has limited resources to protect these remaining animals, and needs help and encouragement from outside its boundaries. The status of the elephant Loxodonta africana borders of the country. Destruction of natural and that of the black rhinoceros Diceros bicomis habitat and harassment by an ever-expanding in Africa continue to give acute concern to con- human population with an ever-increasing servationists. Concern for the elephant popu- demand for land have undoubtedly contributed lation includes worries about declining range, to this situation, but enormous numbers of and whether the ivory trade is taking an exploit- elephants have also been killed for profit. The able surplus or is itself causing populations to ivory trade was already long established in 1899 decline (Parker and Martin, 1982, 1983). In a when Harrison (1901) reported 1500 tusks being recent report, Western and Vigne (1985) sug- sent to the capital, in the two months preceding gested that the total black rhinoceros population his visit, from the southern region of the of the continent was only 8800 in 1984, a drop of Ethiopian Rift Valley where the species has since 40 per cent from the 14,000-15,000 of 1980.
    [Show full text]
  • Rhinoceros & Tiger Conservation
    U.S. Fish & Wildlife Service Rhinoceros & Tiger Conservation Act Summary Report 2001-2003 1 The U.S. Fish and Wildlife Service’s mission is working with others to conserve, protect and enhance fish, wildlife, and plants and their habitats for the continuing benefit of the American people. We are the only agency of the U.S. Government with that primary mission. The Service also supports the Department of the Interior’s Strategic Plan to involve various partners such as State and local governments, communities, federally recognized Tribes, non-governmental organizations, and private citizens. The Service’s Division of International Conservation and its partners worldwide support these goals through cross-border cooperation to preserve the habitats that sustain migratory and endangered species. The leadership, knowledge, and cooperation of international partners is crucial to ensure the global conservation of these species and their habitats. Front: Greater one-horned rhinoceros in tall grass habitat of Kaziranga National Park in India’s northeastern state of Assam. International Rhino Foundation Rhinoceros & Tiger Conservation Act Summary Report 2001-2003 A child living in the vicinity of Russia’s tiger habitat created this painting for an art competition. The competition was a component of an education program supported by the Rhinoceros and Tiger Conservation Fund to develop support for tiger conservation among young people. Artwork property of Khabarovsk Wildlife Foundation Government and non-government personnel of Lao PDR, working with Wildlife Conservation Society staff (top), are conducting a tiger camera trap survey (center) of the country’s most promising tiger habitat. Resulting camera trap photographs include the tiger (bottom) and its prey, a sambhar (right), in Nam Et Phou Louey National Protected Area.
    [Show full text]
  • 1999-2000 Summary Report
    U.S. Fish & Wildlife Service Rhinoceros & Tiger Conservation Act Summary Report 1999-2000 “The mission of the U.S. Fish and Wildlife Service is working with others to conserve, protect and enhance fish, wildlife, plants and their habitats for the continuing benefit of the American people.” Cover: Black rhino © Corel Professional Photo Rhinoceros & Tiger Conservation Act Summary Report 1999-2000 Above: Page from storybook on Vietnamese rhino produced with support from the Rhinoceros and Tiger Conservation Fund. See page 17. ©Ina Becker and Trung Dung, Cat Tien National Park Conservation Project Introduction “The tiger is Rhinos and tigers are grand beasts! Their charisma included them in the heritage of more than a many cultures. They have made their way into storybooks, religions, medicines, and charismatic ad campaigns. In their native habitats they predator: it represent beauty, power, grace, and a world kept in balance by the forces of is a keystone nature rather than the whims of man. species in its However, our attraction to these species environment. and their habitats also threatens their existence. It has led to their killing for By saving the trophies and medicines and to the fragmentation and outright destruction of tiger in the their habitat by people seeking timber and world, we save land resources. They are now among the world’s most endangered species. complex ecosystems and habitats that would other- wise be destroyed in the relentless march of human need and, all too often, greed.” Richard Burge Riding theTiger* *Reprinted with the permission of Cambridge University Press Left: Large blocks of the Amur tiger’s forest habitat remain in northern China adjacent to Russian tiger habitat.
    [Show full text]
  • The Sumatran Rhinoceros (Dicerorhinus Sumatrensis) Robin W
    Intensive Management and Preventative Medicine Protocol for the Sumatran Rhinoceros (Dicerorhinus sumatrensis) Robin W. Radcliffe, DVM, DACZM Scott B. Citino, DVM, DACZM Ellen S. Dierenfeld, MS, PhD Thornas J. Foose, MS, PhD l Donald E. Paglia, MD John S. Romo History and ~ack~iound The Sumatran rhinoceros (~icerorhinussumatrensis) is a highly endangered browsing rhinoceros that inhabits the forested regions of Indonesia and Malaysia. The Sumatran is considered a primitive rhinoceros with a characteristic coat of hair; it is closely related to the woolly rhinoceros (Coelodonfa antiquitatis), a species once abundant throughout Asia during the Pleistocene era. In Malaysia, the Sumatran rhino is known locally as badak Kerbau while in Indonesia the local name is badak Sumatera. Today the Sumatran rhinoceros is considered one of the most7endangered large mammals on earth with an estimated 300 animals remaining. Poaching for the animal's horrhas resulted in their decline with habitat loss a secondary factor contributing to population reduction and isolation. Attempts at captive propagation of the Sumatran rhmoceros have been problematic due to sigruhcant health problems and an inability to provide. appropriate captive nutritional and husbandry requirements needed to meet the demands of these highly specialized browsers. This Preventative Medicine Protocol is designed to provide a basis upon which more natural captive propagation efforts for this species can proceed by providing a tool for monitoring health. Goals of Preven tative Medicine Protocol The goals of the preventative medicine protocol are to provide a comprehensive monitoring program to assist in preventing disease and making appropriate decisions regarding health of captive animals. This protocol can be broken down into four main areas: 1.
    [Show full text]
  • Predation, Sensitivity, and Sex: Why Female Black Rhinoceroses Outlive Males
    Predation, sensitivity, and sex: why female black rhinoceroses outlive males Among sexually dimorphic, polygynoui mammals, adult females tend to outlive males and respond more Joel Berger strongly to predators than males. We asked whether a monomorphic, polygynous species virtually immune Cl fi to predation due to large size (black rhinoceros, Diceros bicomis) conforms to this pattern. Data on 193 Program in Ecology, interactions with lions (Panthera Uo) and spotted hyenas (Crvcuta Croatia) in two nonhabituated populations Evolution, in Namibia studied from 1991 to 1993 revealed that: (1) females were more vigilant or aggressive than and Conservation Biology, males to either of the potential predators; and (2) whether solitary or with calves, females attacked more University of Nevada, Reno, NV 89512, USA often than males. Although solitary females tended to be more aggressive to lions than to hyenas, neither females with calves or males seemed to discriminate between the two carnivores. We also simulated the behavior of human predators (poachers) during 69 encounters with rhinoceroses. While both sexes aban- doned local sites because of our presence, females ran farther than males, covering up to 40 km in a day. These findings implicate a behavioral mechanism to explain why secondary sex ratios favor females— males are more prone to human predation, a prediction consistent with data from 12 populations through- out Africa. Black rhinoceroses appear to be an unanticipated exception to the well-established pattern of male-biased mortality in polygynous mammals; in the absence of intense human predation (a recent event), male mortality fails to exceed that of females, suggesting that intrasexual competition in a polygynous mammal may not be the primary cause of unbalanced secondary sex ratios.
    [Show full text]
  • Cop18 Doc. 48
    Original language: English CoP18 Doc. 48 CONVENTION ON INTERNATIONAL TRADE IN ENDANGERED SPECIES OF WILD FAUNA AND FLORA ____________________ Eighteenth meeting of the Conference of the Parties Colombo (Sri Lanka), 23 May-03 June 2019 Interpretation and implementation matters Regulation of trade BLACK RHINOCEROS HUNTING TROPHIES: EXPORT QUOTA FOR SOUTH AFRICA 1. This document has been submitted by South Africa.* COMMENTS OF THE SECRETARIAT A. As required by Resolution Conf. 9.21 (Rev. CoP13) on Interpretation and application of quotas for species included in Appendix I, South Africa has submitted this request for amending Resolution Conf. 13.5 (Rev. CoP14) on Establishment of export quotas for black rhinoceros hunting trophies with supporting information, including details of the scientific basis for the proposed increased quota 150 days prior to the meeting of the Conference of the Parties. B. South Africa explains the rationale for a proposed increase from an annual export quota of five hunting trophies of adult male black rhinoceros to “a total number of adult black rhinoceroses not exceeding 0.5% of the total black rhinoceros population in South Africa in the year of export (equally applied to all three subspecies, i.e. 0.5% of the total population of each of the three subspecies)”. It is noted that South Africa states that it has not utilised its full current quota of 5 male hunting trophies for the period 2005 to 2015. C. South Africa argues that this is a conservative increase that supports the adaptive management of its black rhino populations, and allows for adjustments based on population size, while maintaining a restriction that only males that meet a set of safeguard criteria qualify for hunting.
    [Show full text]
  • Molecular Phylogenetics of the Rhinoceros Clade And
    MOLECULAR PHYLOGENETICS OF THE RHINOCEROS CLADE AND EVOLUTION OF UCP1 TRANSCRIPTIONAL REGULATORY ELEMENTS ACROSS THE MAMMALIAN PHYLOGENY By Michael J. Gaudry A Thesis submitted to the Faculty of Graduate Studies of The University of Manitoba In partial fulfillment of the requirements of the degree of MASTER OF SCIENCE Department of Biological Sciences University of Manitoba Winnipeg Canada Copyright © 2017 by Michael J. Gaudry ABSTRACT Aiming to resolve contentious phylogenetic relationships among rhinoceros subfamilies (Dicerorhininae, Rhinocerotinae, and Dicerotinae), I constructed a ~131 kilobase nuclear DNA dataset for the Malayan tapir and six rhinoceros species, including the extinct woolly rhinoceros. Phylogenetic analyses, possibly confounded by incomplete lineage sorting associated with quick ancestral speciation events, yielded opposing trees: ((Dicerorhininae, Rhinocerotinae) Dicerotinae) or (Rhinocerotinae (Dicerorhininae, Dicerotinae)), though five of six informative indels independently supported the latter relationship. Additionally, eye genes revealed no inactivating mutations that may underlie reputedly poor vision among rhinoceroses. Furthermore, I investigated thermogenic UCP1 transcriptional regulators among 139 mammal species, expecting deleterious mutations in eutherians possessing UCP1 pseudogenes and possibly even large-bodied species (e.g. rhinoceroses) that retain intact UCP1. Promoters and enhancers were conserved in all species with intact UCP1, suggesting that it remains functionally expressed in these species. However, these elements have been lost in some UCP1-less species, indicating the enhancer is non-pleotropic. ii ACKNOWLEDGMENTS I would especially like to thank my supervisor, Kevin Campbell, for his endless support over the course of my research. I will be forever appreciative for his advice and willingness to share his vast expertise. His energetic enthusiasm and curiosity have been increadibly motivational and he has shown me what it means to be a scientist.
    [Show full text]
  • Modeling Black Rhinoceros (Diceros Bicornis) Population Performance In
    y & E sit nd er a v n i g d e o i r e Journal of B d f S o Soka GE, Rija AA and Owino A, J Biodivers p l e a c ISSN:n 2332-2543 r i e u Endanger Species 2014, 2:3 s o J Biodiversity & Endangered Species DOI: 10.4172/2332-2543.1000126 Research Article Open Access Modeling Black Rhinoceros (Diceros bicornis) Population Performance in East Africa: The Case of Lake Nakuru National Park, Kenya Geofrey E Soka1*, Alfan A Rija1 and Alfred Owino2 1Department of Wildlife Management, Sokoine University of Agriculture, Tanzania 2National Museums of Kenya, PO Box 40658, Nairobi, Kenya *Corresponding author: Geofrey E Soka, Department of Wildlife Management, Sokoine University of Agriculture, Tanzania, Tel: 255782975720; E-mail: [email protected] Rec date: Mar 21, 2014; Acc date: Apr 24, 2014; Pub date: May 4, 2014 Copyright: © 2014 Soka GE, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited. Abstract The black rhinoceros have declined across Africa both in numbers and range distribution, making long-term population persistence of this iconic species uncertain. We conducted simulation models to predict population performance of black rhinoceros in Lake Nakuru National Park under different scenarios of environmental variation and translocation regimes. A decade-long (1987-1997) demographic data were used to construct stochastic simulation models using VORTEX computer program. In addition, we assessed extinction risks and patterns of heterozygosity among the modelled populations (reported every five years) to characterize the dynamics of this population over a hundred years.
    [Show full text]
  • Diceros Bicornis – Black Rhinoceros
    Diceros bicornis – Black Rhinoceros While Black Rhinoceros subpopulations are generally faring well within the assessment region, they are threatened by the poaching pandemic, especially in Kruger National Park. Combatting the poaching crisis requires a multifaceted strategy including anti-poaching programmes, demand reduction campaigns, disrupting criminal networks and providing options for alternative economies in areas abutting protected areas (Ferreira et al. 2015). Global Red List status (2012)‡ D. bicornis Critically Endangered A2abcd Diceros bicornis minor, Emmanuel Do Linh San D. b. bicornis Vulnerable D1 D. b. minor Critically Endangered Regional Red List status (2016) Endangered C2a(i)*† A2abcd D. b. bicornis Endangered D*† D. b. michaeli Critically Endangered A2abcd D. b. minor Endangered C2a(i)*† TOPS listing (NEMBA) (2007) D. b. michaeli Critically Endangered D*† D. b. bicornis National Red List status (2004) D. b. minor D. bicornis Endangered D. b. bicornis Critically Endangered D D. b. michaeli D. b. minor Vulnerable D1 CITES listing (2005) Appendix I D. b. michaeli Not Evaluated Endemic No Reasons for change Percentage of global wild population conserved in South Africa and Swaziland at end of 2015: D. b. bicornis Genuine change: Increased population D. bicornis 36.4% D. b. minor Genuine change: D. b. bicornis 11.6% Projected decline D. b. minor 73.0% D. b. michaeli Genuine change: New listing D. b. michaeli 8.9% *Watch-list Threat †Conservation Dependent ‡Currently under revision Southwestern Black Rhinoceros (English). Diceros Taxonomy bicornis minor: Southern-central Black Rhinoceros (English). Diceros bicornis michaeli: Eastern Black Diceros bicornis (Linnaeus 1758) Rhinoceros (English). ANIMALIA - CHORDATA - MAMMALIA - Taxonomic status: Species and subspecies.
    [Show full text]