Hybridization with Mountain Hares Increases the Functional Allelic Repertoire in Brown Hares Jaakko L
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Purebred Dog Breeds Into the Twenty-First Century: Achieving Genetic Health for Our Dogs
Purebred Dog Breeds into the Twenty-First Century: Achieving Genetic Health for Our Dogs BY JEFFREY BRAGG WHAT IS A CANINE BREED? What is a breed? To put the question more precisely, what are the necessary conditions that enable us to say with conviction, "this group of animals constitutes a distinct breed?" In the cynological world, three separate approaches combine to constitute canine breeds. Dogs are distinguished first by ancestry , all of the individuals descending from a particular founder group (and only from that group) being designated as a breed. Next they are distinguished by purpose or utility, some breeds existing for the purpose of hunting particular kinds of game,others for the performance of particular tasks in cooperation with their human masters, while yet others owe their existence simply to humankind's desire for animal companionship. Finally dogs are distinguished by typology , breed standards (whether written or unwritten) being used to describe and to recognize dogs of specific size, physical build, general appearance, shape of head, style of ears and tail, etc., which are said to be of the same breed owing to their similarity in the foregoing respects. The preceding statements are both obvious and known to all breeders and fanciers of the canine species. Nevertheless a correct and full understanding of these simple truisms is vital to the proper functioning of the entire canine fancy and to the health and well being of the animals which are the object of that fancy. It is my purpose in this brief to elucidate the interrelationship of the above three approaches, to demonstrate how distortions and misunderstandings of that interrelationship now threaten the health of all of our dogs and the very existence of the various canine breeds, and to propose reforms which will restore both balanced breed identity and genetic health to CKC breeds. -
Parasitic Nematodes of Pool Frog (Pelophylax Lessonae) in the Volga Basin
Journal MVZ Cordoba 2019; 24(3):7314-7321. https://doi.org/10.21897/rmvz.1501 Research article Parasitic nematodes of Pool Frog (Pelophylax lessonae) in the Volga Basin Igor V. Chikhlyaev1 ; Alexander B. Ruchin2* ; Alexander I. Fayzulin1 1Institute of Ecology of the Volga River Basin, Russian Academy of Sciences, Togliatti, Russia 2Mordovia State Nature Reserve and National Park «Smolny», Saransk, Russia. *Correspondence: [email protected] Received: Febrary 2019; Accepted: July 2019; Published: August 2019. ABSTRACT Objetive. Present a modern review of the nematodes fauna of the pool frog Pelophylax lessonae (Camerano, 1882) from Volga basin populations on the basis of our own research and literature sources analysis. Materials and methods. Present work consolidates data from different helminthological works over the past 80 years, supported by our own research results. During the period from 1936 to 2016 different authors examined 1460 specimens of pool frog, using the method of full helminthological autopsy, from 13 regions of the Volga basin. Results. In total 9 nematodes species were recorded. Nematode Icosiella neglecta found for the first time in the studied host from the territory of Russia and Volga basin. Three species appeared to be more widespread: Oswaldocruzia filiformis, Cosmocerca ornata and Icosiella neglecta. For each helminth species the following information included: systematic position, areas of detection, localization, biology, list of definitive hosts, the level of host-specificity. Conclusions. Nematodes of pool frog, excluding I. neglecta, belong to the group of soil-transmitted helminthes (geohelminth) and parasitize in adult stages. Some species (O. filiformis, C. ornata, I. neglecta) are widespread in the host range. -
Ecography ECOG-01063 Verde Arregoitia, L
Ecography ECOG-01063 Verde Arregoitia, L. D., Leach, K., Reid, N. and Fisher, D. O. 2015. Diversity, extinction, and threat status in Lagomorphs. – Ecography doi: 10.1111/ecog.01063 Supplementary material 1 Appendix 1 2 Paleobiogeographic summaries for all extant lagomorph genera. 3 4 Pikas – Family Ochotonidae 5 The maximum diversity and geographic extent of pikas occurred during the global climate 6 optimum from the late-Oligocene to middle-Miocene (Ge et al. 2012). When species evolve 7 and diversify at higher temperatures, opportunities for speciation and evolution of thermal 8 niches are likely through adaptive radiation in relatively colder and species poor areas 9 (Araújo et al. 2013). Extant Ochotonids may be marginal (ecologically and geographically) 10 but diverse because they occur in topographically complex areas where habitat diversity is 11 greater and landscape units are smaller (Shvarts et al. 1995). Topographical complexity 12 creates new habitat, enlarges environmental gradients, establishes barriers to dispersal, and 13 isolates populations. All these conditions can contribute to adaptation to new environmental 14 conditions and speciation in excess of extinction for terrestrial species (Badgley 2010). 15 16 Hares and rabbits - Family Leporidae 17 Pronolagus, Bunolagus, Romerolagus, Pentalagus and Nesolagus may belong to lineages 18 that were abundant and widespread in the Oligocene and subsequently lost most (if not all) 19 species. Lepus, Sylvilagus, Caprolagus and Oryctolagus represent more recent radiations 20 which lost species unevenly during the late Pleistocene. Living species in these four genera 21 display more generalist diet and habitat preferences, and are better represented in the fossil 22 record. (Lopez-Martinez 2008). -
Review of the Current State of Genetic Testing - a Living Resource
Review of the Current State of Genetic Testing - A Living Resource Prepared by Liza Gershony, DVM, PhD and Anita Oberbauer, PhD of the University of California, Davis Editorial input by Leigh Anne Clark, PhD of Clemson University July, 2020 Contents Introduction .................................................................................................................................................. 1 I. The Basics ......................................................................................................................................... 2 II. Modes of Inheritance ....................................................................................................................... 7 a. Mendelian Inheritance and Punnett Squares ................................................................................. 7 b. Non-Mendelian Inheritance ........................................................................................................... 10 III. Genetic Selection and Populations ................................................................................................ 13 IV. Dog Breeds as Populations ............................................................................................................. 15 V. Canine Genetic Tests ...................................................................................................................... 16 a. Direct and Indirect Tests ................................................................................................................ 17 b. Single -
Niche Overlap of Mountain Hare Subspecies and the Vulnerability Of
Niche overlap of mountain hare subspecies and the vulnerability of their ranges to invasion by the European hare; the (bad) luck of the Irish Caravaggi, A., Leach, K., Santilli, F., Rintala, J., Helle, P., Tiainen, J., Bisi, F., Martinoli, A., Montgomery, W. I., & Reid, N. (2016). Niche overlap of mountain hare subspecies and the vulnerability of their ranges to invasion by the European hare; the (bad) luck of the Irish. Biological Invasions. https://doi.org/10.1007/s10530-016-1330-z Published in: Biological Invasions Document Version: Publisher's PDF, also known as Version of record Queen's University Belfast - Research Portal: Link to publication record in Queen's University Belfast Research Portal Publisher rights © The Author(s) 2016. This article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. General rights Copyright for the publications made accessible via the Queen's University Belfast Research Portal is retained by the author(s) and / or other copyright owners and it is a condition of accessing these publications that users recognise and abide by the legal requirements associated with these rights. Take down policy The Research Portal is Queen's institutional repository that provides access to Queen's research output. Every effort has been made to ensure that content in the Research Portal does not infringe any person's rights, or applicable UK laws. -
Appendix Lagomorph Species: Geographical Distribution and Conservation Status
Appendix Lagomorph Species: Geographical Distribution and Conservation Status PAULO C. ALVES1* AND KLAUS HACKLÄNDER2 Lagomorph taxonomy is traditionally controversy, and as a consequence the number of species varies according to different publications. Although this can be due to the conservative characteristic of some morphological and genetic traits, like general shape and number of chromosomes, the scarce knowledge on several species is probably the main reason for this controversy. Also, some species have been discovered only recently, and from others we miss any information since they have been first described (mainly in pikas). We struggled with this difficulty during the work on this book, and decide to include a list of lagomorph species (Table 1). As a reference, we used the recent list published by Hoffmann and Smith (2005) in the “Mammals of the world” (Wilson and Reeder, 2005). However, to make an updated list, we include some significant published data (Friedmann and Daly 2004) and the contribu- tions and comments of some lagomorph specialist, namely Andrew Smith, John Litvaitis, Terrence Robinson, Andrew Smith, Franz Suchentrunk, and from the Mexican lagomorph association, AMCELA. We also include sum- mary information about the geographical range of all species and the current IUCN conservation status. Inevitably, this list still contains some incorrect information. However, a permanently updated lagomorph list will be pro- vided via the World Lagomorph Society (www.worldlagomorphsociety.org). 1 CIBIO, Centro de Investigaça˜o em Biodiversidade e Recursos Genéticos and Faculdade de Ciˆencias, Universidade do Porto, Campus Agrário de Vaira˜o 4485-661 – Vaira˜o, Portugal 2 Institute of Wildlife Biology and Game Management, University of Natural Resources and Applied Life Sciences, Gregor-Mendel-Str. -
Use of Two Distant Nesting Areas As a Breeding Strategy of Golden Eagles Aquila Chrysaetos in Valdres, Southeast Norway
Ornis Norvegica (2021), 44: 12–18 Norwegian Ornithological Society doi: 10.15845/on.v44i0.3114 Use of two distant nesting areas as a breeding strategy of Golden Eagles Aquila chrysaetos in Valdres, southeast Norway Henning Dunker Rennaveien 7, 2930 Bagn, Norway; [email protected] Abstract. Sixteen occupied nesting territories of Golden Eagle Aquila chrysaetos were studied between 2000 and 2020, in the southern part of the valley of Valdres, southeast Norway. Most of the study area consists of rolling hills dominated by spruce Picea abies with numerous clear-cuts. It was concluded that at least six (about 40%) of the eagle pairs in these territories move back and forth between two alternate, distant nesting areas 5.3 km apart (average). In two additional pairs, a second nesting area was considered possible. In the remaining eight, only one nesting area was found. The periods of one nesting area in use varied from 2–19 years, before moving to the other nesting area. This result was supported by panoramic mid-day surveillance of the air space between the two nesting areas during 2014–2020. The maintenance of a second core nesting area is most likely a strategy for moving to a more favourable hunting area and might be initiated by a new mate in the pair. The move might also be influenced by avoidance of a close neighbouring pair. A switch of nesting areas, as indicated by this study, could significantly affect results, when the number of eagle pairs in a certain area is counted. Keywords: Golden Eagle, nesting areas, south Norway INTRODUCTION support breeding (Madders & Walker 2002, Watson 2010, Dunker 2015, Walker 2017). -
Balancing Selection at the Prion Protein Gene Consistent with Prehistoric Kurulike Epidemics Simon Mead,1 Michael P
Balancing Selection at the Prion Protein Gene Consistent with Prehistoric Kurulike Epidemics Simon Mead,1 Michael P. H. Stumpf,2 Jerome Whitfield,1,3 Jonathan A. Beck,1 Mark Poulter,1 Tracy Campbell,1 James Uphill,1 David Goldstein,2 Michael Alpers,1,3,4 Elizabeth M. C. Fisher,1 John Collinge1* 1Medical Research Council, Prion Unit, and Department of Neurodegenerative Disease, Institute of Neurology, University College, Queen Square, London WC1N 3BG, UK. 2Department of Biology (Galton Laboratory), University College London, Gower Street, London WC1E 6BT, UK. 3Institute of Medical Research, Goroka, EHP, Papua New Guinea. 4Curtin University of Technology, Perth, WA, Australia. *To whom correspondence should be addressed. E-mail: [email protected] Kuru is an acquired prion disease largely restricted to the cannibalism imposed by the Australian authorities in the mid- Fore linguistic group of the Papua New Guinea Highlands 1950s led to a decline in kuru incidence, and although rare which was transmitted during endocannibalistic feasts. cases still occur these are all in older individuals and reflect Heterozygosity for a common polymorphism in the the long incubation periods possible in human prion human prion protein gene (PRNP) confers relative diseasekuru has not been recorded in any individual born after the late 1950s (4). resistance to prion diseases. Elderly survivors of the kuru A coding polymorphism at codon 129 of PRNP is a strong epidemic, who had multiple exposures at mortuary feasts, susceptibility factor for human prion diseases. Methionine are, in marked contrast to younger unexposed Fore, homozygotes comprise 37% of the UK population whereas predominantly PRNP 129 heterozygotes. -
Introductory Research Essay
Introductory Research Essay Golden eagle (Aquila chrysaetos) ecology and forestry. Edward Moss 2011 Introductory Research Essay No. 10 Department of Wildlife, Fish, and Environmental Studies Swedish University of Agricultural Sciences 901 83 Umeå, Sweden Contents Page 1 Background 3 2 Terminology 4 3 Global range of the golden eagle 5 4 The Swedish golden eagle population 6 5 Food supply with links to eagle reproduction 7 5.1 Prey species, their main habitats and distributions in Sweden. 8 5.2 Temporal and spatial variation of prey and other food sources 9 6 Reproduction 12 6.1 The breeding cycle. 12 6.2 Factors influencing reproduction. 14 7 Habitat selection and properties 17 7.1 The eyrie. 17 7.2 Habitat selection at a landscape scale. 19 8 Golden eagle monitoring 22 9 Land use change 23 9.1 Golden eagles and forestry - a global perspective. 24 9.2 Golden eagles and forestry in Sweden. 25 10 Conclusions 26 References 27 Principal supervisor: Birger Hörnfeldt Assistant supervisors: Frauke Ecke, Tim Hipkiss, Mats Nilsson 2 1 Background The widespread growth of commercial forestry in the second half of the 20th century has led to an increasing concern over the effects it may have upon species dependent on old growth forests. The golden eagle (Aquila chrysaetos) inhabits mainly mountainous environments throughout the northern hemisphere and is an example of just one species that is affected by forestry practices (Whitfield et al. 2001, Pedrini et al. 2001b). Tjernberg (1983a) studied 97 nesting trees in boreal Sweden and found golden eagles nested predominantly in older trees with a mean age of 335 years. -
SNH Commissioned Report 278: the Distribution of Mountain Hare
COMMISSIONED REPORT Commissioned Report No. 278 The distribution of Mountain Hare ( Lepus timidus ) in Scotland (2006/07) (ROAME No. R07AC308) For further information on this report please contact : Rob Raynor Scottish Natural Heritage Great Glen House INVERNESS IV3 8NW Telephone: 01463-725 244 E-mail: [email protected] This report should be quoted as : Kinrade, V., Ewald, J., Smith, A., Newey, S., Iason, G., Thirgood, S. & Raynor, R. (2008). The distribution of Mountain Hare (Lepus timidus) in Scotland (2006/07). Scottish Natural Heritage Commissioned Report No.278 (ROAME No. R07AC308). This report, or any part of it, should not be reproduced without the permission of Scottish Natural Heritage. This permission will not be withheld unreasonably. The views expressed by the author(s) of this report should not be taken as the views and policies of Scottish Natural Heritage. © Scottish Natural Heritage 2008. COMMISSIONED REPORT Summary The distribution of Mountain Hare ( Lepus timidus ) in Scotland (2006/07) Commissioned Report No. 278 (ROAME No. R07AC308) Contractor: Kinrade V, Ewald J, Smith A, Newey S, Iason G, Thirgood S & Raynor R Year of publication: 2008 Background The aim of this questionnaire-based survey was to assess the distribution of mountain hares in Scotland in 2006/07 and estimate the number of mountain hares taken for harvesting and population control purposes over the same time period. A secondary aim was to compare these data to similar data collected in 1995/96 (Tapper 1996) to establish any patterns of change in distribution and the level of take. Main findings • The area surveyed for mountain hares in 2006/07 was 71,098km 2, equivalent to 90% of the total area of Scotland. -
Strong Balancing Selection at HLA Loci: Evidence from Segregation In
Proc. Natl. Acad. Sci. USA Vol. 94, pp. 12452–12456, November 1997 Evolution Strong balancing selection at HLA loci: Evidence from segregation in South Amerindian families (heterozygote advantageymaternal–fetal interactionymajor histocompatibility complexypolymorphismyreciprocal matings) FRANCIS L. BLACK† AND PHILIP W. HEDRICK‡§ †Department of Epidemiology and Public Health, Yale University School of Medicine, New Haven, CT 06520; and ‡Department of Biology, Arizona State University, Tempe, AZ 85287-1501 Edited by Margaret G. Kidwell, University of Arizona, Tucson, AZ, and approved September 3, 1997 (received for review July 23, 1997) ABSTRACT The genotypic proportions for major histo- The reduced proportion of HLA-A and HLA-B homozygotes compatibility complex loci, HLA-A and HLA-B, of progeny in observed in population samples of South Amerindians (8) needs families in 23 South Amerindian tribes in which segregation an s value of 0.425 to explain the deficiency (12). These results for homozygotes and heterozygotes could occur are examined. may not necessarily be in conflict if by chance the observations in Overall, there is a large deficiency of homozygotes compared refs. 8 and 9 are high values that would average away with lower with Mendelian expectations (for HLA-A, 114 observed and values in the past. In fact, there has probably been strong selection 155.50 expected and for HLA-B 110 observed and 144.75 in recent generations, if not the present one (3, 13). expected), consistent with strong balancing selection favoring Here, we present data showing a large excess of heterozy- heterozygotes. There is no evidence that these deficiencies gotes (a large deficiency of homozygotes) compared with were associated with particular alleles or with the age of the Mendelian expectations in 510 offspring from parents with individuals sampled. -
Strasbourg, 22 May 2002
Strasbourg, 21 October 2015 T-PVS/Inf (2015) 18 [Inf18e_2015.docx] CONVENTION ON THE CONSERVATION OF EUROPEAN WILDLIFE AND NATURAL HABITATS Standing Committee 35th meeting Strasbourg, 1-4 December 2015 GROUP OF EXPERTS ON THE CONSERVATION OF AMPHIBIANS AND REPTILES 1-2 July 2015 Bern, Switzerland - NATIONAL REPORTS - Compilation prepared by the Directorate of Democratic Governance / The reports are being circulated in the form and the languages in which they were received by the Secretariat. This document will not be distributed at the meeting. Please bring this copy. Ce document ne sera plus distribué en réunion. Prière de vous munir de cet exemplaire. T-PVS/Inf (2015) 18 - 2 – CONTENTS / SOMMAIRE __________ 1. Armenia / Arménie 2. Austria / Autriche 3. Belgium / Belgique 4. Croatia / Croatie 5. Estonia / Estonie 6. France / France 7. Italy /Italie 8. Latvia / Lettonie 9. Liechtenstein / Liechtenstein 10. Malta / Malte 11. Monaco / Monaco 12. The Netherlands / Pays-Bas 13. Poland / Pologne 14. Slovak Republic /République slovaque 15. “the former Yugoslav Republic of Macedonia” / L’« ex-République yougoslave de Macédoine » 16. Ukraine - 3 - T-PVS/Inf (2015) 18 ARMENIA / ARMENIE NATIONAL REPORT OF REPUBLIC OF ARMENIA ON NATIONAL ACTIVITIES AND INITIATIVES ON THE CONSERVATION OF AMPHIBIANS AND REPTILES GENERAL INFORMATION ON THE COUNTRY AND ITS BIOLOGICAL DIVERSITY Armenia is a small landlocked mountainous country located in the Southern Caucasus. Forty four percent of the territory of Armenia is a high mountainous area not suitable for inhabitation. The degree of land use is strongly unproportional. The zones under intensive development make 18.2% of the territory of Armenia with concentration of 87.7% of total population.