And Water Deer (Hydropotes Inermis) Using Capillary Electrophoresis-Based Multiplex PCR
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Species Fact Sheet: Roe Deer (Capreolus Capreolus) [email protected] 023 8023 7874
Species Fact Sheet: Roe Deer (Capreolus capreolus) [email protected] www.mammal.org.uk 023 8023 7874 Quick Facts Recognition: Small deer, reddish brown in summer, grey in winter. Distinctive black moustache stripe, white chin. Appears tail-less with white/ cream rump patch which is especially conspicuous when its hairs are puffed out when the deer is alarmed. Males have short antlers, erect with no more than three points. Size: Average height at shoulder 60-75cm. Males slightly larger. Weight: Adults 10—25kg Life Span: The maximum age in the wild is 16 years, but most live 7 years.. Distribution & Habitat Roe deer are widespread throughout Scotland and much of England, and in many areas they are abundant. They are increasing their range. They are spreading southwards from their Scottish refuge, and northwards and westwards from the reintroduced populations, but are not yet but are not yet established in most of the Midlands and Kent. They have never occurred in Ireland. They are generally found in open mixed, coniferous or purely deciduous woodland, particularly at edges between woodland and open habitats. Roe deer feed throughout the 24 hours, but are most active at dusk and dawn. General Ecology Behaviour Roe deer exist solitary or in small groups, with larger groups typically feeding together during the winter. At exceptionally high densities, herds of 15 or more roe deer can be seen in open fields during the spring and summer. Males are seasonally territorial, from March to August. Young females usually establish ranges close to their mothers; juvenile males are forced to disperse further afield. -
White-Tailed Deer Winter Feeding Strategy in Area Shared with Other Deer Species
Folia Zool. – 57(3): 283–293 (2008) White-tailed deer winter feeding strategy in area shared with other deer species Miloslav HOMOLKA1, Marta HEROLDOVÁ1 and Luděk BARToš2 1 Institute of Vertebrate Biology, Academy of Sciences of the Czech Republic,v.v.i., Květná 8, CZ-603 65 Brno, Czech Republic; e-mail: [email protected] 2 Department of Ethology, Institute of Animal Science, P.O.B. 1, CZ-104 01 Praha 10 Uhříněves, Czech Republic Received 25 January 2008, Accepted 9 June 2008 Abstract. White-tailed deer were introduced into the Czech Republic about one hundred years ago. Population numbers have remained stable at low density despite almost no harvesting. This differs from other introductions of this species in Europe. We presumed that one of the possible factors preventing expansion of the white-tailed deer population is lack of high-quality food components in an area overpopulated by sympatric roe, fallow and red deer. We analyzed the WTD winter diet and diets of the other deer species to get information on their feeding strategy during a critical period of a year. We focused primarily on conifer needle consumption, a generally accepted indicator of starvation and on bramble leaves as an indicator of high-quality items. We tested the following hypotheses: (1) If the environment has a limited food supply, the poorest competitors of the four deer species will have the highest proportion of conifer needles in the diet ; (2) the deer will overlap in trophic niches and will share limited nutritious resource (bramble). White-tailed, roe, fallow, and red deer diets were investigated by microscopic analysis of plant remains in their faeces. -
Reproductive Seasonality in Captive Wild Ruminants: Implications for Biogeographical Adaptation, Photoperiodic Control, and Life History
Zurich Open Repository and Archive University of Zurich Main Library Strickhofstrasse 39 CH-8057 Zurich www.zora.uzh.ch Year: 2012 Reproductive seasonality in captive wild ruminants: implications for biogeographical adaptation, photoperiodic control, and life history Zerbe, Philipp Abstract: Zur quantitativen Beschreibung der Reproduktionsmuster wurden Daten von 110 Wildwiederkäuer- arten aus Zoos der gemässigten Zone verwendet (dabei wurde die Anzahl Tage, an denen 80% aller Geburten stattfanden, als Geburtenpeak-Breite [BPB] definiert). Diese Muster wurden mit verschiede- nen biologischen Charakteristika verknüpft und mit denen von freilebenden Tieren verglichen. Der Bre- itengrad des natürlichen Verbreitungsgebietes korreliert stark mit dem in Menschenobhut beobachteten BPB. Nur 11% der Spezies wechselten ihr reproduktives Muster zwischen Wildnis und Gefangenschaft, wobei für saisonale Spezies die errechnete Tageslichtlänge zum Zeitpunkt der Konzeption für freilebende und in Menschenobhut gehaltene Populationen gleich war. Reproduktive Saisonalität erklärt zusätzliche Varianzen im Verhältnis von Körpergewicht und Tragzeit, wobei saisonalere Spezies für ihr Körpergewicht eine kürzere Tragzeit aufweisen. Rückschliessend ist festzuhalten, dass Photoperiodik, speziell die abso- lute Tageslichtlänge, genetisch fixierter Auslöser für die Fortpflanzung ist, und dass die Plastizität der Tragzeit unterstützend auf die erfolgreiche Verbreitung der Wiederkäuer in höheren Breitengraden wirkte. A dataset on 110 wild ruminant species kept in captivity in temperate-zone zoos was used to describe their reproductive patterns quantitatively (determining the birth peak breadth BPB as the number of days in which 80% of all births occur); then this pattern was linked to various biological characteristics, and compared with free-ranging animals. Globally, latitude of natural origin highly correlates with BPB observed in captivity, with species being more seasonal originating from higher latitudes. -
Deer Biology That Will Be Most Relevant to Deer Practitioners, Managers and Landowners
Introduction The purpose of this guide is to highlight aspects of deer biology that will be most relevant to deer practitioners, managers and landowners. It is not a complete discussion of deer biology for which there are other sources (see Further Info). This guide links to the following guides: Deer Species, Deer Signs, and Deer Behaviour. Appearance all of our wild deer are spotted when born Each species has it’s own characteristic appearance, some have unique features that are visible even in the very young. Size, body shape, detailed colouration and antler shape are useful clues, as are finer details Deer skulls can be easily distinguished from many such as facial characteristics and the appearance of other mammals, they have: the tail area. Aspects of behaviour may also help to ♦ large eye sockets on the side of the head differentiate species. ♦ in most species, a sub-orbital scent gland pit in All of our wild species are spotted when young but front of the eye from 2-5 months of age go into their adult coat which ♦ pedicles on the frontal bones, on top of from then on cycles through a biannual change in coat which will usually be antlers (male deer texture and/or colouration. The change from winter except Chinese water deer) Occasionally, old to summer coat is the most obvious, changes in female deer may also have lumps on the skull colouration can be very marked. Timing is dependent resembling pedicles. on species and age, younger animals generally changing coat first. Deer hair is hollow (it kinks like Antlers are unique to deer, usually only males have a drinking straw when bent), is rather brittle and is them except in reindeer. -
Behavioral Changes, Stress, and Survival Following Reintroduction of Persian Fallow Deer from Two Breeding Facilities
Contributed Paper Behavioral Changes, Stress, and Survival Following Reintroduction of Persian Fallow Deer from Two Breeding Facilities ROYI ZIDON,∗§ DAVID SALTZ,† LAURENCE S. SHORE,‡ AND UZI MOTRO∗ ∗Department of Evolution, Systematics and Ecology, The Hebrew University of Jerusalem, Jerusalem 91904, Israel †Mitrani Department of Desert Ecology, The Institute for Desert Research, Ben Gurion University of the Negev, Sde Boqer Campus 84990, Israel ‡Veterinary Services and Animal Health, P.O. Box 12, Bet Dagan 50250, Israel Abstract: Reintroductions often rely on captive-raised, na¨ıve animals that have not been exposed to the various threats present in natural environments. Wild animals entering new areas are timid and invest much time and effort in antipredator behavior. On the other hand, captive animals reared in predator- free conditions and in close proximity to humans may initially lack this tendency, but can reacquire some antipredator behavior over time. We monitored the changes in antipredator-related behaviors of 16 radio- collared Persian fallow deer (Dama mesopotamica) reintroduced to the Soreq Valley in Israel from 2 breeding facilities: one heavily visited by the public (The Biblical Zoo of Jerusalem, Israel) and the other with reduced human presence (Hai-Bar Carmel, Israel). We monitored each individual for up to 200 days after release, focusing on flush and flight distance, flight mode (running or walking), and use of cover. In addition, we compared fecal corticosterone (a stress-related hormone) from samples collected from -
Predicting Abundance and Distribution of Wild Deer in England: Supporting a Vision for Natural England
Research Report 10/2 Predicting abundance and distribution of wild deer in England: supporting a vision for Natural England. Rory Putman and Alastair Ward AAAugust 2010 Predicting abundance and distribution of wild deer in England: supporting a vision for Natural England. Prepared by Rory Putman and Alastair Ward Deer Initiative Research Report 10/2 August 2010 Further information can be obtained from: The Deer Initiative The Carriage House Brynkinalt Business Centre Chirk Wrexham LL14 5NS www.thedeerinitiative.co.uk Or email: [email protected] 1 Contents Page 1. Introduction 3 2. Recent distribution and patterns of abundance of deer in England and Wales 5 3. Current patterns of abundance of deer in England 10 4. Factors associated with distribution patterns of different deer species in 14 England 5. Identification of landscape features that might influence the spread of 17 different deer species 6. Application of the models to predict future trends in distribution and 20 abundance 7. Management options to contain future range expansion 21 8. Conclusion 22 9. Recommendations for further work 25 References 26 Appendix One: Identifying threshold densities for wild deer in the UK above which negative impacts may occur. R.J.Putman, J.Langbein, P. Green and P. Watson (2011a). Appendix Two: Assessing deer densities and impacts at the appropriate level for management: a review of methodologies for use beyond the site scale. R.J.Putman, P. Watson and J. Langbein (2011b). Appendix Three: Mapping the local and national abundance of wild deer in England and Wales. Alastair I. Ward, Thomas R. Etherington : Supporting the development of Natural England’s vision for wild deer in England: predicting abundance and distribution Appendix Four: Predicting future distributions of deer in Great Britain and assessing their relative competitive ability using favourability functions. -
Sexual Selection and Extinction in Deer Saloume Bazyan
Sexual selection and extinction in deer Saloume Bazyan Degree project in biology, Master of science (2 years), 2013 Examensarbete i biologi 30 hp till masterexamen, 2013 Biology Education Centre and Ecology and Genetics, Uppsala University Supervisor: Jacob Höglund External opponent: Masahito Tsuboi Content Abstract..............................................................................................................................................II Introduction..........................................................................................................................................1 Sexual selection........................................................................................................................1 − Male-male competition...................................................................................................2 − Female choice.................................................................................................................2 − Sexual conflict.................................................................................................................3 Secondary sexual trait and mating system. .............................................................................3 Intensity of sexual selection......................................................................................................5 Goal and scope.....................................................................................................................................6 Methods................................................................................................................................................8 -
{TEXTBOOK} Is a Camel a Mammal?
IS A CAMEL A MAMMAL? PDF, EPUB, EBOOK Tish Rabe,Jim Durk | 48 pages | 04 Jun 2001 | HarperCollins Publishers | 9780007111077 | English | London, United Kingdom Is a Camel a Mammal? PDF Book Ano ang katangian ng salawikain? Retrieved 5 December Camel is an animal and is not an egg laying mammal. So we had what amounted to two pounds or more of rubber for dinner that night. Is camel a marsupial mammal? What rhymes with mammal? Center for Muslim-Jewish Engagement. Collared peccary P. The Oxford Companion to Food 2nd ed. Both the dromedary the seven-humped camel of Arabia and the Bactrian camel the two-humped camel of Central Asia had been domesticated since before BC. Red brocket M. In addition to providing the Roman Army with its best archers, the Easterners largely Arabs but generally known as 'Syrians' served as Rome's most effective dromedarii or camel-mounted troops. Even salty water can be tolerated, and between drinks it forages far from oases to find food unavailable to other livestock. Somalia a Country Study. White-tailed deer O. Namespaces Article Talk. Do camels lay eggs? Greenwood Publishing Group. View 1 comment. The reason why Cyrus opposed his camels to the enemy's horse was because the horse has a natural dread of the camel, and cannot abide either the sight or the smell of that animal. Archived from the original on 4 August Melissa Stewart. Camel Corps experiment. Is the word camel a short vowel word? ABC News. Consequently, these schools hold that Muslims must perform wudhu ablution before the next time they pray after eating camel meat. -
Cervid Mixed-Species Table That Was Included in the 2014 Cervid RC
Appendix III. Cervid Mixed Species Attempts (Successful) Species Birds Ungulates Small Mammals Alces alces Trumpeter Swans Moose Axis axis Saurus Crane, Stanley Crane, Turkey, Sandhill Crane Sambar, Nilgai, Mouflon, Indian Rhino, Przewalski Horse, Sable, Gemsbok, Addax, Fallow Deer, Waterbuck, Persian Spotted Deer Goitered Gazelle, Reeves Muntjac, Blackbuck, Whitetailed deer Axis calamianensis Pronghorn, Bighorned Sheep Calamian Deer Axis kuhili Kuhl’s or Bawean Deer Axis porcinus Saurus Crane Sika, Sambar, Pere David's Deer, Wisent, Waterbuffalo, Muntjac Hog Deer Capreolus capreolus Western Roe Deer Cervus albirostris Urial, Markhor, Fallow Deer, MacNeil's Deer, Barbary Deer, Bactrian Wapiti, Wisent, Banteng, Sambar, Pere White-lipped Deer David's Deer, Sika Cervus alfredi Philipine Spotted Deer Cervus duvauceli Saurus Crane Mouflon, Goitered Gazelle, Axis Deer, Indian Rhino, Indian Muntjac, Sika, Nilgai, Sambar Barasingha Cervus elaphus Turkey, Roadrunner Sand Gazelle, Fallow Deer, White-lipped Deer, Axis Deer, Sika, Scimitar-horned Oryx, Addra Gazelle, Ankole, Red Deer or Elk Dromedary Camel, Bison, Pronghorn, Giraffe, Grant's Zebra, Wildebeest, Addax, Blesbok, Bontebok Cervus eldii Urial, Markhor, Sambar, Sika, Wisent, Waterbuffalo Burmese Brow-antlered Deer Cervus nippon Saurus Crane, Pheasant Mouflon, Urial, Markhor, Hog Deer, Sambar, Barasingha, Nilgai, Wisent, Pere David's Deer Sika 52 Cervus unicolor Mouflon, Urial, Markhor, Barasingha, Nilgai, Rusa, Sika, Indian Rhino Sambar Dama dama Rhea Llama, Tapirs European Fallow Deer -
02/02/2018 1 Marco Apollonio and Roberta Chirichella
02/02/2018 Marco Apollonio and Roberta Chirichella Department of Veterinary Medicine University of Sassari, Italy First Annual General Meeting of ENETWILD Parma 16-18 January 2018 1 02/02/2018 2005 - 2015 DATA FROM EUROPEAN COUNTRIES: Walter Arnold and Friedrich Reimoser (Austria); Jim Casaer (Belgium); Luděk Bartoš(Czeck R.); Krešimir Krapinec (Croatia); Reidar Andersen (Denmark); Tiit Randveer (Estonia); Vesa Ruusila (Finland); Christine Saint-Andrieux (France); Marco Heurich (Germany); Haritakis Papaioannou (Greece); Csányi Sándor (Hungary); Rory Putman and Peter Watson (Ireland and UK); Francesco Riga (Italy); Jānis Ozoliņš (Latvia); Linas Balčiauskas (Lituania); Dime Melovski (Macedonia); Geert W. T. A. Groot Bruinderink (Netherlands); Atle Mysterud (Norway); Tomasz Borowik (Poland); Carlos Fonseca (Portugal); Istvan Szabo (Romania); Milan Paunović (Serbia); Slavomír Find'o (Slovakia); Boštján Pokorny (Slovenia); Juan Carranza (Spain); Göran Ericsson (Sweden); Reinhard Schnidrig-Petrig (Swizerland). Wild boar distribution in Europe and Near East 2 02/02/2018 WILD BOAR EXTICTION IN EUROPE • SWITZERLAND • BALTIC COUNTRIES • SWEDEN • NORWAY • DENMARK • NETHERLANDS • GREAT BRITAIN • SLOVENIA (ALMOST) Italy (Ghigi A., 1917, 1950) 3 02/02/2018 Italy (Apollonio. et al., 1988) Reintroduction restocking Natural immigration Reintroduction Restocking Natural immigration Autoctonous restocking Restocking Autoctonous Restocking Autoctonous Sus scrofa meridionalis Restocking (with Sus scrofa of Reintroduction different regions) Italy (Apollonio -
The Impact of Lynx and Wolf on Roe Deer Hunting Value in Sweden
The Impact of Lynx and Wolf on Roe Deer Hunting Value in Sweden 2002-2012 KATARINA ELOFSSONa1, TOBIAS HÄGGMARK SVENSSONa aDepartment of Economics, Box 7013, Swedish University of Agricultural Sciences, S-750 07 ABSTRACT Large carnivores provide ecosystem and cultural benefits but also impose costs on livestock owners, due to predation, and on hunters, due to the competition for game. The benefits as well as the costs that accrue to livestock owners have been studied, but this is not the case for the costs that accrue to hunters. The aim of this paper was to identify the impact of lynx (Lynx lynx) and wolf (Canis lupus) on roe deer (Capreolus capreolus) hunting value. We applied a production function approach, using a bioeconomic model where the number of roe deer harvested was assumed to be jointly determined by hunting effort, abundance of predators, availability of other game, and climatic conditions. The impact of the predators on the roe deer harvests was estimated econometrically, and carnivore impacts for a constant and adjusted, steady state hunting effort were derived. The results showed that the marginal cost in terms of hunting values foregone varied between the counties and ranged between 18,000 and 58,000 EUR for lynx and 79,000 and 336,000 EUR for wolf. Larger costs were found in counties where the hunting effort was high, mainly located in south Sweden. The regional variation in costs has implications for decisions on policies affecting the regional distribution of wolf and lynx. KEY WORDS costs, hunting, lynx, moose, predation, production function approach, roe deer, wolves. -
What Is the Risk of a Cervid TSE Being Introduced from Norway to Britain?
What is the risk of a cervid TSE being introduced from Norway into Great Britain? Qualitative Risk Assessment June 2018 © Crown copyright 2018 You may re-use this information (excluding logos) free of charge in any format or medium, under the terms of the Open Government Licence v.3. To view this licence visit www.nationalarchives.gov.uk/doc/open-government-licence/version/3/ or email [email protected] This publication is available at www.gov.uk/government/publications Any enquiries regarding this publication should be sent to us at [[email protected]] www.gov.uk/defra Contents Summary ............................................................................................................................. 1 Acknowledgements .............................................................................................................. 3 Background .......................................................................................................................... 4 Hazard identification ............................................................................................................ 5 Risk Question .................................................................................................................... 11 Risk Assessment ............................................................................................................... 12 Terminology related to the assessed level of risk ........................................................... 12 Entry assessment ..........................................................................................................