Wild Deer Issues in Britain and Mainland Europe John Fletcher
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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. -
Fitzhenry Yields 2016.Pdf
Stellenbosch University https://scholar.sun.ac.za ii DECLARATION By submitting this dissertation electronically, I declare that the entirety of the work contained therein is my own, original work, that I am the sole author thereof (save to the extent explicitly otherwise stated), that reproduction and publication thereof by Stellenbosch University will not infringe any third party rights and that I have not previously in its entirety or in part submitted it for obtaining any qualification. Date: March 2016 Copyright © 2016 Stellenbosch University All rights reserved Stellenbosch University https://scholar.sun.ac.za iii GENERAL ABSTRACT Fallow deer (Dama dama), although not native to South Africa, are abundant in the country and could contribute to domestic food security and economic stability. Nonetheless, this wild ungulate remains overlooked as a protein source and no information exists on their production potential and meat quality in South Africa. The aim of this study was thus to determine the carcass characteristics, meat- and offal-yields, and the physical- and chemical-meat quality attributes of wild fallow deer harvested in South Africa. Gender was considered as a main effect when determining carcass characteristics and yields, while both gender and muscle were considered as main effects in the determination of physical and chemical meat quality attributes. Live weights, warm carcass weights and cold carcass weights were higher (p < 0.05) in male fallow deer (47.4 kg, 29.6 kg, 29.2 kg, respectively) compared with females (41.9 kg, 25.2 kg, 24.7 kg, respectively), as well as in pregnant females (47.5 kg, 28.7 kg, 28.2 kg, respectively) compared with non- pregnant females (32.5 kg, 19.7 kg, 19.3 kg, respectively). -
Wildlife Guide How Many of These Have You Spotted in the Forest?
FOREST OF DEAN / SAVERNAKE FOREST / SNOWDONIA Wildlife GuidE How many of these have you spotted in the forest? SPECIES FOREST OF DEAN Sheep The Forest of Dean is famous for its large population of free roaming sheep derived from many breeds and include welsh mountain, speckled faced or cheviots with the occasional kerry or ryeland. The sheep have been around for hundreds of years and are likely to continue to be part of the Forest scenery. Best time to see sheep: All year round Deer In Norman times, the Forest was protected as a games reserve where red, roe and fallow deer and wild boar were hunted. Today, it is only fallow or roe deer that can be found. Early morning or dusk is the time when you are most likely to see deer in the Forest. Best time to see Fallow deer: All year round Wild Boar Wild boar were once common in England, but were hunted to extinction at least 300 years ago. In recent years, small populations of wild boar have become established again in the wild, with the Forest of Dean's wild boar poppulation now the largest that exists in England. Boars are best spotted early morning or in the evenings in the Forest of Dean. Best time to see Wild Boar: All year round SAVERNAKE FOREST A small bird of prey, the Sparrowhawk is perfectly adpated for hunting birds in small enclosed woodlands. Listen out for the alarm calls of smaller birds as they spot a Sparrowhawk, alerting other birds in the area to the danger. -
Exotic Big Game: a Controversial Resource Stephen Demarals, David A
RANGELANDS12(2), April 1990 121 operation was substantially higher because of the addi- allocating15% of the fixed vehiclecosts to the enterprise, tional driving associated with guiding hunters and may the break-even charge is $77.90 per hunter day. In com- also involve picking up hunters in town. Providing guid- paring the break-even chargeswith the estimated fee of ing services requiresadditional labor and includesa cost $111.93, it appears this option is also profitable. for the operator to becomelicensed as an outfitter and Discussion and Conclusions This is a in if the guide. requirement Wyoming hunting Additional income was the reason cited enterpriseused landsnot owned by the operator, includ- primary by lands, or if are hired the operators for beginning a recreation enterprise. While ing public guides by operator. ranch recreationhas the to earna realiz- The budget for Example 2 is shown in Table 2. In this potential profit, the breakeven is hunter ing that potential dependson each operator'ssituation. example charge $24.81 per day. evaluate his the break-even with the estimated fee Eachoperator must particularsituation and Comparing charge consider suchas with the of $36.32 that this of any subjectivefactors, dealing per day (Table 1) suggests type when a ranch recreation is also public, assessing the potential of operation profitable. When landowners and are able to Example 3 describes an agricultural operation that pro- enterprise. recognize realize a situation and other vides 14,400 acres for deer and The profitable through hunting antelope hunting. recreation activitieson their land, wildlife habitat will be hunting enterprise operates for 28 days with thirty-five viewed as an asset and not a customershunting an average of four days per hunteror liability. -
Ecology of Red Deer a Research Review Relevant to Their Management in Scotland
Ecologyof RedDeer A researchreview relevant to theirmanagement in Scotland Instituteof TerrestrialEcology Natural EnvironmentResearch Council á á á á á Natural Environment Research Council Institute of Terrestrial Ecology Ecology of Red Deer A research review relevant to their management in Scotland Brian Mitchell, Brian W. Staines and David Welch Institute of Terrestrial Ecology Banchory iv Printed in England by Graphic Art (Cambridge) Ltd. ©Copyright 1977 Published in 1977 by Institute of Terrestrial Ecology 68 Hills Road Cambridge CB2 11LA ISBN 0 904282 090 Authors' address: Institute of Terrestrial Ecology Hill of Brathens Glassel, Banchory Kincardineshire AB3 4BY Telephone 033 02 3434. The Institute of Terrestrial Ecology (ITE) was established in 1973, from the former Nature Conservancy's research stations and staff, joined later by the Institute of Tree Biology and the Culture Centre of Algae and Protozoa. ITE contributes to and draws upon the collective knowledge of the fourteen sister institutes which make up the Natural Environment Research Council, spanning all the environmental sciences. The Institute studies the factors determining the structure, composition and processes of land and freshwater systems, and of individual plant and animal species. It is developing a Sounder scientific basis for predicting and modelling environmental trends arising from natural or man-made change. The results of this research are available to those responsible for the protection, management and wise use of our natural resources. Nearly half of ITE'Swork is research commissioned by customers, such as the Nature Conservancy Council who require information for wildlife conservation, the Forestry Commission and the Department of the Environment. The remainder is fundamental research supported by NERC. -
Species Fact Sheet: Sika Deer (Cervus Nippon) [email protected] 023 8023 7874
Species Fact Sheet: Sika Deer (Cervus nippon) [email protected] www.mammal.org.uk 023 8023 7874 Quick Facts Recognition: A medium-sized deer. Has a similar spotted coat to fallow deer in summer, but usually is rougher, thicker, dark grey-brown in winter. Tail is shorter than fallow deer, but with similar white “target” and black margins. Usually has a distinctive “furrowed brow” look, and if seen well, evident white spots on the limbs, marking the site of pedal glands. Males have rounded, not pamate, antlers, looking like a small version of a red deer stag’s antlers. Size: 138-179 cm; Tail length: 14-21cm; Shoulder height 50-120 cm. Weight: Males 40-63kg; females 31-44kg. Life Span: Maximum recorded lifespan in captivity is 26 years; 16 in the wild. Distribution & Habitat Sika are native to SE China, including Taiwan, Korea and Japan. It was introduced to Powerscourt Park, Co Wicklow, Ireland, in 1860, and to London Zoo. Sika then spread to many other parks and escaped or were deliberately released; in some cases they were deliberately released into surrounding woodlands to be hunted on horseback. This resulted in feral populations S England (especially Dorset and the New Forest), in the Forest of Bowland and S Cumbria, and, especially, in Scotland. It is still spreading. Its preference for conifer plantations, especially the thick young stages, has been a big advantage to it. It can reach densities up to 45/km2 in prime habitat. General Ecology Behaviour They typically live in small herds of 6-7 animals, at least in more open habitats, but in dense cover may only live in small groups of 1-3 only. -
Estimating Sika Deer Abundance Using Camera Surveys
ESTIMATING SIKA DEER ABUNDANCE USING CAMERA SURVEYS by Sean Q. Dougherty A thesis submitted to the Faculty of the University of Delaware in partial fulfillment of the requirements for the degree of Master of Science in Wildlife Ecology Fall 2010 Copyright 2010 Sean Q. Dougherty All Rights Reserved ESTIMATING SIKA DEER ABUNDANCE USING CAMERA SURVEYS by Sean Q. Dougherty Approved: ___________________________________________________________ Jacob L. Bowman, Ph.D. Professor in charge of thesis on behalf of the Advisory Committee Approved: ___________________________________________________________ Douglas W. Tallamy, Ph.D. Chair of the Department of Entomology and Wildlife Ecology Approved: ___________________________________________________________ Robin W. Morgan, Ph.D. Dean of the College of Agriculture & Natural Resources Approved: ___________________________________________________________ Charles G. Riordan, Ph.D. Vice Provost for Graduate and Professional Education ACKNOWLEDGMENTS I would like to thank the funding sources that made my research possible; the College of Agriculture and Natural Resources Research Partnership Grant, the University of Delaware Graduate School, the University of Delaware McNair Scholar’s program, Maryland Department of Natural Resources, University of Delaware Department of Entomology and Wildlife Ecology, the West Virginia University McNair Scholar’s program, and Tudor Farms LLC. I would also like to thank my committee members Jake Bowman, Greg Shriver, Brian Eyler, and the staff Tudor Farms LLC for all the support and invaluable advice with all aspects of my research and fieldwork. All my friends and family have been especially valuable for their love and support throughout all my endeavors. Finally, I have to acknowledge Traci Hunt for her support, advice and hours of attentiveness throughout the writing portion of my thesis. -
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 -
Reeves' Muntjac Populations Continue to Grow and Spread Across Great
European Journal of Wildlife Research (2021) 67:34 https://doi.org/10.1007/s10344-021-01478-2 ORIGINAL ARTICLE Reeves’ muntjac populations continue to grow and spread across Great Britain and are invading continental Europe Alastair I. Ward1 & Suzanne Richardson1 & Joachim Mergeay2,3 Received: 27 August 2020 /Revised: 18 November 2020 /Accepted: 5 March 2021 # The Author(s) 2021 Abstract The appropriate response for controlling an invasive non-native species depends on the extent to which its invasion has progressed, which can be revealed by information on its distribution and abundance. Reeves’ muntjac is a native deer to China and Taiwan, but has been introduced and become well-established in Great Britain. Moreover, in recent years, reports and verified records in the wild from other European countries have become more frequent. We reviewed the status of Reeves’ muntjac in Britain and evaluated its national range expansion from 2002 to 2016. While the British population appears to have tripled in size since 1995, the rate at which it has expanded its range seems to have peaked at approximately 12% per year between 2002 and 2005 and has since declined. We also consolidated observations on its international distribution, including a conservative evaluation of its presence in zoological collections. We predict that this species could expand its range to include every European country, although the availability of suitable landcover and climate is likely to vary substantially between countries. To prevent the significant impacts to conservation interests that have been observed in Great Britain from extending across Europe, national administrations should consider eradicating Reeves’ muntjac while that is still feasible. -
The European Fallow Deer (Dama Dama Dama)
Heredity (2017) 119, 16–26 OPEN Official journal of the Genetics Society www.nature.com/hdy ORIGINAL ARTICLE Strong population structure in a species manipulated by humans since the Neolithic: the European fallow deer (Dama dama dama) KH Baker1, HWI Gray1, V Ramovs1, D Mertzanidou2,ÇAkın Pekşen3,4, CC Bilgin3, N Sykes5 and AR Hoelzel1 Species that have been translocated and otherwise manipulated by humans may show patterns of population structure that reflect those interactions. At the same time, natural processes shape populations, including behavioural characteristics like dispersal potential and breeding system. In Europe, a key factor is the geography and history of climate change through the Pleistocene. During glacial maxima throughout that period, species in Europe with temperate distributions were forced south, becoming distributed among the isolated peninsulas represented by Anatolia, Italy and Iberia. Understanding modern patterns of diversity depends on understanding these historical population dynamics. Traditionally, European fallow deer (Dama dama dama) are thought to have been restricted to refugia in Anatolia and possibly Sicily and the Balkans. However, the distribution of this species was also greatly influenced by human-mediated translocations. We focus on fallow deer to better understand the relative influence of these natural and anthropogenic processes. We compared modern fallow deer putative populations across a broad geographic range using microsatellite and mitochondrial DNA loci. The results revealed highly insular populations, depauperate of genetic variation and significantly differentiated from each other. This is consistent with the expectations of drift acting on populations founded by small numbers of individuals, and reflects known founder populations in the north. -
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