Eurasian Lynx Reintroduction in Scotland
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VII. Bodies, Institutes and Centres
VII. Bodies, Institutes and Centres Member state Approval List of bodies, institutes and centres approved for intra- Version Date: UK date Community trade in animals as defined in Article 2(1)(c) of August 2017 Directive 92/65/EEC Approval Approval Name Contact details Remarks number Date AB/21/08/001 13/03/17 Ahmed, A 46 Wyvern Road, Sutton Coldfield, First Approval: West Midlands, B74 2PT 23/10/09 AB/17/98/026 09/03/17 Africa Alive Whites Lane, Kessingland, Suffolk, First Approval: NR33 7TF 24/03/98 AB/17/17/005 15/06/17 All Things Wild Station Road, Honeybourne, First Approval: Evesham, Worcestershire, WR11 7QZ 15/06/17 AB/78/14/002 15/08/16 Amazonia Strathclyde Country Park, Hamilton First Approval: Road, Motherwell, North Lanarkshire, 28/05/14 ML1 3RT AB/29/12/003 06/04/17 Amazon World Zoo Park Watery Lane, Newchurch, Isle of First Approval: Wight, PO36 0LX 15/06/12 AB/17/08/065 08/03/17 Amazona Zoo Hall Road, Cromer, Norfolk, NR27 9JG First Approval: 07/04/08 AB/29/15/003 24/02/17 Animal Management Sparsholt College, Sparsholt, First Approval: Centre Winchester, Hampshire, SO21 2NF 24/02/15 AB/12/15/001 07/02/17 The Animal Zone Rodbaston College, Penkridge, First Approval: Staffordshire, ST19 5PH 16/01/15 AB/07/16/001 10/10/16 Askham Bryan Wildlife Askham Bryan College, Askham First Approval: & Conservation Park Bryan, York, YO23 3FR 10/10/16 AB/07/13/001 17/10/16 [email protected]. First Approval: gov.uk 15/01/13 AB/17/94/001 19/01/17 Banham Zoo (ZSEA Ltd) The Grove, Banham, Norwich, First Approval: Norfolk, NR16 -
Eurasian Lynx – Your Essential Brief
Eurasian lynx – Your essential brief Background Q: Are lynx native to Britain? A: Based on archaeological evidence, the range of the Eurasian lynx (Lynx lynx) included Britain until at least 1,300 years ago. It is difficult to be precise about when or why lynx became extinct here, but it was almost certainly related to human activity – deforestation removed their preferred habitat, and also that of their prey, thus reducing prey availability. These declines in prey species may have been exacerbated by human hunting. Q: Where do they live now? A: Across Europe, Scandinavia, Russia, northern China and Southeast Asia. The range used to include other areas of Western Europe, including Britain, where they are no longer present. Q: How many are there? A: There are thought to be around 50,000 in the world, of which 9,000 – 10,000 live in Europe. They are considered to be a species of least concern by the IUCN. Modern range of the Eurasian lynx Q: How big are they? A: Lynx are on average around 1m in length, 75cm tall and around 20kg, with the males being slightly larger than the females. They can live to 15 years old, but this is rare in the wild. Q: What do they eat? A: The preferred prey of the lynx are the smaller deer species, primarily the roe deer. Lynx may also prey upon other deer species, including chamois, sika deer, smaller red deer, muntjac and fallow deer. Q: Do they eat other things? A: Yes. Lynx prey on many other species when their preferred prey is scarce, including rabbits, hares, foxes, wildcats, squirrel, pine marten, domestic pets, sheep, goats and reared gamebirds. -
Status of Large Carnivores in Serbia
Status of large carnivores in Serbia Duško Ćirović Faculty of Biology University of Belgrade, Belgrade Status and threats of large carnivores in Serbia LC have differend distribution, status and population trends Gray wolf Eurasian Linx Brown Bear (Canis lupus) (Lynx lynx ) (Ursus arctos) Distribution of Brown Bear in Serbia Carpathian Dinaric-Pindos East Balkan Population status of Brown Bear in Serbia Dinaric-Pindos: Distribution 10000 km2 N=100-120 Population increase Range expansion Carpathian East Balkan: Distribution 1400 km2 Dinaric-Pindos N= a few East Balkan Population trend: unknown Carpathian: Distribution 8200 km2 N=8±2 Population stable Legal status of Brown Bear in Serbia According Law on Protection of Nature and the Law on Game and Hunting brown bear in Serbia is strictly protected species. He is under the centralized jurisdiction of the Ministry of Environmental Protection Treats of Brown Bear in Serbia Intensive forestry practice and infrastructure development . Illegal killing Low acceptance due to fear for personal safety Distribution of Gray wolf in Serbia Carpathian Dinaric-Pindos East Balkan Population status of Gray wolf in Serbia Dinaric-Balkan: 2 Carpathian Distribution cca 43500 km N=800-900 Population - stabile/slight increasingly Dinaric Range - slight expansion Carpathian: Distribution 480 km2 (was) Population – a few Population status of Gray wolf in Serbia Carpathian population is still undefined Carpathian Peri-Carpathian Legal status of Gray wolf in Serbia According the Law on Game and Hunting the gray wolf in majority pars of its distribution (south from Sava and Danube rivers) is game species with closing season from April 15th to July 1st. -
ATIC0943 {By Email}
Animal and Plant Health Agency T 0208 2257636 Access to Information Team F 01932 357608 Weybourne Building Ground Floor Woodham Lane www.gov.uk/apha New Haw Addlestone Surrey KT15 3NB Our Ref: ATIC0943 {By Email} 4 October 2016 Dear PROVISION OF REQUESTED INFORMATION Thank you for your request for information about zoos which we received on 26 September 2016. Your request has been handled under the Freedom of Information Act 2000. The information you requested and our response is detailed below: “Please can you provide me with a full list of the names of all Zoos in the UK. Under the classification of 'Zoos' I am including any place where a member of the public can visit or observe captive animals: zoological parks, centres or gardens; aquariums, oceanariums or aquatic attractions; wildlife centres; butterfly farms; petting farms or petting zoos. “Please also provide me the date of when each zoo has received its license under the Zoo License act 1981.” See Appendix 1 for a list that APHA hold on current licensed zoos affected by the Zoo License Act 1981 in Great Britain (England, Scotland and Wales), as at 26 September 2016 (date of request). The information relating to Northern Ireland is not held by APHA. Any potential information maybe held with the Department of Agriculture, Environment and Rural Affairs Northern Ireland (DAERA-NI). Where there are blanks on the zoo license start date that means the information you have requested is not held by APHA. Please note that the Local Authorities’ Trading Standard departments are responsible for administering and issuing zoo licensing under the Zoo Licensing Act 1981. -
Prey Density, Environmental Productivity and Home-Range Size in the Eurasian Lynx (Lynx Lynx)
J. Zool., Lond. (2005) 265, 63–71 C 2005 The Zoological Society of London Printed in the United Kingdom DOI:10.1017/S0952836904006053 Prey density, environmental productivity and home-range size in the Eurasian lynx (Lynx lynx) Ivar Herfindal1, John D. C. Linnell2*, John Odden2, Erlend Birkeland Nilsen1 and Reidar Andersen1,2 1 Department of Biology, Norwegian University of Science and Technology, N-7491 Trondheim, Norway 2 Norwegian Institute for Nature Research, Tungasletta 2, N-7485 Trondheim, Norway (Accepted 19 May 2004) Abstract Variation in size of home range is among the most important parameters required for effective conservation and management of a species. However, the fact that home ranges can vary widely within a species makes data transfer between study areas difficult. Home ranges of Eurasian lynx Lynx lynx vary by a factor of 10 between different study areas in Europe. This study aims to try and explain this variation in terms of readily available indices of prey density and environmental productivity. On an individual scale we related the sizes of 52 home ranges, derived from 23 (9:14 male:female) individual resident lynx obtained from south-eastern Norway, with an index of density of roe deer Capreolus capreolus. This index was obtained from the density of harvested roe deer within the municipalities covered by the lynx home ranges. We found a significant negative relationship between harvest density and home- range size for both sexes. On a European level we related the sizes of 111 lynx (48:63 male: female) from 10 study sites to estimates derived from remote sensing of environmental productivity and seasonality. -
Current Status of the Eurasian Lynx. Cat News. (2016)
ISSN 1027-2992 I Special Issue I N° 10 | Autumn 2016 CatsCAT in Iran news 02 CATnews is the newsletter of the Cat Specialist Group, a component Editors: Christine & Urs Breitenmoser of the Species Survival Commission SSC of the International Union Co-chairs IUCN/SSC for Conservation of Nature (IUCN). It is published twice a year, and is Cat Specialist Group available to members and the Friends of the Cat Group. KORA, Thunstrasse 31, 3074 Muri, Switzerland For joining the Friends of the Cat Group please contact Tel ++41(31) 951 90 20 Christine Breitenmoser at [email protected] Fax ++41(31) 951 90 40 <[email protected]> Original contributions and short notes about wild cats are welcome Send <[email protected]> contributions and observations to [email protected]. Guidelines for authors are available at www.catsg.org/catnews Cover Photo: From top left to bottom right: Caspian tiger (K. Rudloff) This Special Issue of CATnews has been produced with support Asiatic lion (P. Meier) from the Wild Cat Club and Zoo Leipzig. Asiatic cheetah (ICS/DoE/CACP/ Panthera) Design: barbara surber, werk’sdesign gmbh caracal (M. Eslami Dehkordi) Layout: Christine Breitenmoser & Tabea Lanz Eurasian lynx (F. Heidari) Print: Stämpfli Publikationen AG, Bern, Switzerland Pallas’s cat (F. Esfandiari) Persian leopard (S. B. Mousavi) ISSN 1027-2992 © IUCN/SSC Cat Specialist Group Asiatic wildcat (S. B. Mousavi) sand cat (M. R. Besmeli) jungle cat (B. Farahanchi) The designation of the geographical entities in this publication, and the representation of the material, do not imply the expression of any opinion whatsoever on the part of the IUCN concerning the legal status of any country, territory, or area, or its authorities, or concerning the delimitation of its frontiers or boundaries. -
In Our Hands: the British and UKOT Species That Large Charitable Zoos & Aquariums Are Holding Back from Extinction (AICHI Target 12)
In our hands: The British and UKOT species that Large Charitable Zoos & Aquariums are holding back from extinction (AICHI target 12) We are: Clifton & West of England Zoological Society (Bristol Zoo, Wild Places) est. 1835 Durrell Wildlife Conservation Trust (Jersey Zoo) est. 1963 East Midland Zoological Society (Twycross Zoo) est. 1963 Marwell Wildlife (Marwell Zoo) est. 1972 North of England Zoological Society (Chester Zoo) est. 1931 Royal Zoological Society of Scotland (Edinburgh Zoo, Highland Wildlife Park) est. 1913 The Deep est. 2002 Wild Planet Trust (Paignton Zoo, Living Coasts, Newquay Zoo) est. 1923 Zoological Society of London (ZSL London Zoo, ZSL Whipsnade Zoo) est. 1826 1. Wildcat 2. Great sundew 3. Mountain chicken 4. Red-billed chough 5. Large heath butterfly 6. Bermuda skink 7. Corncrake 8. Strapwort 9. Sand lizard 10. Llangollen whitebeam 11. White-clawed crayfish 12. Agile frog 13. Field cricket 14. Greater Bermuda snail 15. Pine hoverfly 16. Hazel dormouse 17. Maiden pink 18. Chagos brain coral 19. European eel 2 Executive Summary: There are at least 76 species native to the UK, Crown Dependencies, and British Overseas Territories which Large Charitable Zoos & Aquariums are restoring. Of these: There are 20 animal species in the UK & Crown Dependencies which would face significant declines or extinction on a global, national, or local scale without the action of our Zoos. There are a further 9 animal species in the British Overseas Territories which would face significant declines or extinction without the action of our Zoos. These species are all listed as threatened on the IUCN Red List. There are at least 19 UK animal species where the expertise of our Zoological Institutions is being used to assist with species recovery. -
Predicting Global Population Connectivity and Targeting Conservation Action for Snow Leopard Across Its Range
Ecography 39: 419–426, 2016 doi: 10.1111/ecog.01691 © 2015 e Authors. Ecography © 2015 Nordic Society Oikos Subject Editor: Bethany Bradley. Editor-in-Chief: Miguel Araújo. Accepted 27 April 2015 Predicting global population connectivity and targeting conservation action for snow leopard across its range Philip Riordan, Samuel A. Cushman, David Mallon, Kun Shi and Joelene Hughes P. Riordan ([email protected]) and J. Hughes, Dept of Zoology, Univ. of Oxford, South Parks Road, Oxford, OX1 3PS, UK. – S. A. Cushman, US Forest Service, Rocky Mountain Research Station, 800 E Beckwith, Missoula, MT 59801, USA. – D. Mallon, Division of Biology and Conservation Ecology, School of Science and the Environment, Manchester Metropolitan Univ., Manchester, M1 5GD, UK. – K. Shi and PR, Wildlife Inst., College of Nature Conservation, Beijing Forestry Univ., 35, Tsinghua-East Road, Beijing 100083, China. Movements of individuals within and among populations help to maintain genetic variability and population viability. erefore, understanding landscape connectivity is vital for effective species conservation. e snow leopard is endemic to mountainous areas of central Asia and occurs within 12 countries. We assess potential connectivity across the species’ range to highlight corridors for dispersal and genetic flow between populations, prioritizing research and conservation action for this wide-ranging, endangered top-predator. We used resistant kernel modeling to assess snow leopard population connectivity across its global range. We developed an expert-based resistance surface that predicted cost of movement as functions of topographical complexity and land cover. e distribution of individuals was simulated as a uniform density of points throughout the currently accepted global range. -
An Evaluation of Conservation by UK Zoos RESULTS
ANIMAL ARK OR SINKINGAn evaluation of SHIP? conservation by UK zoos Photo © Dr Joseph Tobias, University of Oxford Photo © Charles Smith, United States Fish and Wildlife Service July 2007 At least 5,624 species of vertebrate animals are Annual Reports, published accounts and animal threatened with extinction worldwide1. inventories5; BIAZA6 published data; data on Humankind’s contribution to the rapid loss of the European Co-operative Breeding Programmes (EEPs earth’s flora and fauna is now a widely & ESPs7) from EAZA8; ICM Research public opinion acknowledged phenomenon. To date, 190 survey (May 2007)9. countries have pledged to make a concerted effort to conserve the world’s threatened species Full details are available in Born Free reports: Is the by signing up to the Convention on Biological Ark Afloat? Captivity and Ex Situ Conservation in UK Diversity. Zoos (2007) and Committed to Conservation? An Overview of the Consortium of Charitable Zoos’ In The involvement of zoos in the conservation of Situ Conservation Dividend (2007). Both reports biodiversity, and specifically ex situ conservation2, available at www.bornfree.org.uk/zoocon became a legal obligation in Europe in 2002 with the implementation of the European Zoos Directive. The Directive was fully incorporated into UK zoo The IUCN Red List of Threatened legislation in 2003. Perhaps recognising an SpeciesTM compared to species in the CCZ opportunity to refute growing scepticism over the The IUCN Red List catalogues and highlights those keeping of animals in captivity, zoos assumed the taxa facing a higher risk of global extinction. In this role of animal ‘arks’ and promoted their new review, the Red List status for all mammal, bird and conservation purpose. -
Return of a Lost Structure in the Evolution of Felid Dentition Revisited: a Devoevo Perspective on the Irreversibility of Evolution
bioRxiv preprint doi: https://doi.org/10.1101/2021.02.04.429820; this version posted February 5, 2021. The copyright holder for this preprint (which was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission. RUNNING HEAD: LYNX M2 AND IRREVERSIBILE EVOLUTION Return of a lost structure in the evolution of felid dentition revisited: A DevoEvo perspective on the irreversibility of evolution Vincent J. Lynch Department of Biological Sciences, University at Buffalo, SUNY, 551 Cooke Hall, Buffalo, NY, 14260, USA. Correspondence: [email protected] 1 bioRxiv preprint doi: https://doi.org/10.1101/2021.02.04.429820; this version posted February 5, 2021. The copyright holder for this preprint (which was not certified by peer review) is the author/funder. All rights reserved. No reuse allowed without permission. RUNNING HEAD: LYNX M2 AND IRREVERSIBILE EVOLUTION Abstract There is a longstanding interest in whether the loss of complex characters is reversible (so-called “Dollo’s law”). Reevolution has been suggested for numerous traits but among the first was Kurtén (1963), who proposed that the presence of the second lower molar (M2) of the Eurasian lynx (Lynx lynx) was a violation of Dollo’s law because all other Felids lack M2. While an early and often cited example for the reevolution of a complex trait, Kurtén (1963) and Werdelin (1987) used an ad hoc parsimony argument to support their proposition that M2 reevolved in Eurasian lynx. Here I revisit the evidence that M2 reevolved in Eurasian lynx using explicit parsimony and maximum likelihood models of character evolution and find strong evidence that Kurtén (1963) and Werdelin (1987) were correct – M2 reevolved in Eurasian lynx. -
Conservation of Snow Leopards: Spill-Over Benefits for Other Carnivores?
Conservation of snow leopards: spill-over benefits for other carnivores? J USTINE S. ALEXANDER,JEREMY J. CUSACK,CHEN P ENGJU S HI K UN and P HILIP R IORDAN Abstract In high-altitude settings of Central Asia the protection will also benefit many other species (Noss, Endangered snow leopard Panthera uncia has been recog- ; Andelman & Fagan, ). Top predators often nized as a potential umbrella species. As a first step in asses- meet this criterion (Sergio et al., ; Dalerum et al., sing the potential benefits of snow leopard conservation for ; Rozylowicz et al., ), with many large carnivores other carnivores, we sought a better understanding of the additionally possessing charismatic qualities and wide pub- presence of other carnivores in areas occupied by snow leo- lic recognition that can attract disproportionate conserva- pards in China’s Qilianshan National Nature Reserve. We tion investments (Sergio et al., ; Karanth & Chellam, used camera-trap and sign surveys to examine whether ). The flagship status of such carnivores can bring in- other carnivores were using the same travel routes as snow direct benefits to other species that are neglected or over- leopards at two spatial scales. We also considered temporal looked, by highlighting common threats and emphasizing interactions between species. Our results confirm that other their mutual dependence. A fundamental step in identifying carnivores, including the red fox Vulpes vulpes, grey wolf and quantifying potential benefits for other species is to Canis lupus, Eurasian lynx Lynx lynx and dhole Cuon alpinus, demonstrate the spatial extent of co-occurrence in the occur along snow leopard travel routes, albeit with low detec- area of interest (Andelman & Fagan, ). -
West Midland Safari Park
ReWyre Initiative West Midland Safari Park Economic Impact Study (EIS) - Final Draft February 2011 Commercial in Confidence AMION Consulting Limited Horton House, Exchange Flags, Liverpool L2 3YL ReWyre Initiative West Midland Safari Park Economic Impact Study (EIS) - Final Draft February 2011 ReWyre Initiative West Midland Safari Park Economic Impact Study (EIS) - Final Draft February 2011 Reviewed and approved by: Signature(s): Name(s): Graham Russell Job Title(s): Partner Director Date: February 2011 AMION Consulting is the trading name of AMION Consulting Limited Registered Office: Langtons, The Plaza, 100 Old Hall Street, Liverpool L3 9QJ Company No: 3909897 Tel: 0151 227 5563 Ref: K:\CLIENTS\ReWyre\Deliverables\EIS report\WMSP EIS (Final Draft) 030211.doc ReWyre Initiative West Midland Safari Park Economic Impact Study (EIS) - Final Draft February 2011 Contents 1 Introduction ................................................................................................................... 1 1.1 Overview ....................................................................................................................................... 1 1.2 Purpose and objectives of the EIS ................................................................................................. 1 1.3 Approach ....................................................................................................................................... 2 1.4 Structure of the report .................................................................................................................