Trophy Hunting, Size, Rarity and Willingness to Pay: Inter–Specific Analyses of Trophy Prices Require Reliable Specific Data
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The Mediterranean Forests Are Extraordinarily Beautiful, a Fascinating an Extraordinary Patrimony of Wealth Whose Conservation Can Be Highly Controversy
THE editerraneanFORESTS mA NEW CONSERVATION STRATEGY 1 3 2 4 5 6 the unveiled a meeting point the mediterranean: amazing plant an unknown millennia forests on the global 200 the terrestrial current a brand new the state of WWF a new approach wealth of the of nature a sea of forests diversity animal world of human the wane in the sub-ecoregions mediterranean tool: the gap mediterranean in action for forest mediterranean and civilisations interaction with mediterranean in the forest cover analysis forests protection forests forests mediterranean 23 46 81012141617 18 19 22 24 7 1 Argania spinosa fruits, Essaouira, Morocco. Credit: WWF/P. Regato 2 Reed-parasol maker, Tunisia. Credit: WWF-Canon/M. Gunther 3 Black-shouldered Kite. Credit: Francisco Márquez 4 Endemic mountain Aquilegia, Corsica. Credit: WWF/P. Regato 5 Sacred ibis. Credit: Alessandro Re 6 Joiner, Kure Mountains, Turkey. Credit: WWF/P. Regato 7 Barbary ape, Morocco. Credit: A. & J. Visage/Panda Photo It is like no other region on Earth. Exotic, diverse, roamed by mythical WWF Mediterranean Programme Office launched its campaign in 1999 creatures, deeply shaped by thousands of years of human intervention, the to protect 10 outstanding forest sites among the 300 identified through cradle of civilisations. a comprehensive study all over the region. When we talk about the Mediterranean region, you could be forgiven for The campaign has produced encouraging results in countries such as Spain, thinking of azure seas and golden beaches, sun and sand, a holidaymaker’s Turkey, Croatia and Lebanon. NATURE AND CULTURE, of forest environments in the region. But in recent times, the balance AN INTIMATE RELATIONSHIP Long periods of considerable forest between nature and humankind has paradise. -
Rewilding Watersheds: Using Nature's Algorithms to Fix Our Broken Rivers
Marine and Freshwater Research © CSIRO 2021 https://doi.org/10.1071/MF20335_AC Supplementary material Rewilding watersheds: using nature’s algorithms to fix our broken rivers Natalie K. RideoutA,G,1, Bernhard WegscheiderB,1, Matilda KattilakoskiA, Katie M. McGeeC,D, Wendy A. MonkE, and Donald J. BairdF ACanadian Rivers Institute, Department of Biology, University of New Brunswick, 10 Bailey Drive, Fredericton, NB, E3B 5A3, Canada. BCanadian Rivers Institute, Faculty of Forestry and Environmental Management, University of New Brunswick, 2 Bailey Drive, Fredericton, NB, E3B 5A3, Canada. CEnvironment and Climate Change Canada, Canada Centre for Inland Waters, 867 Lakeshore Road, Burlington, ON, L7R 4A6, Canada. DCentre for Biodiversity Genomics and Department of Integrative Biology, University of Guelph, 50 Stone Road E., Guelph, ON, N1G 2W1, Canada. EEnvironment and Climate Change Canada @ Canadian Rivers Institute, Faculty of Forestry and Environmental Management, University of New Brunswick, 2 Bailey Drive, Fredericton, NB, E3B 5A3, Canada. FEnvironment and Climate Change Canada @ Canadian Rivers Institute, Department of Biology, University of New Brunswick, 10 Bailey Drive, Fredericton, NB, E3B 5A3, Canada. GCorresponding author. Email: [email protected] 1These authors contributed equally to the work. Page 1 of 49 Table S1. References linking ecosystem functions with rewilding goals, providing supporting evidence for Fig. 1 Restore natural flow Mitigate climate Restore riparian Re-introduce Improve water quality Reduce habitat and sediment regime warming vegetation extirpated species fragmentation 1 Metabolism Aristi et al. 2014 Song et al. 2008 Wassenaar et al. 2010 Huang et al. 2018 Jankowski and Schindler 2019 2 Decomposition Delong 2010 Perry et al. 2011 Delong 2010 Wenisch et al. -
Favourableness and Connectivity of a Western Iberian Landscape for the Reintroduction of the Iconic Iberian Ibex Capra Pyrenaica
Favourableness and connectivity of a Western Iberian landscape for the reintroduction of the iconic Iberian ibex Capra pyrenaica R ITA T. TORRES,JOÃO C ARVALHO,EMMANUEL S ERRANO,WOUTER H ELMER P ELAYO A CEVEDO and C ARLOS F ONSECA Abstract Traditional land use practices declined through- Keywords Capra pyrenaica, environmental favourableness, out many of Europe’s rural landscapes during the th cen- graph theory, habitat connectivity, Iberian ibex, reintroduc- tury. Rewilding (i.e. restoring ecosystem functioning with tion, ungulate minimal human intervention) is being pursued in many areas, and restocking or reintroduction of key species is often part of the rewilding strategy. Such programmes re- Introduction quire ecological information about the target areas but this is not always available. Using the example of the an has shaped landscapes for centuries (Vos & Iberian ibex Capra pyrenaica within the Rewilding Europe Meekes, ). In the last decades socio-economic M framework we address the following questions: ( ) Are and lifestyle changes have driven a rural exodus and the there areas in Western Iberia that are environmentally fa- abandonment of land throughout many of Europe’s rural vourable for reintroduction of the species? ( ) If so, are landscapes (MacDonald et al., ; Höchtl et al., ). these areas well connected with each other? ( ) Which of In some cases sociocultural and economic problems have these areas favour the establishment and expansion of a vi- created new opportunities for conservation (Theil et al., ). able population -
Characterization of Moose Movement Patterns and Movement of Black Bears in Relation to Anthropogenic Food Sources on Joint Basse
Form Approved REPORT DOCUMENTATION PAGE OMB No. 074-0188 AD_________________ (Leave blank) Award Number(s): W81XWH-08-2-0179-0002 W912DY-09-2-0011 W9126G-10-2-0042 TITLE: Characterization of moose movement patterns and movement of black bears in relation to anthropogenic food sources on Joint Base Elmendorf- Richardson, Alaska PRINCIPAL INVESTIGATOR: (Enter the name and degree of Principal Investigator and any Associates) Sean D. Farley,Ph.D.; Perry Barboza, Ph.D ; Herman Griese, MS; Christopher Garner, BS CONTRACTING ORGANIZATION: 673d Civil Engineering Squadron 724 Quartermaster Drive Joint Base Elmendorf Richardson, Alaska 99505-8860 REPORT DATE: Sept 2014 TYPE OF REPORT: Final PREPARED FOR: U.S. Army Medical Research and Materiel Command Fort Detrick, Maryland 21702-5012 (W81XWH-08-2-0179-0002) Army Corps of Engineers U.S. Army Engineering and Support Center Huntsville, Alabama 35816-1822 (W912DY-09-2-0011) Army Corps of Engineers U.S. Army Engineering and Support Center Fort Worth, Texas 76102-0300 (W9126G-10-2-0042) DISTRIBUTION STATEMENT: (Check one) X Approved for public release; distribution unlimited Distribution limited to U.S. Government agencies only; report contains proprietary information The views, opinions and/or findings contained in this report are those of the author(s) and should not be construed as an official Department of the Army position, policy or decision unless so designated by other documentation. 1 Public reporting burden for this collection of information is estimated to average 1 hour per response, including the time for reviewing instructions, searching existing data sources, gathering and maintaining the data needed, and completing and reviewing this collection of information. -
Alaska's Predator Control Programs
Alaska’sAlaska’s PredatorPredator ControlControl ProgramsPrograms Managing for Abundance or Abundant Mismanagement? In 1995, Alaska Governor Tony Knowles responded to negative publicity over his state’s predator control programs by requesting a National Academy of Sciences review of Alaska’s entire approach to predator control. Following the review Governor Knowles announced that no program should be considered unless it met three criteria: cost-effectiveness, scientific scrutiny and broad public acceptability. The National Academy of Sciences’ National Research Council (NRC) released its review, Wolves, Bears, and Their Prey in Alaska, in 1997, drawing conclusions and making recommendations for management of Alaska’s predators and prey. In 1996, prior to the release of the NRC report, the Wolf Management Reform Coalition, a group dedicated to promoting fair-chase hunting and responsible management of wolves in Alaska, published Showdown in Alaska to document the rise of wolf control in Alaska and the efforts undertaken to stop it. This report, Alaska’s Predator Control Programs: Managing for Abundance or Abundant Mismanagement? picks up where that 1996 report left off. Acknowledgements Authors: Caroline Kennedy, Theresa Fiorino Editor: Kate Davies Designer: Pete Corcoran DEFENDERS OF WILDLIFE Defenders of Wildlife is a national, nonprofit membership organization dedicated to the protection of all native wild animals and plants in their natural communities. www.defenders.org Cover photo: © Nick Jans © 2011 Defenders of Wildlife 1130 17th Street, N.W. Washington, D.C. 20036-4604 202.682.9400 333 West 4th Avenue, Suite 302 Anchorage, AK 99501 907.276.9453 Table of Contents 1. Introduction ............................................................................................................... 2 2. The National Research Council Review ...................................................................... -
Sustainable Trophy Hunting of Iberian Ibex Por Una Caza Sostenible Del Trofeo De Macho Montés
Forum Galemys, 30: 1-4, 2018 ISSN 1137-8700 e-ISSN 2254-8408 DOI: 10.7325/Galemys.2018.F1 Sustainable trophy hunting of Iberian ibex Por una caza sostenible del trofeo de macho montés João Carvalho1,2*, Paulino Fandos3, Marco Festa-Bianchet4, Ulf Büntgen5,6,7, Carlos Fonseca1 & Emmanuel Serrano2* 1. Department of Biology & Centre for Environmental and Marine Studies (CESAM), University of Aveiro, Aveiro, Portugal. 2. Wildlife Ecology & Health Group (WE&H) and Servei d’Ecopatologia de Fauna Salvatge (SEFaS), Departament de Medicina i Cirurgia Animals, Universitat Autònoma de Barcelona, 08193 Bellaterra, Barcelona, Spain. 3. Agencia de Medio Ambiente y Agua, Isla de la Cartuja, 41092 Sevilla, Spain. 4. Département de Biologie, Université de Sherbrooke, Sherbrooke, Québec J1K 2R1, Canada. 5. Department of Geography, University of Cambridge, Cambridge, United Kingdom. 6. Swiss Federal Research Institute (WSL), 8903 Birmensdorf, Switzerland. 7. Global Change Research Centre and Masaryk University, 613 00 Brno, Czech Republic. *Corresponding authors: [email protected] (JC), [email protected] (ES) Keywords: Capra pyrenaica, horns, mountain ungulates, size-selective harvesting. Selective hunting practices, such as trophy apparently led to an evolutionary decline in horn hunting, remove individuals with specific size (Pigeon et al. 2017). In contrast, we know very phenotypes (Kuparinen & Festa-Bianchet 2017). little about the possible effects of selective harvesting For mountain ungulates, trophy hunting involves on the iconic Iberian ibex (Capra pyrenaica, Fig. 1), the selective harvest of males with large horns. which is experiencing increased pressure not only Trophy hunters usually pay a substantial fee, which from trophy hunting (Pérez et al. 2011), but also in some cases is proportional to the ‘trophy score’ from changes in both climate and land-use practices of the animal they harvest. -
Removing the Gray Wolf (Canis Lupus) from the List of Endangered
References Cited for the Proposed Rule “Removing the Gray Wolf (Canis lupus) from the List of Endangered and Threatened Wildlife and Maintaining Protections for the Mexican Wolf (Canis lupus baileyi) by Listing It as Endangered” Adams, L.G., R.O. Stephenson, B.W. Dale, R.T. Ahgook, and D. J. Demma. 2008. Population dynamics and harvest characteristics of wolves in the central Brooks Range, Alaska. Wildlife Monographs 170: 1-25. Adaptive Management Oversight Committee and Interagency Field Team [AMOC and IFT]. 2005. Mexican wolf Blue Range reintroduction project 5-year review. Unpublished report to U.S. Fish and Wildlife Service, Region 2, Albuquerque, New Mexico, USA. http://www.fws.gov/southwest/es/mexicanwolf/MWNR_FYRD.shtml Anschutz, Steve. 2003. E-mail from Anschutz, USFWS Nebraska Field Office Supervisor to Laura Ragan, USFWS Regional Office, Ft. Snelling, MN, dated 04/01/03. Subject: gray wolf shot. 1 p. Anschutz, Steve. 2006. E-mail from Anschutz, USFWS Nebraska Field Office Supervisor to Ron Refsnider, USFWS Regional Office, Ft. Snelling, MN, dated 10/30/06. Subject: Nebraska wolf from 1995? Arizona Department of Health Services. 2012. Rabies Statistics and Maps, 2008-2012. www.azdhs.gov/phs/oids/vector/rabies/stats.htm. Accessed on July 23, 2012. Alaska Department of Fish and Game. 2007. Predator management in Alaska. Alaska Department of Fish and Game Division of Wildlife Conservation. 32pp. Alaska Department of Fish and Game. 2011. 2011-2012 Alaska trapping regulations. Alaska Department of Fish and Game. 48pp. Allendorf, F.W. and N. Ryman. 2002. The role of genetics in population viability analysis. Pages 50-85 in Beissinger, S.R., and D.R. -
Capra Pyrenaica
Colom-Cadena et al. Acta Veterinaria Scandinavica 2014, 56:83 http://www.actavetscand.com/content/56/1/83 RESEARCH Open Access Management of a caseous lymphadenitis outbreak in a new Iberian ibex (Capra pyrenaica) stock reservoir Andreu Colom-Cadena1, Roser Velarde1, Jes?s Salinas 2, Carmen Borge3, Ignacio Garc?a-Bocanegra 3, Emmanuel Serrano1,4, Diana Gass? 1, Ester Bach1, Encarna Casas-D?az 1, Jorge R L?pez-Olvera 1, Santiago Lav?n 1, Lu?s Le?n-Vizca?no 2 and Gregorio Mentaberre1* Abstract Background: In 2010, an Iberian ibex (Capra pyrenaica hispanica) stock reservoir was established for conservation purposes in north-eastern Spain. Eighteen ibexes were captured in the wild and housed in a 17 hectare enclosure. Once in captivity, a caseous lymphadenitis (CLA) outbreak occurred and ibex handlings were carried out at six-month intervals between 2010 and 2013 to perform health examinations and sampling. Treatment with a bacterin-based autovaccine and penicillin G benzatine was added during the third and subsequent handlings, when infection by Corynebacterium pseudotuberculosis was confirmed. Changes in lesion score, serum anti-C. pseudotuberculosis antibodies and haematological parameters were analyzed to assess captivity effects, disease emergence and treatment efficacy. Serum acute phase proteins (APP) Haptoglobin (Hp), Amyloid A (SAA) and Acid Soluble Glycoprotein (ASG) concentrations were also determined to evaluate their usefulnessasindicatorsofclinical status. Once in captivity, 12 out of 14 ibexes (85.7%) seroconverted, preceding the emergence of clinical signs; moreover, TP, WBC, eosinophil and platelet cell counts increased while monocyte and basophil cell counts decreased. After treatment, casualties and fistulas disappeared and both packed cell volume (PCV) and haemoglobin concentration significantly increased. -
Tanganyika Wildlife Park L L C Customer ID: 324586 1037 So 183Rd St W Certificate: 48-C-0156 GODDARD, KS 67052 Site: 001 Tanganyika Wildlife Park L L C
United States Department of Agriculture MSHAVER Animal and Plant Health Inspection Service 2016090000638385 Insp_id Inspection Report Tanganyika Wildlife Park L L C Customer ID: 324586 1037 So 183rd St W Certificate: 48-C-0156 GODDARD, KS 67052 Site: 001 Tanganyika Wildlife Park L L C Type: ROUTINE INSPECTION Date: 21-JUN-2021 2.131(b)(1) Critical Handling of animals. This licensee made available for transport to another licensed facility three Eurasian Lynx kittens under 28 days of age. The Certificate of Veterinary Inspection (CVI) shows an inspection date of 5/4/2020 with the kittens at 18 days of age. The shipping date on the CVI matches the APHIS 7020 form provided by the licensee showing a transport date of 5/6/2020. Neonatal nondomestic cats have special handing and husbandry needs and are placed in danger when they are exposed to members of the public and/or stressful conditions, including transportation. Cubs under 4 weeks of age (28 days) do not have a developed immune system, are susceptible to a wide variety of diseases including those of domestic cats, and cannot thermoregulate. The licensee must ensure that handling of all animals be done as expeditiously and carefully as possible in a manner that does not cause trauma, overheating, excessive cooling, behavioral stress, phy sical harm, or unnecessary discomfort. To be corrected from this day forward. This inspection and exit interview were conducted with facility representatives. Additional Inspectors: MICHAEL TYGART, VETERINARY MEDICAL OFFICEREnd Section Prepared By: MARGARET -
PDF File Containing Table of Lengths and Thicknesses of Turtle Shells And
Source Species Common name length (cm) thickness (cm) L t TURTLES AMNH 1 Sternotherus odoratus common musk turtle 2.30 0.089 AMNH 2 Clemmys muhlenbergi bug turtle 3.80 0.069 AMNH 3 Chersina angulata Angulate tortoise 3.90 0.050 AMNH 4 Testudo carbonera 6.97 0.130 AMNH 5 Sternotherus oderatus 6.99 0.160 AMNH 6 Sternotherus oderatus 7.00 0.165 AMNH 7 Sternotherus oderatus 7.00 0.165 AMNH 8 Homopus areolatus Common padloper 7.95 0.100 AMNH 9 Homopus signatus Speckled tortoise 7.98 0.231 AMNH 10 Kinosternon subrabum steinochneri Florida mud turtle 8.90 0.178 AMNH 11 Sternotherus oderatus Common musk turtle 8.98 0.290 AMNH 12 Chelydra serpentina Snapping turtle 8.98 0.076 AMNH 13 Sternotherus oderatus 9.00 0.168 AMNH 14 Hardella thurgi Crowned River Turtle 9.04 0.263 AMNH 15 Clemmys muhlenbergii Bog turtle 9.09 0.231 AMNH 16 Kinosternon subrubrum The Eastern Mud Turtle 9.10 0.253 AMNH 17 Kinixys crosa hinged-back tortoise 9.34 0.160 AMNH 18 Peamobates oculifers 10.17 0.140 AMNH 19 Peammobates oculifera 10.27 0.140 AMNH 20 Kinixys spekii Speke's hinged tortoise 10.30 0.201 AMNH 21 Terrapene ornata ornate box turtle 10.30 0.406 AMNH 22 Terrapene ornata North American box turtle 10.76 0.257 AMNH 23 Geochelone radiata radiated tortoise (Madagascar) 10.80 0.155 AMNH 24 Malaclemys terrapin diamondback terrapin 11.40 0.295 AMNH 25 Malaclemys terrapin Diamondback terrapin 11.58 0.264 AMNH 26 Terrapene carolina eastern box turtle 11.80 0.259 AMNH 27 Chrysemys picta Painted turtle 12.21 0.267 AMNH 28 Chrysemys picta painted turtle 12.70 0.168 AMNH 29 -
Moose Survey Report 2013
AERIAL MOOSE SURVEY on and around KANUTI NATIONAL WILDLIFE REFUGE November, 2013 Tim Craig US Fish and Wildlife Service and Glenn W. Stout Alaska Department of Fish and Game February 2014 DATA SUMMARY Survey Dates: 12- 18 November (Intensive survey only) Total area covered by survey: Kanuti National Wildlife Refuge (hereafter, Refuge) Survey Area: 2,715 mi2 (7,029 km2); Total Survey Area: 3,736 mi2 (9676 km2) Total Number sample units Refuge Survey Area: 508; Total Survey Area: 701 Number of sample units surveyed: Refuge Survey Area: 105; Total Survey Area: 129 Total moose observed: Refuge Survey Area: 259 moose (130 cows, 95 bulls, and 34 calves); Total Survey Area: 289 moose (145 cows, 105 bulls, 39 calves) November population estimate: Refuge Survey Area: 551 moose (90% confidence interval = 410 - 693) comprised of 283 cows, 183 bulls, and 108 calves*; Total Survey Area: 768 moose (90% confidence interval = 589 – 947) comprised of 387 cows, 257 bulls, 144 calves*. *Subtotals by class do not equal the total population because of accumulated error associated with each estimate. Estimated total density: Refuge Survey Area: 0.20 moose/mi2 (0.08 moose/km2); Total Survey Area: 0.21 moose/mi2 (0.08 moose/km2) Estimated ratios: Refuge survey area: 36 calves:100 cows, 11 yearling bulls:100 cows, 37 large bulls:100 cows, 65 total bulls:100 cows; Total Survey Area: 35 calves:100 cows, 11 yearling bulls:100 cows, 40 large bulls:100 cows, 67 total bulls:100 cows 2 INTRODUCTION The Kanuti National Wildlife Refuge (hereafter, Refuge), the Alaska Department of Fish and Game (ADF&G) and the Bureau of Land Management cooperatively conducted a moose (Alces alces) population survey 12 - 18 November 2013 on, and around, the Refuge. -
Jan 2021 ZSL Stocklist.Pdf (699.26
Zoological Society of London - January 2021 stocklist ZSL LONDON ZOO Status at 01.01.2021 m f unk Invertebrata Aurelia aurita * Moon jellyfish 0 0 150 Pachyclavularia violacea * Purple star coral 0 0 1 Tubipora musica * Organ-pipe coral 0 0 2 Pinnigorgia sp. * Sea fan 0 0 20 Sarcophyton sp. * Leathery soft coral 0 0 5 Sinularia sp. * Leathery soft coral 0 0 18 Sinularia dura * Cabbage leather coral 0 0 4 Sinularia polydactyla * Many-fingered leather coral 0 0 3 Xenia sp. * Yellow star coral 0 0 1 Heliopora coerulea * Blue coral 0 0 12 Entacmaea quadricolor Bladdertipped anemone 0 0 1 Epicystis sp. * Speckled anemone 0 0 1 Phymanthus crucifer * Red beaded anemone 0 0 11 Heteractis sp. * Elegant armed anemone 0 0 1 Stichodactyla tapetum Mini carpet anemone 0 0 1 Discosoma sp. * Umbrella false coral 0 0 21 Rhodactis sp. * Mushroom coral 0 0 8 Ricordea sp. * Emerald false coral 0 0 19 Acropora sp. * Staghorn coral 0 0 115 Acropora humilis * Staghorn coral 0 0 1 Acropora yongei * Staghorn coral 0 0 2 Montipora sp. * Montipora coral 0 0 5 Montipora capricornis * Coral 0 0 5 Montipora confusa * Encrusting coral 0 0 22 Montipora danae * Coral 0 0 23 Montipora digitata * Finger coral 0 0 6 Montipora foliosa * Hard coral 0 0 10 Montipora hodgsoni * Coral 0 0 2 Pocillopora sp. * Cauliflower coral 0 0 27 Seriatopora hystrix * Bird nest coral 0 0 8 Stylophora sp. * Cauliflower coral 0 0 1 Stylophora pistillata * Pink cauliflower coral 0 0 23 Catalaphyllia jardinei * Elegance coral 0 0 4 Euphyllia ancora * Crescent coral 0 0 4 Euphyllia glabrescens * Joker's cap coral 0 0 2 Euphyllia paradivisa * Branching frog spawn 0 0 3 Euphyllia paraancora * Branching hammer coral 0 0 3 Euphyllia yaeyamaensis * Crescent coral 0 0 4 Plerogyra sinuosa * Bubble coral 0 0 1 Duncanopsammia axifuga + Coral 0 0 2 Tubastraea sp.