The Elusive and Mysterious Wood Bison
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National Parks: Time to Burn (For Ecological Integrity’S Sake)
National Parks: Time to Burn (for Ecological Integrity’s Sake) By Andrea Johancsik, AWA Conservation Specialist tanding at the peak of the east end nities. In Alberta we saw the subsequent National Park this way in 1915. Eight de- of Rundle last month, my friends creation of Waterton Lakes National Park cades later, then- graduate student Jeanine S and I marveled at the sunny, spring in 1895, Elk Island National Park in 1906, Rhemtulla, Dr. Eric Higgs, and other mem- day we were fortunate enough to witness Jasper National Park in 1907, and Wood bers of the Mountain Legacy project pains- from 2,530m high. The hike gives vistas of Buffalo National Park in 1922. The high- takingly retook all 735 of Bridgland’s Jasper remote mountain peaks and forested slopes, ly popular and newly accessible mountain photos. They wanted to compare how the as well as the highly visible town of Can- parks became dominated by tourism and vegetation on the landscape had changed, more and the Spray Lakes dam. However, commercial development, roads, and re- if it had changed at all, over nearly a cen- arguably one of the biggest human-caused moval of keystone species like the plains tury. Their study found that vegetation has changes in the mountain national parks is bison. Many of the 3.6 million visitors who become less diverse and is now dominated much less obvious. Decades of fire suppres- passed through Banff National Park last year by closed-canopy coniferous forests; in 1915 sion have changed the landscape in a dra- probably didn’t realize they were looking at the landscape consisted of open coniferous matic way; had we been at the summit 80 a drastically different landscape from the one forest, grasslands, young forests and some years ago our view likely would have been of a century ago. -
The Effects of Linear Developments on Wildlife
Bibliography Rec# 5. LeBlanc, R. 1991. The aversive conditioning of a roadside habituated grizzly bear within Banff Park: progress report 1991. 6 pp. road impacts/ grizzly bear/ Ursus arctos/ Banff National Park/ aversive conditions/ Icefields Parkway. Rec# 10. Forman, R.T.T. 1983. Corridors in a landscape: their ecological structure and function. Ekologia 2 (4):375-87. corridors/ landscape/ width. Rec# 11. McLellan, B.N. 1989. Dymanics of a grizzly bear population during a period of industrial resource extraction. III Natality and rate of increase. Can. J. Zool. Vol. 67 :1865-1868. reproductive rate/ grizzly bear/ Ursus arctos/ British Columbia/ gas exploration/ timber harvest. Rec# 14. McLellan, B.N. 1989. Dynamics of a grizzly bear population during a period of industrial resource extraction. II.Mortality rates and causes of death. Can. J. Zool. Vol. 67 :1861-1864. British Columbia/ grizzly bear/ Ursus arctos/ mortality rate/ hunting/ outdoor recreation/ gas exploration/ timber harvest. Rec# 15. Miller, S.D., Schoen, J. 1993. The Brown Bear in Alaska . brown bear/ grizzly bear/ Ursus arctos middendorfi/ Ursus arctos horribilis/ population density/ distribution/ legal status/ human-bear interactions/ management/ education. Rec# 16. Archibald, W.R., Ellis, R., Hamilton, A.N. 1987. Responses of grizzly bears to logging truck traffic in the Kimsquit River valley, British Columbia. Int. Conf. Bear Res. and Manage. 7:251-7. grizzly bear/ Ursus / arctos/ roads/ traffic/ logging/ displacement/ disturbance/ carnivore/ BC/ individual disruption / habitat displacement / habitat disruption / social / filter-barrier. Rec# 20. Kasworm, W.F., Manley, T.L. 1990. Road and trail influences on grizzly bears and black bears in northwest Montana. -
Influence of Common Eland (Taurotragus Oryx) Meat Composition on Its Further Technological Processing
CZECH UNIVERSITY OF LIFE SCIENCES PRAGUE Faculty of Tropical AgriSciences Department of Animal Science and Food Processing Influence of Common Eland (Taurotragus oryx) Meat Composition on its further Technological Processing DISSERTATION THESIS Prague 2018 Author: Supervisor: Ing. et Ing. Petr Kolbábek prof. MVDr. Daniela Lukešová, CSc. Co-supervisors: Ing. Radim Kotrba, Ph.D. Ing. Ludmila Prokůpková, Ph.D. Declaration I hereby declare that I have done this thesis entitled “Influence of Common Eland (Taurotragus oryx) Meat Composition on its further Technological Processing” independently, all texts in this thesis are original, and all the sources have been quoted and acknowledged by means of complete references and according to Citation rules of the FTA. In Prague 5th October 2018 ………..………………… Acknowledgements I would like to express my deep gratitude to prof. MVDr. Daniela Lukešová CSc., Ing. Radim Kotrba, Ph.D. and Ing. Ludmila Prokůpková, Ph.D., and doc. Ing. Lenka Kouřimská, Ph.D., my research supervisors, for their patient guidance, enthusiastic encouragement and useful critiques of this research work. I am very gratefull to Ing. Petra Maxová and Ing. Eva Kůtová for their valuable help during the research. I am also gratefull to Mr. Petr Beluš, who works as a keeper of elands in Lány, Mrs. Blanka Dvořáková, technician in the laboratory of meat science. My deep acknowledgement belongs to Ing. Radek Stibor and Mr. Josef Hora, skilled butchers from the slaughterhouse in Prague – Uhříněves and to JUDr. Pavel Jirkovský, expert marksman, who shot the animals. I am very gratefull to the experts from the Natura Food Additives, joint-stock company and from the Alimpex-maso, Inc. -
Horned Animals
Horned Animals In This Issue In this issue of Wild Wonders you will discover the differences between horns and antlers, learn about the different animals in Alaska who have horns, compare and contrast their adaptations, and discover how humans use horns to make useful and decorative items. Horns and antlers are available from local ADF&G offices or the ARLIS library for teachers to borrow. Learn more online at: alaska.gov/go/HVNC Contents Horns or Antlers! What’s the Difference? 2 Traditional Uses of Horns 3 Bison and Muskoxen 4-5 Dall’s Sheep and Mountain Goats 6-7 Test Your Knowledge 8 Alaska Department of Fish and Game, Division of Wildlife Conservation, 2018 Issue 8 1 Sometimes people use the terms horns and antlers in the wrong manner. They may say “moose horns” when they mean moose antlers! “What’s the difference?” they may ask. Let’s take a closer look and find out how antlers and horns are different from each other. After you read the information below, try to match the animals with the correct description. Horns Antlers • Made out of bone and covered with a • Made out of bone. keratin layer (the same material as our • Grow and fall off every year. fingernails and hair). • Are grown only by male members of the • Are permanent - they do not fall off every Cervid family (hoofed animals such as year like antlers do. deer), except for female caribou who also • Both male and female members in the grow antlers! Bovid family (cloven-hoofed animals such • Usually branched. -
Reclassifying the Wood Bison
6734 Federal Register / Vol. 76, No. 26 / Tuesday, February 8, 2011 / Proposed Rules input in person, by mail, e-mail, or January 13, 2011. generally means that we will post any phone at any time during the Peter J. Probasco, personal information you provide us rulemaking process. Acting Chair, Federal Subsistence Board. (see the Public Comments section below January 13, 2011. for more information). Executive Order 13211 Steve Kessler, FOR FURTHER INFORMATION CONTACT: This Executive Order requires Subsistence Program Leader, USDA–Forest Marilyn Myers at U.S. Fish and Wildlife agencies to prepare Statements of Service. Service, Fisheries and Ecological Energy Effects when undertaking certain [FR Doc. 2011–2679 Filed 2–7–11; 8:45 am] Services, 1011 E. Tudor Road, actions. However, this proposed rule is BILLING CODE 3410–11–P; 4310–55–P Anchorage, Alaska 99503, or telephone not a significant regulatory action under 907–786–3559 or by facsimile at (907) E.O. 13211, affecting energy supply, 786–3848. If you use a distribution, or use, and no Statement of DEPARTMENT OF THE INTERIOR telecommunications device for the deaf (TDD), please call the Federal Energy Effects is required. Fish and Wildlife Service Information Relay Service (FIRS) at Drafting Information 800–877–8339. 50 CFR Part 17 SUPPLEMENTARY INFORMATION: Theo Matuskowitz drafted these regulations under the guidance of Peter [Docket No. FWS–R9–IA–2008–0123; MO Public Comments 92210–1113FWDB B6] J. Probasco of the Office of Subsistence We intend that any final action Management, Alaska Regional Office, RIN 1018–AI83 resulting from this proposed rule will be U.S. -
The Mackenzie Wood Bison (Bison Bison Athabascae) C.C
ARCTIC VOL. 43, NO. 3 (SEPTEMBER 1990) P. 231-238 Growth and Dispersal of an Erupting Large Herbivore Population in Northern Canada: The Mackenzie Wood Bison (Bison bison athabascae) C.C. GATES' and N.C. LARTER' (Received 6 September 1989; accepted in revised form Il January 1990) ABSTRACT. In 1963,18 wood bison (Bison bison athabuscue)were introduced to the Mackenzie Bison Sanctuary. Thepopulation has grown at a mean exponential rate of r = 0.215 f 0.007, reaching 1718 bison 2 10 months of age by April 1987. Analysis of annual population growth revealed a maximum exponential rateof r = 0.267 in 1975, followed by a declining rate, reaching a low value of r = 0.103 in 1987. Selective predation on calves was proposed as a mechanism to explain the declining rate of population growth. The area occupiedby the population increased at an exponential rate of0.228 f 0.017 km2.year". The dispersal ofmature males followed a pattern described as an innate process, while dispersal of females and juveniles exhibited characteristicsof pressure-threshold dispersal. Key words: erupting population, dispersal, wood bison, Bison bison athabascae, Northwest Rrritories RJ~SUMÉ.En 1963, on a introduit 18 bisons des bois(Bison bison athabuscue)dans la Rtserve de bisons Mackenzie.La population a connu un taux moyen de croissance exponentielle der= 0,215 f 0,007, atteignant 1718 bisons qui avaient 10 mois ou plus en avril 1987. Une analyse de la croissance annuelle de la population montre un taux moyen de croissance exponentielle der = 0,267 en 1975, suivid'un taux en baisse jusqu'B r = 0,103 en 1987.On avanceque la prkdation selectives'optrant sur les veauxexplique la baisse du taux de croissance lade population. -
Infectious Diseases of Saiga Antelopes and Domestic Livestock in Kazakhstan
Infectious diseases of saiga antelopes and domestic livestock in Kazakhstan Monica Lundervold University of Warwick, UK June 2001 1 Chapter 1 Introduction This thesis combines an investigation of the ecology of a wild ungulate, the saiga antelope (Saiga tatarica, Pallas), with epidemiological work on the diseases that this species shares with domestic livestock. The main focus is on foot-and-mouth disease (FMD) and brucellosis. The area of study was Kazakhstan (located in Central Asia, Figure 1.1), home to the largest population of saiga antelope in the world (Bekenov et al., 1998). Kazakhstan's independence from the Soviet Union in 1991 led to a dramatic economic decline, accompanied by a massive reduction in livestock numbers and a virtual collapse in veterinary services (Goskomstat, 1996; Morin, 1998a). As the rural economy has disintegrated, the saiga has suffered a dramatic increase in poaching (Bekenov et al., 1998). Thus the investigation reported in this thesis includes ecological, epidemiological and socio-economic aspects, all of which were necessary in order to gain a full picture of the dynamics of the infectious diseases of saigas and livestock in Kazakhstan. The saiga is an interesting species to study because it is one of the few wildlife populations in the world that has been successfully managed for commercial hunting over a period of more than 40 years (Milner-Gulland, 1994a). Its location in Central Asia, an area that was completely closed to foreigners during the Soviet era, means that very little information on the species and its management has been available in western literature. The diseases that saigas share with domestic livestock have been a particular focus of this study because of the interesting issues related to veterinary care and disease control in the Former Soviet Union (FSU). -
Wood Bison (Bison Bison Athabascae)
U.S. Fish & Wildlife Service Threatened and Endangered Species Wood Bison (Bison bison athabascae) The wood bison (Bison bison athabascae) is the largest native land mammal in North America. They have a large triangular head, a thin beard, and rudimentary throat mane; their horns usually extend above the hair on their head; and the highest point of their hump is forward of their front legs. These physical characteristics distinguish them from the plains bison (Bison bison bison), which is the subspecies that occurs on the prairies of the continental United States. Protected Status The wood bison is listed as threatened under the 1973 Endangered Species Act (ESA). In Canada the wood bison is protected as threatened under the Species at Risk Act. Range and Population Size The wood bison is adapted to meadow Wood bison cow and calf at the Alaska Wildlife Conservation Center. Doug Lindstrand and forest habitats in subarctic regions. Historically, its range was generally north of that occupied by Canada, hunting is strictly regulated uninfected herds. Captive herds the plains bison, and included most and is not a threat to the species as of disease-free animals have been boreal regions of northern Alberta; it once was. The main threats are established in both Alaska and northeastern British Columbia; diseases of domestic cattle (bovine Russia. a small portion of northwestern tuberculosis and bovine brucellosis), Saskatchewan; the western which were unintentionally introduced Alaska’s Captive Herd Northwest Territories; most of the to wood bison in the early 1920s, The captive herd in Alaska is being Yukon Territory; and much of interior and loss of habitat (primarily from cared for at the Alaska Wildlife Alaska. -
Plains Bison and Wood Bison Conservation in Canada
Bison Conservation in Canada Shelley Pruss Parks Canada Agency Greg Wilson Environment and Climate Change Canada 19 May 2016 1 Canada is home to two subspecies of bison Key morphological differences between Wood Bison bull (Bison bison athabascae) Plains Bison bulls(Bison bison bison) Line drawing courtesy of Wes Olson taken from COSEWIC. 2013. COSEWIC assessment and status report on the Plains Bison (Bison bison bison) and the Wood Bison (Bison bison athabascae) in Canada. 2 PLAINS BISON All wild Plains Bison subpopulations in Canada today are the descendants of approximately 81 ancestors captured in three locations in the 1870s and 1880s, and persist as a tiny fraction of their original numbers (~30 million in North America). WOOD BISON Alaska Dept of Fish and Game Historical (pre-settlement) distribution of Wood Bison and Plains Bison in North America. Modified from Gates et al. (2010). Polygons courtesy of Keith Aune, Wildlife Conservation Society (COSEWIC 3 2013) The Species at Risk Act The federal government is responsible for implementing the federal Species at Risk Act (SARA) • Purpose: to prevent species from being extirpated or becoming extinct and to provide for recovery of species at risk The key provisions of SARA are: • Prohibitions against killing or harming listed species on federal lands • Requirement to develop a national recovery strategy and action plan(s) and to identify critical habitat to the extent possible for Extirpated, Endangered, and Threatened species • Management plans are developed for species of Special -
LANDFIRE Biophysical Setting Model Biophysical Setting: 9814340 Texas-Louisiana Coastal Prairie
LANDFIRE Biophysical Setting Model Biophysical Setting: 9814340 Texas-Louisiana Coastal Prairie This BPS is lumped with: 1487 This BPS is split into multiple models: BpS 1434 is systematically lumped with 1487. BpS 1487 is too fine for mapping and modeling. General Information Contributors (also see the Comments field) Date 1/24/2007 Modeler 1 Chris Harper [email protected] Reviewer Modeler 2 Ron Masters [email protected] Reviewer Modeler 3 Patrick Walther [email protected] Reviewer Vegetation Type Dominant Species Map Zone Model Zone ANGE Upland 98 Alaska Northern Plains Grassland/Herbaceous SCSC California N-Cent.Rockies General Model Sources PAVIS Great Basin Pacific Northwest Literature SPSP Great Lakes South Central Local Data TRDA3 Hawaii Southeast Expert Estimate PAHE2 Northeast S. Appalachians SONU2 Southwest MOCE2 Geographic Range This BpS encompasses non-saline tallgrass prairie vegetation ranging along the coast of LA and TX. This coastal prairie region once covered as much as nine million acres (Grace 2000). The prairie region of southwestern LA was once extensive (~ 2.5 million acres) but today is limited to small, remnant parcels (100-1000ac). Gulf Coast and inland varying distances from 50-150 miles (80-240 km) from south TX to LA and the mouth of the Mississippi River. In LA, it is bordered to the north and east by Southern Floodplain Forest (Kuchler 1964). To the south and west it also joins with the desert grasslands. This BpS is found in MZ37 in ECOMAP subsections 232Ea and 232Eb. Biophysical Site Description This BpS is found on Vertisols and Alfisols which developed over Pleistocene terraces flanking the Gulf Coast. -
European Bison
IUCN/Species Survival Commission Status Survey and Conservation Action Plan The Species Survival Commission (SSC) is one of six volunteer commissions of IUCN – The World Conservation Union, a union of sovereign states, government agencies and non- governmental organisations. IUCN has three basic conservation objectives: to secure the conservation of nature, and especially of biological diversity, as an essential foundation for the future; to ensure that where the Earth’s natural resources are used this is done in a wise, European Bison equitable and sustainable way; and to guide the development of human communities towards ways of life that are both of good quality and in enduring harmony with other components of the biosphere. A volunteer network comprised of some 8,000 scientists, field researchers, government officials Edited by Zdzis³aw Pucek and conservation leaders from nearly every country of the world, the SSC membership is an Compiled by Zdzis³aw Pucek, Irina P. Belousova, unmatched source of information about biological diversity and its conservation. As such, SSC Ma³gorzata Krasiñska, Zbigniew A. Krasiñski and Wanda Olech members provide technical and scientific counsel for conservation projects throughout the world and serve as resources to governments, international conventions and conservation organisations. IUCN/SSC Action Plans assess the conservation status of species and their habitats, and specifies conservation priorities. The series is one of the world’s most authoritative sources of species conservation information -
Isotopic Evidence for Diet and Subsistence Pattern of the Saint-Ce´Saire I Neanderthal: Review and Use of a Multi-Source Mixing Model
Journal of Human Evolution 49 (2005) 71e87 Isotopic evidence for diet and subsistence pattern of the Saint-Ce´saire I Neanderthal: review and use of a multi-source mixing model Herve´Bocherens a,b,*, Dorothe´e G. Drucker c, Daniel Billiou d, Maryle` ne Patou-Mathis e, Bernard Vandermeersch f a Institut des Sciences de l’Evolution, UMR 5554, Universite´ Montpellier 2, Place E. Bataillon, F-34095 Montpellier cedex 05, France b PNWRC, Canadian Wildlife Service, Environment Canada, 115 Perimeter Road, Saskatoon, Saskatchewan, S7N 0X4 Canada c PNWRC, Canadian Wildlife Service, Environment Canada, 115 Perimeter Road, Saskatoon, Saskatchewan, S7N 0X4 Canada d Laboratoire de Bioge´ochimie des Milieux Continentaux, I.N.A.P.G., EGER-INRA Grignon, URM 7618, 78026 Thiverval-Grignon, France e Institut de Pale´ontologie Humaine, 1 rue Rene´ Panhard, 75 013 Paris, France f C/Nun˜ez de Balboa 4028001 Madrid, Spain Received 10 December 2004; accepted 16 March 2005 Abstract The carbon and nitrogen isotopic abundances of the collagen extracted from the Saint-Ce´saire I Neanderthal have been used to infer the dietary behaviour of this specimen. A review of previously published Neanderthal collagen isotopic signatures with the addition of 3 new collagen isotopic signatures from specimens from Les Pradelles allows us to compare the dietary habits of 5 Neanderthal specimens from OIS 3 and one specimen from OIS 5c. This comparison points to a trophic position as top predator in an open environment, with little variation through time and space. In addition, a comparison of the Saint-Ce´saire I Neanderthal with contemporaneous hyaenas has been performed using a multi-source mixing model, modified from Phillips and Gregg (2003, Oecologia 127, 171).