Distribution, Morphology, and Habitat Use of the Red Fox in the Northern
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After Long-Term Decline, Are Aspen Recovering in Northern Yellowstone? ⇑ Luke E
Forest Ecology and Management 329 (2014) 108–117 Contents lists available at ScienceDirect Forest Ecology and Management journal homepage: www.elsevier.com/locate/foreco After long-term decline, are aspen recovering in northern Yellowstone? ⇑ Luke E. Painter a, , Robert L. Beschta a, Eric J. Larsen b, William J. Ripple a a Department of Forest Ecosystems and Society, Oregon State University, Corvallis, OR 97331, USA b Department of Geography and Geology, University of Wisconsin – Stevens Point, Stevens Point, WI 54481-3897, USA article info abstract Article history: In northern Yellowstone National Park, quaking aspen (Populus tremuloides) stands were dying out in the Received 18 December 2013 late 20th century following decades of intensive browsing by Rocky Mountain elk (Cervus elaphus). In Received in revised form 28 May 2014 1995–1996 gray wolves (Canis lupus) were reintroduced, joining bears (Ursus spp.) and cougars (Puma Accepted 30 May 2014 concolor) to complete the guild of large carnivores that prey on elk. This was followed by a marked decline in elk density and change in elk distribution during the years 1997–2012, due in part to increased pre- dation. We hypothesized that these changes would result in less browsing and an increase in height of Keywords: young aspen. In 2012, we sampled 87 randomly selected stands in northern Yellowstone, and compared Wolves our data to baseline measurements from 1997 and 1998. Browsing rates (the percentage of leaders Elk Browsing effects browsed annually) in 1997–1998 were consistently high, averaging 88%, and only 1% of young aspen Trophic cascade in sample plots were taller than 100 cm; none were taller than 200 cm. -
Conservation of the Wildcat (Felis Silvestris) in Scotland: Review of the Conservation Status and Assessment of Conservation Activities
Conservation of the wildcat (Felis silvestris) in Scotland: Review of the conservation status and assessment of conservation activities Urs Breitenmoser, Tabea Lanz and Christine Breitenmoser-Würsten February 2019 Wildcat in Scotland – Review of Conservation Status and Activities 2 Cover photo: Wildcat (Felis silvestris) male meets domestic cat female, © L. Geslin. In spring 2018, the Scottish Wildcat Conservation Action Plan Steering Group commissioned the IUCN SSC Cat Specialist Group to review the conservation status of the wildcat in Scotland and the implementation of conservation activities so far. The review was done based on the scientific literature and available reports. The designation of the geographical entities in this report, 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. The SWCAP Steering Group contact point is Martin Gaywood ([email protected]). Wildcat in Scotland – Review of Conservation Status and Activities 3 List of Content Abbreviations and Acronyms 4 Summary 5 1. Introduction 7 2. History and present status of the wildcat in Scotland – an overview 2.1. History of the wildcat in Great Britain 8 2.2. Present status of the wildcat in Scotland 10 2.3. Threats 13 2.4. Legal status and listing 16 2.5. Characteristics of the Scottish Wildcat 17 2.6. Phylogenetic and taxonomic characteristics 20 3. Recent conservation initiatives and projects 3.1. Conservation planning and initial projects 24 3.2. Scottish Wildcat Action 28 3.3. -
MOLECULAR GENETIC IDENTIFICATION of a MEXICAN ONZA SPECIMEN AS a PUMA (PUMA CONCOLOR) in the Americas, There Are Two Documented
Cryptozoology, 12, 1993-1996, 42-49 © 1996 International Society of Cryptozoology MOLECULAR GENETIC IDENTIFICATION OF A MEXICAN ONZA SPECIMEN AS A PUMA (PUMA CONCOLOR) PE tit A. DRATCH Laboratory of Viral Carcinogenesis, National Cancer Institute, Frederick Cancer Research and Development Center, Building 560/Room 21-105, Frederick, Maryland 21702, U.S.A. and National Fish and Wildlife Forensics Laboratory Ashland, Oregon 96520, U.S.A. WENDY RosLuND National Fish and Wildlife Forensics Laboratory Ashland, Oregon 96520, U.S.A. JANICE S. MARTENSON, MELANIE CULVER, AND STEPHEN J. O'BRIEN' Laboratory of Viral Carcinogenesis, National Cancer Institute, Frederick Cancer Research and Development Center, Building 560/Room 21-105, Frederick, Maryland 21702, U.S.A. ABSTRACT: Tissue samples from an alleged Mexican Onza, shot in the western Sierra Madre in 1986, were subjected to several biochemical assays in an attempt to determine the specimen's relationship to felid species of North America. Protein analyses included isoenzyme electrophoresis and albumin isoelectric focusing. Mi- tochondrial DNA was assayed for restriction fragment lengths with 28 restriction enzymes, and the NÐ5 gene was sequenced. The resulting protein and rnitochondrial DNA characteristics of the Onza were indistinguishable from those of North Amer- ican pumas. INTRODUCTION In the Americas, there are two documented species of large cats: 1) Puma concolor, the puma, also called mountain lion, cougar, and panther in dif- ferent regions of North America, and known as leon in Mexico; and 2) Panthera onca, the jaguar, or tigre as it is known south of the U.S. border. To whom correspondence should be addressed. 42 DRATCH ET AL.: ONZA MOLECULAR GENETIC IDENTIFICATION 43 Flo. -
Wolf Interactions with Non-Prey
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln USGS Northern Prairie Wildlife Research Center US Geological Survey 2003 Wolf Interactions with Non-prey Warren B. Ballard Texas Tech University Ludwig N. Carbyn Canadian Wildlife Service Douglas W. Smith US Park Service Follow this and additional works at: https://digitalcommons.unl.edu/usgsnpwrc Part of the Animal Sciences Commons, Behavior and Ethology Commons, Biodiversity Commons, Environmental Policy Commons, Recreation, Parks and Tourism Administration Commons, and the Terrestrial and Aquatic Ecology Commons Ballard, Warren B.; Carbyn, Ludwig N.; and Smith, Douglas W., "Wolf Interactions with Non-prey" (2003). USGS Northern Prairie Wildlife Research Center. 325. https://digitalcommons.unl.edu/usgsnpwrc/325 This Article is brought to you for free and open access by the US Geological Survey at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in USGS Northern Prairie Wildlife Research Center by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. 10 Wolf Interactions with Non-prey Warren B. Ballard, Ludwig N. Carbyn, and Douglas W. Smith WOLVES SHARE THEIR ENVIRONMENT with many an wolves and non-prey species. The inherent genetic, be imals besides those that they prey on, and the nature of havioral, and morphological flexibility of wolves has the interactions between wolves and these other crea allowed them to adapt to a wide range of habitats and tures varies considerably. Some of these sympatric ani environmental conditions in Europe, Asia, and North mals are fellow canids such as foxes, coyotes, and jackals. America. Therefore, the role of wolves varies consider Others are large carnivores such as bears and cougars. -
Dental and Temporomandibular Joint Pathology of the Kit Fox (Vulpes Macrotis)
Author's Personal Copy J. Comp. Path. 2019, Vol. 167, 60e72 Available online at www.sciencedirect.com ScienceDirect www.elsevier.com/locate/jcpa DISEASE IN WILDLIFE OR EXOTIC SPECIES Dental and Temporomandibular Joint Pathology of the Kit Fox (Vulpes macrotis) N. Yanagisawa*, R. E. Wilson*, P. H. Kass† and F. J. M. Verstraete* *Department of Surgical and Radiological Sciences and † Department of Population Health and Reproduction, School of Veterinary Medicine, University of California, Davis, California, USA Summary Skull specimens from 836 kit foxes (Vulpes macrotis) were examined macroscopically according to predefined criteria; 559 specimens were included in this study. The study group consisted of 248 (44.4%) females, 267 (47.8%) males and 44 (7.9%) specimens of unknown sex; 128 (22.9%) skulls were from young adults and 431 (77.1%) were from adults. Of the 23,478 possible teeth, 21,883 teeth (93.2%) were present for examina- tion, 45 (1.9%) were absent congenitally, 405 (1.7%) were acquired losses and 1,145 (4.9%) were missing ar- tefactually. No persistent deciduous teeth were observed. Eight (0.04%) supernumerary teeth were found in seven (1.3%) specimens and 13 (0.06%) teeth from 12 (2.1%) specimens were malformed. Root number vari- ation was present in 20.3% (403/1,984) of the present maxillary and mandibular first premolar teeth. Eleven (2.0%) foxes had lesions consistent with enamel hypoplasia and 77 (13.8%) had fenestrations in the maxillary alveolar bone. Periodontitis and attrition/abrasion affected the majority of foxes (71.6% and 90.5%, respec- tively). -
Wildlife; Threatened and Endangered Species
2009 SNF Monitoring and Evaluation Report Wildlife; Threatened and Endangered Species Introduction The data described in this report outlines the history, actions, procedures, and direction that the Superior National Forest (aka the Forest or SNF) has implemented in support of the Gray Wolf Recovery Plan and Lynx Conservation Assessment and Strategy (LCAS). The Forest contributes towards the conservation and recovery of the two federally listed threatened and endangered species: Canada lynx and gray wolf, through habitat and access management practices, collaboration with other federal and state agencies, as well as researchers, tribal bands and non-governmental partners. Canada lynx On 24 March 2000, the U.S. Fish and Wildlife Service designated the Canada lynx a “Threatened” species in the lower 48 states. From 2004-2009 the main sources of information about Canada lynx for the SNF included the following: • Since 2003 the Canada lynx study has been investigating key questions needed to contribute to the recovery and conservation of Canada lynx in the Western Great Lakes. Study methods are described in detail in the annual study progress report available online at the following address: http://www.nrri.umn.edu/lynx/ . These methods have included collecting information on distribution, snow tracking lynx, tracking on the ground and in the air radio-collared lynx, studying habitat use, collecting and analyzing genetic samples (for example, from hair or scat) and conducting pellet counts of snowshoe hare (the primary prey). • In 2006 permanent snow tracking routes were established across the Forest. The main objective is to maintain a standardized, repeatable survey to monitor lynx population indices and trends. -
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. -
The Red and Gray Fox
The Red and Gray Fox There are five species of foxes found in North America but only two, the red (Vulpes vulpes), And the gray (Urocyon cinereoargentus) live in towns or cities. Fox are canids and close relatives of coyotes, wolves and domestic dogs. Foxes are not large animals, The red fox is the larger of the two typically weighing 7 to 5 pounds, and reaching as much as 3 feet in length (not including the tail, which can be as long as 1 to 1 and a half feet in length). Gray foxes rarely exceed 11 or 12 pounds and are often much smaller. Coloration among fox greatly varies, and it is not always a sure bet that a red colored fox is indeed a “red fox” and a gray colored fox is indeed a “gray fox. The one sure way to tell them apart is the white tip of a red fox’s tail. Gray Fox (Urocyon cinereoargentus) Red Fox (Vulpes vulpes) Regardless of which fox both prefer diverse habitats, including fields, woods, shrubby cover, farmland or other. Both species readily adapt to urban and suburban areas. Foxes are primarily nocturnal in urban areas but this is more an accommodation in avoiding other wildlife and humans. Just because you may see it during the day doesn’t necessarily mean it’s sick. Sometimes red fox will exhibit a brazenness that is so overt as to be disarming. A homeowner hanging laundry may watch a fox walk through the yard, going about its business, seemingly oblivious to the human nearby. -
Educator's Guide
Educator’s Guide the jill and lewis bernard family Hall of north american mammals inside: • Suggestions to Help You come prepared • essential questions for Student Inquiry • Strategies for teaching in the exhibition • map of the Exhibition • online resources for the Classroom • Correlations to science framework • glossary amnh.org/namammals Essential QUESTIONS Who are — and who were — the North as tundra, winters are cold, long, and dark, the growing season American Mammals? is extremely short, and precipitation is low. In contrast, the abundant precipitation and year-round warmth of tropical All mammals on Earth share a common ancestor and and subtropical forests provide optimal growing conditions represent many millions of years of evolution. Most of those that support the greatest diversity of species worldwide. in this hall arose as distinct species in the relatively recent Florida and Mexico contain some subtropical forest. In the past. Their ancestors reached North America at different boreal forest that covers a huge expanse of the continent’s times. Some entered from the north along the Bering land northern latitudes, winters are dry and severe, summers moist bridge, which was intermittently exposed by low sea levels and short, and temperatures between the two range widely. during the Pleistocene (2,588,000 to 11,700 years ago). Desert and scrublands are dry and generally warm through- These migrants included relatives of New World cats (e.g. out the year, with temperatures that may exceed 100°F and dip sabertooth, jaguar), certain rodents, musk ox, at least two by 30 degrees at night. kinds of elephants (e.g. -
Felis Silvestris, Wild Cat
The IUCN Red List of Threatened Species™ ISSN 2307-8235 (online) IUCN 2008: T60354712A50652361 Felis silvestris, Wild Cat Assessment by: Yamaguchi, N., Kitchener, A., Driscoll, C. & Nussberger, B. View on www.iucnredlist.org Citation: Yamaguchi, N., Kitchener, A., Driscoll, C. & Nussberger, B. 2015. Felis silvestris. The IUCN Red List of Threatened Species 2015: e.T60354712A50652361. http://dx.doi.org/10.2305/IUCN.UK.2015-2.RLTS.T60354712A50652361.en Copyright: © 2015 International Union for Conservation of Nature and Natural Resources Reproduction of this publication for educational or other non-commercial purposes is authorized without prior written permission from the copyright holder provided the source is fully acknowledged. Reproduction of this publication for resale, reposting or other commercial purposes is prohibited without prior written permission from the copyright holder. For further details see Terms of Use. The IUCN Red List of Threatened Species™ is produced and managed by the IUCN Global Species Programme, the IUCN Species Survival Commission (SSC) and The IUCN Red List Partnership. The IUCN Red List Partners are: BirdLife International; Botanic Gardens Conservation International; Conservation International; Microsoft; NatureServe; Royal Botanic Gardens, Kew; Sapienza University of Rome; Texas A&M University; Wildscreen; and Zoological Society of London. If you see any errors or have any questions or suggestions on what is shown in this document, please provide us with feedback so that we can correct or extend the information -
Spatial Characteristics of Residential Development Shift Large Carnivore Prey Habits
The Journal of Wildlife Management; DOI: 10.1002/jwmg.21098 Research Article Spatial Characteristics of Residential Development Shift Large Carnivore Prey Habits JUSTINE A. SMITH,1 Department of Environmental Studies, Center for Integrated Spatial Research, University of California, Santa Cruz, 1156 High Street, Santa Cruz, CA 95064, USA YIWEI WANG, San Francisco Bay Bird Observatory, 524 Valley Way, Milpitas, CA 95035, USA CHRISTOPHER C. WILMERS, Department of Environmental Studies, Center for Integrated Spatial Research, University of California, Santa Cruz, 1156 High Street, Santa Cruz, CA 95064, USA ABSTRACT Understanding how anthropogenic development affects food webs is essential to implementing sustainable growth measures, yet little is known about how the spatial configuration of residential development affects the foraging behavior and prey habits of top predators. We examined the influence of the spatial characteristics of residential development on prey composition in the puma (Puma concolor). We located the prey remains of kills from 32 pumas fitted with global positioning system (GPS) satellite collars to determine the housing characteristics most influencing prey size and species composition. We examined how differences in housing density, proximity, and clustering influenced puma prey size and diversity. We found that at both local (150 m) and regional (1 km) spatial scales surrounding puma kill sites, housing density (but not the clustering of housing) was the greatest contributor to puma consumption of small prey (<20 kg), which primarily comprised human commensals or pets. The species-specific relationships between housing density and prey occupancy and detection rates assessed using camera traps were not always similar to those between housing density and proportions of diet, suggesting that pumas may exercise some diet selectivity. -
Brown Bear (Ursus Arctos) John Schoen and Scott Gende Images by John Schoen
Brown Bear (Ursus arctos) John Schoen and Scott Gende images by John Schoen Two hundred years ago, brown (also known as grizzly) bears were abundant and widely distributed across western North America from the Mississippi River to the Pacific and from northern Mexico to the Arctic (Trevino and Jonkel 1986). Following settlement of the west, brown bear populations south of Canada declined significantly and now occupy only a fraction of their original range, where the brown bear has been listed as threatened since 1975 (Servheen 1989, 1990). Today, Alaska remains the last stronghold in North America for this adaptable, large omnivore (Miller and Schoen 1999) (Fig 1). Brown bears are indigenous to Southeastern Alaska (Southeast), and on the northern islands they occur in some of the highest-density FIG 1. Brown bears occur throughout much of southern populations on earth (Schoen and Beier 1990, Miller et coastal Alaska where they are closely associated with salmon spawning streams. Although brown bears and grizzly bears al. 1997). are the same species, northern and interior populations are The brown bear in Southeast is highly valued by commonly called grizzlies while southern coastal populations big game hunters, bear viewers, and general wildlife are referred to as brown bears. Because of the availability of abundant, high-quality food (e.g. salmon), brown bears enthusiasts. Hiking up a fish stream on the northern are generally much larger, occur at high densities, and have islands of Admiralty, Baranof, or Chichagof during late smaller home ranges than grizzly bears. summer reveals a network of deeply rutted bear trails winding through tunnels of devil’s club (Oplopanx (Klein 1965, MacDonald and Cook 1999) (Fig 2).