Implications for Pronghorn Persistence in Grand Teton

Total Page:16

File Type:pdf, Size:1020Kb

Implications for Pronghorn Persistence in Grand Teton CONSERVATION IMPLICATIONS OF FOOD WEBS INVOLVING WOLVES, COYOTES, AND PRONGHORN by Kim Murray Berger A dissertation submitted in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY in Wildlife Biology UTAH STATE UNIVERSITY Logan, Utah 2007 ii Copyright © Kim Murray Berger 2007 All Rights Reserved iii ABSTRACT Conservation Implications of Food Webs Involving Wolves, Coyotes, and Pronghorn by Kim Murray Berger, Doctor of Philosophy Utah State University, 2007 Major Professor: Eric M. Gese Department: Wildland Resources Coyote (Canis latrans) predation is an important factor in the mortality of neonatal pronghorn (Antilocapra americana). It has been suggested that the extirpation of gray wolves (Canis lupus) contributed to an overall increase in coyote densities and a concomitant rise in predation rates on pronghorn fawns, a process known as trophic cascades. To test this hypothesis we contrasted cause-specific mortality and survival rates of fawns captured at wolf-free and wolf-abundant sites; used demographic modeling to assess the impact of wolves on pronghorn population dynamics; and evaluated coyote survival rates, causes-specific mortality, and spatial segregation with wolves, to identify mechanisms by which wolves limit coyote densities. Fawn survival rates were 400% higher, and coyote densities 33% lower, at sites used by wolves. Wolves killed 56% of transient coyotes, and dispersal rates of transients were 117% higher at the wolf-abundant site; thus, differential effects on solitary coyotes may be an important mechanism by which wolves reduce coyote densities. Our results support the hypothesis that the iv extirpation of wolves contributes to high rates of coyote predation on pronghorn fawns, and add to a growing body of evidence demonstrating the importance of top-down forces in structuring the dynamics of consumer-resource interactions. (169 pages) v ACKNOWLEDGMENTS Funding for this research was provided by Grand Teton National Park and the Biological Resources Division of the U.S. Geological Survey under Cooperative Agreement No. 01CRAG0031, with additional support from the Wildlife Conservation Society, National Wildlife Research Center at Utah State University, NatureFlight Foundation, and Earth Friends Foundation. I thank Noah Weber, Renee Wulff, Mike Nordell, Jana Martinez, Sonja Berger, and the pronghorn capture team volunteers for field assistance, and Jim Pehringer (Wildlife Services) for assistance with coyote captures. Grand Teton National Park, the Wyoming Game & Fish Department, the U.S. Fish & Wildlife Service, and the U.S. Forest Service granted necessary permits. Mike Jimenez, Sarah Dewey, and Lisa Robertson provided wolf locations. I am indebted to Mary Conner for her infinite patience and assistance with issues related to Program MARK, simulation modeling, and statistical analysis, and Gary White for indulging all my “true or false” questions about random effects models and variance components. John Fieberg graciously provided code for the analysis of home-range overlap. I thank Eric Gese for his professionalism throughout the graduate school process, for allowing me to pursue my intellectual interests while still providing guidance when I needed it, and for somehow finding time to assist with field work every year. John Bissonette, Mary Conner, Dan Rosenberg, and Phaedra Budy provided thoughtful comments on my manuscripts. Lastly, I thank Joel for being a source of inspiration, for his patience during my long absences from home, and for being my biggest fan. Kim Murray Berger vi PREFACE Chapter 2, Does Interference Competition with Wolves Limit the Distribution and Abundance of Coyotes?, will be submitted to the Journal of Animal Ecology. The sole co-author will be Eric M. Gese. Chapter 3, Evidence of a Species-Level Trophic Cascade in a Terrestrial Food Web Involving Wolves, Coyotes, and Pronghorn, will be submitted to Ecology. Coauthors will be Eric M. Gese and Joel Berger. Chapter 4, Recolonizing Wolves and Mesopredator Suppression of Coyotes: Impacts on Pronghorn Population Dynamics, will be submitted to Ecological Applications. The sole co-author will be Mary M. Conner. vii CONTENTS Page ABSTRACT....................................................................................................................... iii ACKNOWLEDGMENTS ...................................................................................................v PREFACE.......................................................................................................................... vi LIST OF TABLES............................................................................................................. ix LIST OF FIGURES ........................................................................................................... xi CHAPTER 1. INTRODUCTION .......................................................................................1 2. DOES INTERFERENCE COMPETITION WITH WOLVES LIMIT THE DISTRIBUTION AND ABUNDANCE OF COYOTES?..................6 3. EVIDENCE OF A SPECIES-LEVEL TROPHIC CASCADE IN A TERRESTRIAL FOOD WEB INVOLVING WOLVES, COYOTES, AND PRONGHORN.................................................................................45 4. RECOLONIZING WOLVES AND MESOPREDATOR SUPPRESSION OF COYOTES: IMPACTS ON PRONGHORN POPULATION DYNAMICS ....................................................................84 5. CONCLUSIONS......................................................................................130 APPENDICES .................................................................................................................137 Appendix A. Coyote Densities Predicted by Scat Deposition Index ................138 Appendix B. Description of Known Fate Models Examined in the Analysis of Neonatal Pronghorn Survival ..................................................140 Appendix C. Model-Selection Results Comparing the Performance of Models by Site and Treatment and Resulting Estimates of Neonatal Survival. ...................................................................142 Appendix D. A Technique to Estimate the Number of Reproductive Females in the Population and Neonatal Survival Rates from Count Data ..........................................................................145 Appendix E. Effect of Percentage Yearlings in the Initial Population Vector on the Results of Demographic Modeling ...................................147 viii Appendix F. Effect of Correlation in Overwinter Survival Rates on the Results of Demographic Modeling ..............................................150 Appendix G Permission-to-Use Letters............................................................152 CURRICULUM VITAE..................................................................................................154 ix LIST OF TABLES Table Page 2-1 Model selection results for survival of coyotes at two study sites in Grand Teton National Park, Wyoming, 2001-2004...............................................37 2-2 Seasonal and annual estimates of coyote survival at two study sites in Grand Teton National Park, Wyoming, 2002-2004..........................................................38 2-3 Population densities of coyotes and wolves at three study areas in the Greater Yellowstone Ecosystem, 1991-2005.........................................................39 2-4 Overlap between annual coyote and seasonal wolf home ranges and core areas as measured by percentage of area and utilization distribution overlap index (UDOI) in Grand Teton National Park, Wyoming, 2002-2004.............................40 3-1 Descriptions of variables included in the analysis of pronghorn fawn survival....75 3-2 Model selection results for survival of pronghorn fawns during the first 60 days of life at three study sites in northwestern Wyoming, 2002-2004.................76 3-3 Model-averaged estimates of pronghorn fawn survival during the first 60 days of life at three study sites in northwestern Wyoming, 2002-2004.........................77 4-1 Comparison of observed neonatal survival rates of radio-collared fawns and neonatal survival rates estimated from young:female ratios during fall classification counts.............................................................................................117 4-2 Stage classes, ages, and vital rates used to construct the demographic models...118 4-3 Survival rates for adults and juveniles used to estimate correlation in overwinter survival ..............................................................................................119 4-4 Average population projection matrices for pronghorn based on differences in survival rates of neonates at wolf-free and wolf-abundant sites in Grand Teton National Park, Wyoming ...........................................................................120 4-5 Sample sizes (n) and percentages of radio-collared pronghorn fawns dying by various causes during the first 60 days of life in Grand Teton National Park, Wyoming. ...................................................................................................121 4-6 Model selection results from analysis of neonatal pronghorn survival at wolf- free and wolf-abundant sites in Grand Teton National Park, Wyoming..............122 x 4-7 Comparison of estimated survival rates for male and female fawns based on parameter estimates from the top-ranked model..................................................123 A-1 Results of regression analysis to estimate coyote densities as a
Recommended publications
  • Smithsonian Institution Archives (SIA)
    SMITHSONIAN OPPORTUNITIES FOR RESEARCH AND STUDY 2020 Office of Fellowships and Internships Smithsonian Institution Washington, DC The Smithsonian Opportunities for Research and Study Guide Can be Found Online at http://www.smithsonianofi.com/sors-introduction/ Version 2.0 (Updated January 2020) Copyright © 2020 by Smithsonian Institution Table of Contents Table of Contents .................................................................................................................................................................................................. 1 How to Use This Book .......................................................................................................................................................................................... 1 Anacostia Community Museum (ACM) ........................................................................................................................................................ 2 Archives of American Art (AAA) ....................................................................................................................................................................... 4 Asian Pacific American Center (APAC) .......................................................................................................................................................... 6 Center for Folklife and Cultural Heritage (CFCH) ...................................................................................................................................... 7 Cooper-Hewitt,
    [Show full text]
  • Proceedings of the Seventeenth Wildlife Damage Management Conference, Orange Beach, AL, February 26-March 1, 2017
    PROCEEDINGS SEVENTEENTH WILDLIFE DAMAGE MANAGEMENT CONFERENCE Perdido Beach Resort Orange Beach, AL February 26 – March 1, 2017 Sponsored by USDA APHIS Wildlife Services Tomahawk Live Trap ALFA Alabama Farmers Federation Facilitated by Wildlife Damage Management Working Group of The Wildlife Society Alabama Cooperative Extension System School of Forestry and Wildlife Sciences, Auburn University USDA Wildlife Services-Alabama Editors Dana J. Morin Michael J. Cherry Published at Southern Illinois University, Carbondale, IL USA i Conference Committees Conference Chair Mark D. Smith, Alabama Cooperative Extension System, School of Forestry and Wildlife Sciences, Auburn University Program Committee Jim Armstrong (Chair)—Alabama Cooperative Extension System, School of Forestry and Wildlife Sciences, Auburn University Ken Gruver—UDSA Wildlife Services-Alabama Bronson Strickland—Mississippi State University Extension, Department of Wildlife, Fisheries, and Aquaculture, Mississippi State University Brian Dorr—USDA/APHIS/Wildlife Services, National Wildlife Research Center Michael Mengak—Warnell School of Forestry and Natural Resources, University of Georgia Field Trip Coordinator Leif Stephens—UDSA Wildlife Services-Alabama Proceedings Co-Editors Dana J. Morin, Cooperative Wildlife Research Laboratory, Southern Illinois University Michael J. Cherry, Department of Fish and Wildlife Conservation, Virginia Tech ii The Wildlife Society - Wildlife Damage Management Working Group Officers and Board Members Chair – Joe Caudell; Indiana Department of
    [Show full text]
  • Assabet River National Wildlife Refuge Final Comprehensive Conservation Plan January 2005
    U.S. Fish & Wildlife Service Assabet River National Wildlife Refuge Final Comprehensive Conservation Plan January 2005 This goose, designed by J.N. “Ding” Darling, has become the symbol of the National Wildlife Refuge System The U.S. Fish and Wildlife Service is the principle federal agency for conserving, protecting, and enhancing fish and wildlife in their habitats for the continuing benefit of the American people. The Service manages the 96-million acre National Wildlife Refuge System comprised of 544 national wildlife refuges and thousands of waterfowl production areas. It also operates 65 national fish hatcheries and 78 ecological services field stations. The agency enforces federal wildlife laws, manages migratory bird populations, restores significant fisheries, conserves and restores wildlife habitat such as wetlands, administers the Endangered Species Act, and helps foreign governments with their conservation efforts. It also oversees the Federal Aid program which distributes hundreds of millions of dollars in excise taxes on fishing and hunting equipment to state wildlife agencies. Comprehensive Conservation Plans provide long term guidance for management decisions; set forth goals, objectives, and strategies needed to accomplish refuge purposes; and, identify the Service’s best estimate of future needs. These plans detail program planning levels that are sometimes substantially above current budget allocations and, as such, are primarily for Service strategic planning and program prioritization purposes. The plans do not constitute
    [Show full text]
  • Ecological Responses to Habitat Fragmentation Per Se
    ES48CH01-Fahrig ARI 18 September 2017 16:55 Annual Review of Ecology, Evolution, and Systematics Ecological Responses to Habitat Fragmentation Per Se Lenore Fahrig Geomatics and Landscape Ecology Research Laboratory, Department of Biology, Carleton University, Ottawa, Ontario K1S 5B6, Canada; email: [email protected] Annu. Rev. Ecol. Evol. Syst. 2017. 48:1–23 Keywords First published online as a Review in Advance on landscape pattern, landscape structure, landscape configuration, landscape May 31, 2017 complementation, landscape connectivity, landscape heterogeneity, patch The Annual Review of Ecology, Evolution, and area, patch isolation, edge effect, SLOSS Systematics is online at ecolsys.annualreviews.org https://doi.org/10.1146/annurev-ecolsys-110316- Abstract 022612 For this article, I reviewed empirical studies finding significant ecological Copyright c 2017 by Annual Reviews. responses to habitat fragmentation per se—in other words, significant re- All rights reserved sponses to fragmentation independent of the effects of habitat amount (here- after referred to as habitat fragmentation). I asked these two questions: Are most significant responses to habitat fragmentation negative or positive? And do particular attributes of species or landscapes lead to a predominance of negative or positive significant responses? I found 118 studies reporting ANNUAL REVIEWS Further 381 significant responses to habitat fragmentation independent of habitat Click here to view this article's amount. Of these responses, 76% were positive. Most significant fragmen- online features: • Download figures as PPT slides tation effects were positive, irrespective of how the authors controlled for • Navigate linked references • Download citations habitat amount, the measure of fragmentation, the taxonomic group, the type • Explore related articles • Search keywords of response variable, or the degree of specialization or conservation status of the species or species group.
    [Show full text]
  • Technical Review 12-04 December 2012
    The North American Model of Wildlife Conservation Technical Review 12-04 December 2012 1 The North American Model of Wildlife Conservation The Wildlife Society and The Boone and Crockett Club Technical Review 12-04 - December 2012 Citation Organ, J.F., V. Geist, S.P. Mahoney, S. Williams, P.R. Krausman, G.R. Batcheller, T.A. Decker, R. Carmichael, P. Nanjappa, R. Regan, R.A. Medellin, R. Cantu, R.E. McCabe, S. Craven, G.M. Vecellio, and D.J. Decker. 2012. The North American Model of Wildlife Conservation. The Wildlife Society Technical Review 12-04. The Wildlife Society, Bethesda, Maryland, USA. Series Edited by Theodore A. Bookhout Copy Edit and Design Terra Rentz (AWB®), Managing Editor, The Wildlife Society Lisa Moore, Associate Editor, The Wildlife Society Maja Smith, Graphic Designer, MajaDesign, Inc. Cover Images Front cover, clockwise from upper left: 1) Canada lynx (Lynx canadensis) kittens removed from den for marking and data collection as part of a long-term research study. Credit: John F. Organ; 2) A mixed flock of ducks and geese fly from a wetland area. Credit: Steve Hillebrand/USFWS; 3) A researcher attaches a radio transmitter to a short-horned lizard (Phrynosoma hernandesi) in Colorado’s Pawnee National Grassland. Credit: Laura Martin; 4) Rifle hunter Ron Jolly admires a mature white-tailed buck harvested by his wife on the family’s farm in Alabama. Credit: Tes Randle Jolly; 5) Caribou running along a northern peninsula of Newfoundland are part of a herd compositional survey. Credit: John F. Organ; 6) Wildlife veterinarian Lisa Wolfe assesses a captive mule deer during studies of density dependence in Colorado.
    [Show full text]
  • A Robust Goal Is Needed for Species in the Post‐2020 Global Biodiversity
    Received: 16 April 2020 Revised: 3 September 2020 Accepted: 4 November 2020 DOI: 10.1111/conl.12778 POLICY PERSPECTIVE A robust goal is needed for species in the Post-2020 Global Biodiversity Framework Brooke A. Williams1,2 James E.M. Watson1,2,3 Stuart H.M. Butchart4,5 Michelle Ward1,2 Thomas M. Brooks6,7,8 Nathalie Butt1,2 Friederike C. Bolam9 Simon N. Stuart10,11 Louise Mair9 Philip J. K. McGowan9 Richard Gregory12,13 Craig Hilton-Taylor14 David Mallon15 Ian Harrison6,16 Jeremy S. Simmonds1,2 1 School of Earth and Environmental Sciences, University of Queensland, St Lucia, Queensland, Australia 2 Centre for Biodiversity and Conservation Science, University of Queensland, St Lucia, Queensland, Australia 3 Wildlife Conservation Society, Global Conservation Program, Bronx, New York 4 BirdLife International, Cambridge, UK 5 Department of Zoology, Cambridge University, Cambridge, UK 6 IUCN, Gland, Switzerland 7 World Agroforestry Center (ICRAF), University of the Philippines Los Baños, Laguna, Philippines 8 Institute for Marine and Antarctic Studies, University of Tasmania, Hobart, Australia 9 School of Natural and Environmental Sciences, Newcastle University, Newcastle upon Tyne, UK 10 Synchronicity Earth, London, UK 11 A Rocha International, London, UK 12 RSPB Centre for Conservation Science, The Lodge, Sandy, Bedfordshire, UK 13 Department of Genetics, Evolution and Environment, Centre for Biodiversity & Environment Research, University College London, London, UK 14 IUCN, Cambridge, UK 15 Division of Biology and Conservation Ecology, Manchester Metropolitan University, Manchester, UK 16 Conservation International, Arlington, Virginia Correspondence Brooke Williams, School of Earth and Abstract Environmental Sciences, University of In 2010, Parties to the Convention on Biological Diversity (CBD) adopted the Queensland, St Lucia 4072, Australia.
    [Show full text]
  • Sierra Leone Biodiversity Country Study
    National Biodiversity Report TABLE OF CONTENTS LIST OF ABBREVIATIONS AND ACRONYMS EXECUTIVE SUMMARY I. INTRODUCTION II. BACKGROUND TO THE SIERRA LEONE BIODIVERSITY COUNTRY STUDY A. Introduction B. Status and Trends of Components of Biodiversity C. The value of the Biodiversity of Sierra Leone D. Major Threats to Biodiversity in Sierra Leone E. Legal and Policy Frameworks for Biodiversity Conservation and Sustainable Use F. Institutional Responsibilities and Capacities G. Institutional Arrangements for the Implementation of Strategic Recommendations III. GOALS AND OBJECTIVES A. The Overall Vision B. Goals and Strategic Objectives C. Sector Specific Conservation Goals and Objectives IV. THE NATIONAL BIODIVERSITY STRATEGY A. Introduction B. Summary of Thematic (sectoral) Strategies C. Summary of General Measures (Cross-cutting Strategies) V. COLLABORATION AND PARTNERSHIP i VI. THE ACTION PLAN A. Introduction B. Thematic Action Plans C. Cross-sectoral Action Plan D. Schedule of Implementation E. The Budget F. Monitoring and Evaluation VII. SHARING OF NATIONAL EXPERIENCE ANNEX NBSAP IMPLEMENTATION SCHEDULE REFERENCES ii LIST OF ABBREVIATION AND ACRONYMS ADB - African Development Bank AFRC - Armed Forces Revolutionary Council BSAP - Biodiversity Strategy Action Plan CBD - Convention on Biological Diversity CCD - Convention to Combat Desertification CHESIL - Council for Human Ecology of Sierra Leone CILSS - Convention Establishing a Permanent Inter-State Committee for the Control of Draught in the Sahel CITES - Convention on International Trade
    [Show full text]
  • A Comparative Health Assessment of Urban and Non-Urban Mule Deer (Odocoileus Hemionus) in the Kootenay Region, British Columbia, Canada
    A Comparative Health Assessment of Urban and Non-Urban Mule Deer (Odocoileus hemionus) in the Kootenay Region, British Columbia, Canada Thesis Presented in Partial Fulfillment of the Requirements for the Degree Master of Science in the Graduate School of The Ohio State University By Amélie Mathieu, DMV Graduate Program in Comparative and Veterinary Medicine The Ohio State University 2018 Thesis Committee Dr. Thomas E. Wittum, Advisor Dr. Mark S. Flint, Co-Advisor Dr. Barbara A. Wolfe Dr. Randall E. Junge 1 Copyright by Amélie Mathieu 2018 2 Abstract The provincial wildlife management agency, British Columbia Ministry of Forests, Lands, Natural Resource Operations and Rural Development, performed a translocation trial from 2015 to 2017 to control the urban mule deer (Odocoileus hemionus; uMD) overpopulation and supplement the declining non-urban mule deer (nuMD) population in the Kootenay region, British Columbia, Canada. Several local communities are now considering using uMD translocations as a long-term wildlife management method. The aim of this study was to characterize the health risks associated with the translocation initiative by comparing pathogen exposure, body condition scores (BCS) and pregnancy rates of urban and non-urban mule deer (nuMD) and to develop predictive disease models to inform management decisions related to urban deer translocations. Blood samples collected from 200 free-ranging mule deer captured in urban and non-urban environments in the Kootenay region from 2014 to 2017 were tested for exposure to selected pathogens and pregnancy status. Body condition scoring (BCS) and morphometric examinations were performed for each deer. BCS averaged 3.4 on a five-point scale, was greater in nuMD, and significantly differed between years.
    [Show full text]
  • Robert F. Rockwell 69 Old Stagecoach Road Redding, CT 06896 212.769.5793 (W) 917.539.2064 (C) [email protected]
    Robert F. Rockwell 69 Old Stagecoach Road Redding, CT 06896 212.769.5793 (w) 917.539.2064 (c) [email protected] http://research.amnh.org/users/rfr Professional Experience Biology Department, City College of The City University of New York Professor (1986-present); Associate Professor (1981-1985); Assistant Professor (1976-1980); Chair of Graduate Studies (1993-1996; 1997-1998) The Graduate School and University Center, City University of New York Professor (1986-present) Chair of Ecology and Evolutionary Biology subprogram of the Biology Ph.D. program (2002-2010) Ornithology Department, American Museum of Natural History Research Associate – non-salaried (1986-present) Center for Environmental Research and Conservation, Columbia University Adjunct Senior Scientist – non-salaried (1999-present) Richard Gilder Graduate School, American Museum of Natural History Adjunct Professor – non-salaried (2011-present) Institute of Arctic Biology, University of Alaska Fairbanks Principal Research Scientist, non-salaried (2012-present) Hudson Bay Project Corporation President – non-salaried (1996-present) Education Ph.D. Department of Biology, Queen's University, Kingston, Ontario (1975) M.Sc. Department of Biology, Wright State University, Dayton, Ohio (1971) B.Sc. Department of Biology, Wright State University, Dayton, Ohio (1969) Professional Societies American Association for the Advancement of Science, American Ornithologists' Union (Fellow), American Society of Naturalists, Association of Field Ornithologists, British Ecological Society, Cooper Ornithological
    [Show full text]
  • Development of Protocols to Inventory Or Monitor Wildlife, Fish, Or Rare Plants
    United States Department Development of Protocols of Agriculture Forest Service To Inventory or Monitor Gen. Tech. Report WO-72 Wildlife, Fish, or Rare Plants June 2006 United States Department of Agriculture Development of Protocols Forest Service To Inventory or Monitor Gen. Tech. Report WO-72 Wildlife, Fish, or Rare Plants June 2006 By David Vesely Brenda C. McComb Christina D. Vojta Lowell H. Suring Juraj Halaj Richard S. Holthausen Benjamin Zuckerberg Patricia M. Manley The proper citation for this document is as follows: Vesely, D.; McComb, B.C.; Vojta, C.D.; Suring, L.H.; Halaj, J.; Holthausen, R.S.; Zuckerberg, B.; Manley, P.M. 2006. Development of Protocols To Inventory or Monitor Wildlife, Fish, or Rare Plants. Gen. Tech. Rep. WO-72. Washington, DC: U.S. Department of Agriculture, Forest Service. 100 p. Cover photos. Monitoring wildlife, rare plants, and their habitats is conveyed through three photos: (1) Peromyscus maniculatus, on Pesola scale (photo credit: Dean E. Pearson); (2) western prairie fringed orchid (Platanthera praeclara) (photo credit: Carolyn Hull Sieg); and (3) measuring a ponderosa pine (Pinus ponderosa) log in Idaho (photo credit: Victoria A. Saab). The U.S. Department of Agriculture (USDA) prohibits discrimination in all its programs and activities on the basis of race, color, national origin, age, disability, and where applicable, sex, marital status, familial status, parental status, religion, sexual orientation, genetic information, political beliefs, reprisal, or because all or part of an individual’s income is derived from any public assistance program. (Not all prohibited bases apply to all programs.) Persons with disabilities who require alternative means for communication of program information (Braille, large print, audiotape, etc.) should contact USDA’s TARGET Center at (202) 720-2600 (voice and TDD).
    [Show full text]
  • Chesapeake Marshlands National Wildlife Refuge Complex
    U.S. Fish & Wildlife Service Chesapeake Marshlands National Wildlife Refuge Complex Comprehensive Conservation Plan September 2006 Cover Pictures: Premier Blackwater NWR habitat, USFWS Photo (in background) Delmarva Fox Squirrel, USFWS Photo Bald Eagle, USFWS Photo Canada Geese, USFWS Photo This goose, designed by J.N. “Ding” Darling, has become the symbol of the National Wildlife Refuge System. The U.S. Fish and Wildlife Service is the principal Federal agency responsible for conserving, protecting, and enhancing fish, wildlife, plants, and their habitats for the continuing benefit of the American people. The Service manages the 95-million acre National Wildlife Refuge System comprised of more than 545 national wildlife refuges and thousands of waterfowl production areas. It also operates 65 national fish hatcheries and 78 ecological services field stations. The agency enforces Federal wildlife laws, manages migratory bird populations, restores nationally significant fisheries, conserves and restores wildlife habitat such as wetlands, administers the Endangered Species Act, and helps foreign governments with their conservation efforts. It also oversees the Federal Assistance Program which distributes hundreds of millions of dollars in excise taxes on fishing and hunting equipment to state wildlife agencies. Comprehensive Conservation Plans provide long term guidance for management decisions and set forth goals, objectives, and strategies needed to accomplish refuge purposes and identify the Service’s best estimate of future needs. These plans detail program planning levels that are sometimes substantially above current budget allocations and, as such, are primarily for Service strategic planning and program prioritization purposes. The plans do not constitute a commitment for staffing increases, operational and maintenance increases, or funding for future land acquisition.
    [Show full text]
  • NACCB 2012 St North Biology Americacongress Forconservation Society Biology Forconservation North America Section
    NACCB 2012 Abstracts 1st North America Congress for Conservation Biology Bridging the Gap: Connecting People, Nature, and Climate Society for Conservation Biology North America Section NACCB 2012 Society for Conservation Biology North America Section North America Congress for Conservation Biology Congress Abstracts Ordered by surname of first author. Author index at the end of the book. The Inaugural SCB North American Congress for Conservation Biology · Oakland, California · July 15-18, 2012 Monday, July 16 9:45 Can Brain Size Help using a novel application of multinomial logistic Predict Conservation Status Of Mammalian regression. The output of this method is a vector of Species? the relative probability of occupancy by each of a Abelson, Eric*, Stanford University set of vegetation types, for each pixel in the As global anthropogenic pressure on wildlife landscape. The overall vulnerability of vegetation mounts, conservationists are faced with finding to climate change can then be quantified as the salient characteristics that predict population change in modeled probabilities between the decline in mammals. Confounding the ability to vectors modeled under present versus future preserve mammalian species is the complexity of climates. These changes capture the likelihood of traits and behaviors that influence their ability to long-term climate-driven vegetation change for thrive in changing landscapes. While the brain is each pixel, without relying on specific predictions the seat of information processing, storage and the of present and future vegetation types. Based on origination of behaviors, the importance of neural this model, we find that the vegetation patches physiology to conservation is poorly understood. with greatest vulnerability to climate change are Encephalization (here defined as brain size those that lie close to the edge of the climate corrected for body size and phylogeny) has been suitability envelopes for their respective vegetation shown to be correlated with behavioral flexibility in types.
    [Show full text]