Minnesota's Wildlife Action Plan 2015-2025

Total Page:16

File Type:pdf, Size:1020Kb

Minnesota's Wildlife Action Plan 2015-2025 Glossary of Terms and Acronyms Terms adaptive management. A decision process that promotes flexible decision making in the face of uncertainty or changing conditions, and allows for adaptation as the effect of management actions and outcomes become better understood. Monitoring of conservation actions and outcomes is a key component of adaptive management. biological diversity. The variety of living organisms that are recognized and analyzed by biologists at three levels of organization: ecosystems; the species that comprise those ecosystems; and the genetic variability within those species (Wilson 2001). Species present in an ecosystem include animals, plants, fungi, protists, and bacteria and range enormously in size and ecological functions. Functional diversity (see definition) is an aspect of biological diversity that some scientists believe may be of particular importance to ecosystem resilience. Biological diversity can be measured at different spatial scales (Whittaker 1960): • alpha-diversity: the number of species found in a small homogeneous area. • beta-diversity: extent of change in species composition among habitats or communities. • gamma-diversity: total species diversity in a landscape. Conservation Focus Areas. Priority areas for working with partners to identify, design, and implement conservation actions and report on the effectiveness toward achieving the goals and objectives defined in the Wildlife Action Plan. Conservation Focus Areas are intended to focus conservation efforts over the next 10 years to maintain and enhance the resiliency of the Wildlife Action Network. ecological classification system. A system used to identify, describe, and map progressively smaller areas of land with increasingly uniform ecological features. The system uses associations of biotic and environmental factors, including climate, geology, topography, soils, hydrology, and vegetation. Map units for six levels occur in Minnesota: Provinces, Sections, Subsections, Land Type Associations, Land Types, and Land Type Phases. For more information see http://www.dnr.state.mn.us/ecs/index. html. ecological engineers. Species that alter the habitat to such a degree that they modify the fates and opportunities of other species (for example, beavers). ecosystem function. The flows of energy and material in food webs and cycles. ecosystem process. A natural phenomenon in an ecosystem that leads toward a particular result. ecosystem services. The benefits that people obtain from ecosystems. These include a wide range of products and services that include provisioning services such as food, water, timber, and fiber; regulation services such as the regulation of climate, floods, disease, wastes, and water quality; cultural services such as recreation, aesthetic enjoyment, and spiritual fulfillment; and supporting services such as soil formation, photosynthesis, and nutrient cycling. ecosystem structure. The distribution of energy, materials, and species. ecotone. A region of transition between two biological communities. focal species. Species that have key, broad-scale ecosystem-level effects. These species affect ecological systems in diverse ways and can be further described as indicator species, keystone species, ecological engineers, umbrella species, and link species. See separate definitions for these concepts. Glossary of Terms and Acronyms Minnesota’s Wildlife Action Plan 2015‐2025 67 functional diversity. Species that influence ecosystem dynamics such as stability, productivity, nutrient balance, and water purification. Functional groups of species are sets of species that have similar traits, which contribute to the likelihood that the group will be similar in its effects on ecosystem functioning (Tilman 2001). Another aspect of species function in osec ystems is response diversity (see definition). Measures of functional diversity can take various forms; some examples are as fol- lows: • functional richness: the number of functional groups present in an area. • functional diversity: the number of functional groups present relative to the abundance of indi- viduals within a functional group (Jost 2007, Tuomisto 2010). • functional evenness: calculated as the quotient between functional diversity and functional rich- ness (Tuomisto 2012). • functional redundancy: the number of species contributing similarly to an ecosystem function (Laliberte et al. 2010) and can be measured as the average number of species within each func- tional group (Allen et al. 2005). • cross-scale redundancy: the average number of spatial scales at which each function is repre- sented (Allen et al. 2005). habitat. A place (ecosystem) where a species lives and interacts with the physical environment and other species. Some species require multiple habitats at different stages in their life cycle. hydrologic unit code (HUC). A mapping system of watersheds at nested scales, where a smaller number represents a coarser scale. indicator species. Species that tell us about the status of other species and habitats or the impacts of a stressor. keystone species. Species that have greater effects on ecological processes than would be predicted from their abundance or biomass alone. Lakes of Biological Significance. https://gisdata.mn.gov/dataset/env-lakes-of-biological-signific link species. Species that exert critical roles in the transfer of matter and energy across trophic levels (of a food web) or provide critical links for energy transfer within complex food webs. Marxan. A conservation prioritization mapping software that assists in finding the most efficient ways of physically linking conservation target areas. recruitment. The increase in a natural population as juveniles are born and survive, or immigrants arrive. Usually measured or detected by the presence multiple age-classes of juveniles. resilience. The capacity of a system to absorb disturbance and reorganize while undergoing change so as to still retain essentially the same function, structure, and feedbacks, and therefore identity (Folke et al. 2010). response diversity. The variability of responses to environmental change among species contributing to the same ecosystem function (Elmqvist et al. 2003, Laliberte et al. 2010). Sites of Biodiversity Significance. http://www.dnr.state.mn.us/eco/mcbs/biodiversity_guidelines.html species. A population whose members are able to interbreed freely under natural conditions. species viability. A viable species is one with self-sustaining and interacting populations that are well- distributed throughout the species’ range. Self-sustaining populations are those that are sufficiently Glossary of Terms and Acronyms Minnesota’s Wildlife Action Plan 2015‐2025 68 abundant and have sufficient diversity to display the array of life-history strategies and forms to provide for their long-term persistence and adaptability over time. The definition of the term well- distributed can vary based on current, historic, and potential population and habitat conditions. Maintaining viability is a means of ensuring, as much as possible, that a species will not go extinct in the foreseeable future (U.S. Department of Agriculture. Committee of Scientists 1999). status and trend monitoring. Long-term measurement of one or more variables, such as species abun- dance or water clarity, used to identify patterns of change and determine the state of one or more species, habitats, or ecosystems. stewardship species. A stewardship species is defined as either: A. Species for which populations in Minnesota represent a significant portion of their North American breeding or wintering population, or B. Species whose Minnesota populations are stable, but whose populations outside of Minnesota have declined or are declining in a substantial part of their range. C. Species for which migrating populations congregating in Minnesota represent a significant portion of the North American population. Stream Index of Biological Integrity. http://www.pca.state.mn.us/index.php/water/water-monitor- ing-and-reporting/biological-monitoring/index-of-biological-integrity.html stressor. A condition that directly or indirectly negatively impacts a habitat or species. target habitat. Habitats that are present in a Conservation Focus Area that are utilized by Species in Greatest Conservation Need and require management attention to be sustained or enhanced over time. Target habitats are identified for individual Conservation Focus Areas. target species. An individual or group of Species in Greatest Conservation Need that inhabit target habi- tats and require special management attention or could serve as focal species for monitoring purpos- es. Target species are identified for individual Conservation Focus Areas. umbrella species. Species that either have large area requirements or use multiple habitats and thus overlap the habitat requirements of many other species. vulnerability assessment. A tool used in adaptation planning for informing the development and im- plementation of resource management practices. Vulnerability assessment as it pertains to climate change is usually structured around three distinct components: sensitivity, exposure, and adaptive capacity. Wildlife Action Network. Mapped aquatic and terrestrial habitats, buffers, and connections that rep- resent a diversity of quality habitats that contain populations of Species in Greatest Conservation Need. Acronyms AMSD Adaptive Management Spatial Database BMP Best Management Practice CFA Conservation Focus Area DNR Department of Natural
Recommended publications
  • Biocultural Indicators to Support Locally Led Environmental Management and Monitoring
    Copyright © 2019 by the author(s). Published here under license by the Resilience Alliance. DeRoy, B. C., C. T. Darimont, and C. N. Service. 2019. Biocultural indicators to support locally led environmental management and monitoring. Ecology and Society 24(4):21. https://doi.org/10.5751/ES-11120-240421 Synthesis Biocultural indicators to support locally led environmental management and monitoring Bryant C. DeRoy 1,2, Chris T. Darimont 1,2 and Christina N. Service 1,2,3 ABSTRACT. Environmental management (EM) requires indicators to inform objectives and monitor the impacts or efficacy of management practices. One common approach uses “functional ecological” indicators, which are typically species whose presence or abundance are tied to functional ecological processes, such as nutrient productivity and availability, trophic interactions, and habitat connectivity. In contrast, and used for millennia by Indigenous peoples, biocultural indicators are rooted in local values and place- based relationships between nature and people. In many landscapes today where Indigenous peoples are reasserting sovereignty and governance authority over natural resources, the functional ecological approach to indicator development does not capture fundamental values and ties to the natural world that have supported social-ecological systems over the long term. Accordingly, we argue that the development and use of biocultural indicators to shape, monitor, and evaluate the success of EM projects will be critical to achieving ecological and social sustainability today. We have provided a framework composed of criteria to be considered when selecting and applying meaningful and efficacious biocultural indicators among the diverse array of potential species and values. We used a case study from a region now referred to as coastal British Columbia, Canada, to show how the suggested application of functional ecological indicators by the provincial government created barriers to the development of meaningful cogovernance.
    [Show full text]
  • Analysis of Habitat Fragmentation and Ecosystem Connectivity Within the Castle Parks, Alberta, Canada by Breanna Beaver Submit
    Analysis of Habitat Fragmentation and Ecosystem Connectivity within The Castle Parks, Alberta, Canada by Breanna Beaver Submitted in Partial Fulfillment of the Requirements for the Degree of Master of Science in the Environmental Science Program YOUNGSTOWN STATE UNIVERSITY December, 2017 Analysis of Habitat Fragmentation and Ecosystem Connectivity within The Castle Parks, Alberta, Canada Breanna Beaver I hereby release this thesis to the public. I understand that this thesis will be made available from the OhioLINK ETD Center and the Maag Library Circulation Desk for public access. I also authorize the University or other individuals to make copies of this thesis as needed for scholarly research. Signature: Breanna Beaver, Student Date Approvals: Dawna Cerney, Thesis Advisor Date Peter Kimosop, Committee Member Date Felicia Armstrong, Committee Member Date Clayton Whitesides, Committee Member Date Dr. Salvatore A. Sanders, Dean of Graduate Studies Date Abstract Habitat fragmentation is an important subject of research needed by park management planners, particularly for conservation management. The Castle Parks, in southwest Alberta, Canada, exhibit extensive habitat fragmentation from recreational and resource use activities. Umbrella and keystone species within The Castle Parks include grizzly bears, wolverines, cougars, and elk which are important animals used for conservation agendas to help protect the matrix of the ecosystem. This study identified and analyzed the nature of habitat fragmentation within The Castle Parks for these species, and has identified geographic areas of habitat fragmentation concern. This was accomplished using remote sensing, ArcGIS, and statistical analyses, to develop models of fragmentation for ecosystem cover type and Digital Elevation Models of slope, which acted as proxies for species habitat suitability.
    [Show full text]
  • Umbrella Species As a Conservation Planning Tool
    Umbrella Species as a Conservation Planning Tool An Assessment Using Resident Birds in Hemiboreal and Boreal Forests Jean-Michel Roberge Faculty of Natural Resources and Agricultural Sciences Department of Conservation Biology Uppsala Doctoral thesis Swedish University of Agricultural Sciences Uppsala 2006 Acta Universitatis Agriculturae Sueciae 2006: 84 ISSN 1652-6880 ISBN 91-576-7133-8 © 2006 Jean-Michel Roberge, Uppsala Tryck: SLU Service/Repro, Uppsala 2006 Abstract Roberge, J.-M. 2006. Umbrella species as a conservation planning tool: an assessment using resident birds in hemiboreal and boreal forests. Doctor’s dissertation. ISSN 1652-6880, ISBN 91-576-7133-8. In northern Europe, a long history of anthropogenic land use has led to profound changes within forest ecosystems. One of the proposed approaches for conservation and restoration of forest biodiversity is the use of umbrella species, whose conservation would confer protection to large numbers of naturally co-occurring species. This thesis aims to evaluate some of the prerequisites to the umbrella species concept, focusing on resident birds in hemiboreal and boreal forests. The study was performed in four areas belonging to the southern Baltic Sea region: central and southern Sweden, south-central Lithuania and northeastern Poland. A review of empirical evaluations of the umbrella species concept performed in various systems suggested that multispecies approaches addressing the requirements of both the umbrellas and the beneficiary species have better potential than approaches based coarsely on the area needs of single species. An analysis of co-occurrence patterns among resident forest birds in landscape units of 100 ha showed that some species reliably indicated high species richness through their presence.
    [Show full text]
  • Umbrella Species: Critique and Lessons from East Africa
    Animal Conservation (2003) 6, 171–181 © 2003 The Zoological Society of London DOI:10.1017/S1367943003003214 Printed in the United Kingdom Umbrella species: critique and lessons from East Africa T. M. Caro Department of Wildlife, Fish, and Conservation Biology, University of California, Davis, CA 96516, USA Tanzania Wildlife Research Institute, P.O. Box 661, Arusha, Tanzania (Received 28 April 2002; accepted 26 November 2002) Abstract Umbrella species are ‘species with large area requirements, which if given sufficient protected habitat area, will bring many other species under protection’. Historically, umbrella species were employed to delineate specific reserve boundaries but are now used in two senses: (1) as aids to identifying areas of species richness at a large geographic scale; (2) as a means of encompassing populations of co-occuring species at a local scale. In the second sense, there is a dilemma as to whether to maximize the number or viability of background populations; the umbrella population itself needs to be viable as well. Determining population viability is sufficiently onerous that it could damage the use of umbrella species as a conservation shortcut. The effectiveness of using the umbrella-species concept at a local scale was investigated in the real world by examining reserves in East Africa that were gazetted some 50 years ago using large mammals as umbrella species. Populations of these species are still numerous in most protected areas although a few have declined. Populations of other, background species have in general been well protected inside reserves; for those populations that have declined, the causes are unlikely to have been averted if reserves had been set up using other conservation tools.
    [Show full text]
  • Selecting Umbrella Species for Conservation: a Test of Habitat Models and Niche Overlap for Beach-Nesting Birds
    Biological Conservation 203 (2016) 233–242 Contents lists available at ScienceDirect Biological Conservation journal homepage: www.elsevier.com/locate/bioc Selecting umbrella species for conservation: A test of habitat models and niche overlap for beach-nesting birds B. Maslo a,b,⁎,K.Leua, C. Faillace a,M.A.Westonc,T.Poverd,T.A.Schlachere a Ecology, Evolution, and Natural Resources, Rutgers, The State University of New Jersey, New Brunswick, NJ, USA b Rutgers Cooperative Extension, New Jersey Agricultural Experiment Station, Rutgers, The State University of New Jersey, New Brunswick, NJ, USA c Centre for Integrative Biology, Deakin University, Geelong, Australia d Conserve Wildlife Foundation of New Jersey, Trenton, NJ, USA e School of Science and Engineering, University of the Sunshine Coast, Maroochydore, Australia article info abstract Article history: Umbrella species are rarely selected systematically from a range of candidate species. On sandy beaches, birds Received 18 March 2016 that nest on the upper beach or in dunes are threatened globally and hence are prime candidates for conservation Received in revised form 8 August 2016 intervention and putative umbrella species status. Here we use a maximum-likelihood, multi-species distribution Accepted 12 September 2016 modeling approach to select an appropriate conservation umbrella from a group of candidate species occupying Available online xxxx similar habitats. We identify overlap in spatial extent and niche characteristics among four beach-nesting bird species of conservation concern, American oystercatchers (Haematopus palliatus), black skimmers (Rynchops Keywords: Beach-nesting birds niger), least terns (Sterna antillarum) and piping plovers (Charadrius melodus), across their entire breeding Conservation shortcuts range in New Jersey, USA.
    [Show full text]
  • Biology for Queensland
    BIOLOGY FOR QUEENSLAND AN AUSTRALIAN PERSPECTIVE UNITS LORRAINE HUXLEY MARGARET WALTER SERIES CONSULTANT 3 & 4 ROBYN FLEXMAN SAMPLE CHAPTER UNCORRECTED PAGE PROOFS To access a sample of the additional digital resources and teacher materials that support this series, visit: www.oup.com.au/ sampledigital For more information, or to book an appointment with your local sales consultant, contact: Tegan Hooper Email: [email protected] Mobile: 0456 655 441 Melissa Wearne Email: [email protected] Mobile: 0447 557 931 AN AUSTRALIAN PERSPECTIVE BIOLOGY FOR QUEENSLAND UNITS 3 & 4 LORRAINE HUXLEY MARGARET WALTER SERIES CONSULTANT ROBYN FLEXMAN DRAFT 1 Oxford University Press is a department of the University of Oxford. It furthers the University’s objective of excellence in research, scholarship, and education by publishing worldwide. Oxford is a registered trademark of Oxford University Press in the UK and in certain other countries. CONTENTS Published in Australia by Oxford University Press Level 8, 737 Bourke Street, Docklands, Victoria 3008, Australia. © Lorraine Huxley, Margaret Walter Using Biology for Queensland: An Australian 3.6 Identifying features in terrestrial The moral rights of the authors have been asserted Perspective Units 3 & 4 ����������������������������������������������� VI ecosystems ��������������������������������������������������������XXX First published 2020 3rd Edition Acknowledgements ����������������������������������������������������� X 3.7 Biodiversity in ecosystems ����������������������������XXX All rights reserved. No part of this publication may be reproduced, stored in a retrieval system, or transmitted, 3.8 Measuring features of an in any form or by any means, without the prior permission in writing of Oxford University Press, or as expressly permitted by law, by licence, or under terms agreed with the reprographics rights organisation.
    [Show full text]
  • Defining and Evaluating the Umbrella Species Concept for Conserving
    Contributed Paper Defining and Evaluating the Umbrella Species Concept for Conserving and Restoring Landscape Connectivity IAN BRECKHEIMER,∗ NICK M. HADDAD,† WILLIAM F. MORRIS,‡ ANNE M. TRAINOR,§ WILLIAM R. FIELDS,∗∗ R. TODD JOBE,†† BRIAN R. HUDGENS,‡‡ AARON MOODY,§§ AND JEFFREY R. WALTERS∗∗∗ ∗Department of Biology, University of Washington, Box 351800, Seattle, WA 98195, U.S.A., email [email protected] †Department of Biological Science, North Carolina State University, Box 7617, Raleigh, NC 27695, U.S.A. ‡Department of Biology, Duke University, 125 Science Drive, Durham, NC 27708, U.S.A. §Yale University, School of Forestry and Environmental Studies, 370 Prospect Street, New Haven, CT 06511, U.S.A. ∗∗USGS Patuxent Wildlife Research Center, SO Conte Anadromous Fish Research Lab, 1 Migratory Way, Turner Falls, MA 01376, U.S.A. ††Signal Innovations Group, Inc., 4721 Emperor Boulevard, Suite 330, Durham, NC 27703, U.S.A. ‡‡Institute for Wildlife Studies, P.O. Box 1104, Arcata, CA 95518, U.S.A. §§Department of Geography, Box 3220, University of North Carolina at Chapel Hill, Chapel Hill, NC 27599, U.S.A. ∗∗∗Department of Biological Sciences, Virginia Tech, 1405 Perry Street, Box 0406, Blacksburg, VA 24061, U.S.A. Abstract: Conserving or restoring landscape connectivity between patches of breeding habitat is a common strategy to protect threatened species from habitat fragmentation. By managing connectivity for some species, usually charismatic vertebrates, it is often assumed that these species will serve as conservation umbrellas for other species. We tested this assumption by developing a quantitative method to measure overlap in dispersal habitat of 3 threatened species—a bird (the umbrella), a butterfly, and a frog—inhabiting the same fragmented landscape.
    [Show full text]
  • Species Biodiversity
    SPECIES: THE CORNERSTONE OFBIODIVERSITY AN EXAMINATION OF HOW SPECIES DIVERSITY IS THE KEY TO A HEALTHY PLANET, AND A CLOSER LOOK AT A MAJOR TOOL USED IN BIODIVERSITY CONSERVATION 4 Kathryn Pintus, IUCN So far, we’ve had a look at genetic diversity, and we’ve learned that genes are responsible for the wide variety of species that exist on Earth. But what exactly is a species? A species is a basic biological unit, describing organisms which are able to breed together and produce fertile offspring (offspring that are able to produce young). The above statement is a fairly widely accepted definition, and in some cases it is easy enough to determine whether two organisms are separate species simply by looking at them; the mighty blue whale is clearly not the same species as the fly agaric mushroom. A BANANA SLUG EATING A RASPBERRY AT A CAMPSITE IN REDWOOD NATIONAL PaRK, CALIFORNIA, USA. © Anthony Avellano (age 14) 39 CHAPTER 4 | Species: the cornerstone of biodiversity However, the situation is not taxonomy, and this provides and where it lives), and others always quite so straightforward. us with a common language that still on phylogenetics (using The science of describing and we can all use to communicate molecular genetics to look at classifying organisms is called about species, but it can get evolutionary relatedness). For rather complicated! Biology is this reason, when considering split into several fields, including two organisms which on botany, zoology, ecology, the surface may look almost genetics and behavioural identical, scientists sometimes science, and scientists from each disagree as to how to classify of these branches of biology will them.
    [Show full text]
  • Evaluating Policy-Relevant Surrogate Taxa for Biodiversity Conservation: a Case Study from British Columbia
    Canadian Journal of Zoology Evaluating policy-relevant surrogate taxa for biodiversity conservation: a case study from British Columbia Journal: Canadian Journal of Zoology Manuscript ID cjz-2019-0178.R1 Manuscript Type: Note Date Submitted by the 24-Sep-2019 Author: Complete List of Authors: Falconer, Sarah; University of British Columbia Okanagan, Biology Ford, Adam; University of British Columbia Okanagan, Biology Is your manuscript invited for consideration in a Special Not applicableDraft (regular submission) Issue?: WILDLIFE MANAGEMENT < Discipline, conservation, game species, Keyword: HABITAT < Habitat, indicator species https://mc06.manuscriptcentral.com/cjz-pubs Page 1 of 37 Canadian Journal of Zoology Evaluating policy-relevant surrogate taxa for biodiversity conservation: a case study from British Columbia Sarah Falconer a, Adam T. Ford a,b a Department of Biology, The University of British Columbia - Okanagan Campus, 1177 Research Road, Kelowna, British Columbia, Canada V1V 1V7 b Corresponding author: [email protected] Draft https://mc06.manuscriptcentral.com/cjz-pubs Canadian Journal of Zoology Page 2 of 37 2 Abstract Conservation efforts often lead to a small proportion of species receiving a disproportionate amount of attention. This bias in finding may help or hinder broader goals of biodiversity conservation depending on the surrogacy value of the well-funded species. Surrogate species are selected to represent other taxa in a shared environment when it would be costly or impractical to obtain information on individual taxa. We compared the surrogacy value of common groups of taxa implicated in conservation – game species, carnivores, non-game species, and other species. Using a publicly available dataset of species-habitat associations, we compared the surrogacy value for 1012 species and 64 habitat types in British Columbia.
    [Show full text]
  • Using the Focal Species Approach for Conserving Biodiversity in Landscapes Managed for Forestry
    Using the Focal Species Approach for Conserving Biodiversity in Landscapes Managed for Forestry By Susan J. Hannon and Cindy McCallum Sustainable Forest Management Network G-208, Biological Sciences Building University of Alberta Edmonton, Alberta T6G 2E9 CANADA Phone: (780) 492-6659 Fax: (780) 492-8160 Email: [email protected] http://www.ualberta.ca/sfm/ A Network of Centres of Excellence Un réseau des centres d’excellence OUR PARTNERS AND AFFILIATES MARCH 2004 GRANTING COUNCILS ABORIGINAL GROUPS • Networks of Centres of Excellence (NCE) Program • Gwich'in Renewable Resource Board • Natural Sciences and Engineering Research • Heart Lake First Nation THE SUSTAINABLE FOREST MANAGEMENT NETWORK Council of Canada (NSERC) • Kaska Tribal Council • Social Sciences and Humanities Research • Little Red River/Tall Cree Nation Established in 1995, the Sustainable Forest Management Network (SFM Network) is an incorporated, non-profit Council of Canada (SSHRC) • Moose Cree First Nation research organization based at the University of Alberta in Edmonton, Alberta, Canada. SPECIAL FUNDING AGREEMENTS NON-GOVERNMENTAL ORGANIZATIONS (NGOs) • Ducks Unlimited The SFM Network’s mission is to: • Sustainable Forest Management Network/BIOCAP • Deliver an internationally-recognized, interdisciplinary program that undertakes relevant university-based Canada Foundation Joint Venture Agreement INSTITUTION PARTNERS research; FUNDING PARTNERS • University of Alberta • Develop networks of researchers, industry, government, Aboriginal, and non-government organization
    [Show full text]
  • The Hidden Risk of Using Umbrella Species As Conservation Surrogates: a Spatio-Temporal Approach
    Biological Conservation 253 (2021) 108913 Contents lists available at ScienceDirect Biological Conservation journal homepage: www.elsevier.com/locate/biocon The hidden risk of using umbrella species as conservation surrogates: A spatio-temporal approach Fang Wang a,*, Julie Winkler b, Andr´es Vina˜ c, William Joseph McShea d, Sheng Li e, Thomas Connor c, Zhiqiang Zhao c, Dajun Wang e, Hongbo Yang c, Ying Tang c, Jindong Zhang f, Jianguo Liu c a Ministry of Education Key Laboratory for Biodiversity Science and Ecological Engineering, Coastal Ecosystems Research Station of the Yangtze River Estuary, Institute of Biodiversity Science, School of Life Sciences, Fudan University, Shanghai 200438, China b Department of Geography, Environment, and Spatial Sciences, Michigan State University, East Lansing, MI 48823, USA c Center for Systems Integration and Sustainability, Department of Fisheries and Wildlife, Michigan State University, East Lansing, MI 48823, USA d National Zoological Park, Smithsonian Conservation Biology Institute, Front Royal, VA 22630, USA e College of Life Sciences, Peking University, 5 Yiheyuan Rd., Beijing 100871, China f Key Laboratory of Southwest China Wildlife Resources Conservation (Ministry of Education), College of Life Sciences, China West Normal University, Nanchong 637009, China ARTICLE INFO ABSTRACT Keywords: The use of a charismatic umbrella species as surrogate for sympatric species is often advocated as an effcient Umbrella species approach. However, comprehensive evaluations from a spatio-temporal perspective are few, leaving the long- Conservation planning term effectiveness of such practices remain uncertain. We modeled the habitat change for giant panda and Giant panda eight sympatric mammalian species using observations from extensive camera trap surveys and remotely-sensed Multi-species conservation environmental predictors during two time periods, early 2000s and early 2010s.
    [Show full text]
  • A Mechanistic Approach to Evaluation of Umbrella Species As Conservation Surrogates
    A Mechanistic Approach to Evaluation of Umbrella Species as Conservation Surrogates KENICHI OZAKI,∗ MASAHIRO ISONO, TAKAYUKI KAWAHARA, SHIGEO IIDA, TAKUMA KUDO, AND KENJI FUKUYAMA Hokkaido Research Center, Forestry and Forest Products Research Institute, Hitsujigaoka, Sapporo 062–8516, Japan Abstract: Although species with large area requirements are sometimes used as umbrella species, their general utility as conservation tools is uncertain. We surveyed the species diversity of birds, butterflies, carabids, and forest-floor plants in forest sites across an area (1600 km2) in which we delineated large breeding home ranges of Northern Goshawk (Accipiter gentilis). We tested whether protection of the home ranges could serve as an effective umbrella to protect sympatric species of the four taxa. We also used an empirical habitat model of occupancy of home range to examine mechanisms by which the Northern Goshawk acts as an umbrella species. Among species richness, abundance, and species composition of the four taxa, only abundance and species composition of birds differed between sites located inside and outside home ranges, which was due to greater abundance of bird species that were prey of Northern Goshawks inside the home ranges. Thus, although home range indicated areas with high abundance of certain bird prey species, it was not effective as an indicator of the species diversity of all four taxa. We also did not find any difference in species richness, abundance, and species composition between sites predicted as occupied and unoccupied using the habitat model. In contrast, when we selected sites on the basis of each habitat variable in the model, habitat variables that selected sites either in agricultural or forested landscapes encompassed sites with high species richness or particular species composition.
    [Show full text]