Assessing Ecological Function in the Context of Species Recovery H
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Megafauna Extinction, Tree Species Range Reduction, and Carbon Storage in Amazonian Forests
Ecography 39: 194–203, 2016 doi: 10.1111/ecog.01587 © 2015 The Authors. Ecography © 2015 Nordic Society Oikos Subject Editor: Yadvinder Mahli. Editor-in-Chief: Nathan J. Sanders. Accepted 27 September 2015 Megafauna extinction, tree species range reduction, and carbon storage in Amazonian forests Christopher E. Doughty, Adam Wolf, Naia Morueta-Holme, Peter M. Jørgensen, Brody Sandel, Cyrille Violle, Brad Boyle, Nathan J. B. Kraft, Robert K. Peet, Brian J. Enquist, Jens-Christian Svenning, Stephen Blake and Mauro Galetti C. E. Doughty ([email protected]), Environmental Change Inst., School of Geography and the Environment, Univ. of Oxford, South Parks Road, Oxford, OX1 3QY, UK. – A. Wolf, Dept of Ecology and Evolutionary Biology, Princeton Univ., Princeton, NJ 08544, USA. – N. Morueta-Holme, Dept of Integrative Biology, Univ. of California – Berkeley, CA 94720, USA. – B. Sandel, J.-C. Svenning and NM-H, Section for Ecoinformatics and Biodiversity, Dept of Bioscience, Aarhus Univ., Ny Munkegade 114, DK-8000 Aarhus C, Denmark. – P. M. Jørgensen, Missouri Botanical Garden, PO Box 299, St Louis, MO 63166-0299, USA. – C. Violle, CEFE UMR 5175, CNRS – Univ. de Montpellier – Univ. Paul-Valéry Montpellier – EPHE – 1919 route de Mende, FR-34293 Montpellier Cedex 5, France. – B. Boyle and B. J. Enquist, Dept of Ecology and Evolutionary Biology, Univ. of Arizona, Tucson, AZ 85721, USA. – N. J. B. Kraft, Dept of Biology, Univ. of Maryland, College Park, MD 20742, USA. BJE also at: The Santa Fe inst., 1399 Hyde Park Road, Santa Fe, NM 87501, USA. – R. K. Peet, Dept of Biology, Univ. of North Carolina, Chapel Hill, NC 27599-3280, USA. -
Final Report of the Statewide Ecological Extinction Task Force
FINAL REPORT OF THE STATEWIDE ECOLOGICAL EXTINCTION TASK FORCE ESTABLISHED UNDER THE PROVISIONS OF SENATE CONCURRENT RESOLUTION NO. 20 OF THE 149TH GENERAL ASSEMBLY RESPECTFULLY SUBMITTED TO THE GOVERNOR, PRESIDENT PRO TEMPORE OF THE SENATE, AND SPEAKER OF THE HOUSE DECEMBER 1ST, 2017 TABLE OF CONTENTS MEMBERS OF THE TASK FORCE ............................................................................... 1 PREFACE.................................................................................................................. 2 INTRODUCTION ........................................................................................................ 3 EXECUTIVE SUMMARY BACKGROUND OF THE TASK FORCE .............................................................. 6 OVERVIEW OF MEETINGS .............................................................................. 7 TASK FORCE FINDINGS ............................................................................................ 10 TASK FORCE RECOMMENDATIONS .......................................................................... 11 APPENDICES A. SENATE CONCURRENT RESOLUTION 20 ................................................... 16 B. COMPOSITION OF TASK FORCE AND MEMBER BIOGRAPHIES ................... 19 C. MINUTES FROM TASK FORCE MEETINGS ................................................. 32 D. INTERN REPORT ....................................................................................... 105 E. LINKS TO SUPPLEMENTAL MATERIALS CONTRIBUTED BY TASK FORCE MEMBERS ............................................. -
Ecosystem Consequences of Bird Declines
Ecosystem consequences of bird declines C¸ag˘ an H. S¸ekerciog˘ lu*, Gretchen C. Daily, and Paul R. Ehrlich Center for Conservation Biology, Department of Biological Sciences, Stanford University, 371 Serra Mall, Stanford, CA 94305-5020 Contributed by Paul R. Ehrlich, October 28, 2004 We present a general framework for characterizing the ecological historically extinct (129) bird species of the world from 248 and societal consequences of biodiversity loss and applying it to sources into a database with Ͼ600,000 entries. Our scenarios the global avifauna. To investigate the potential ecological conse- (Fig. 3, which is published as supporting information on the quences of avian declines, we developed comprehensive databases PNAS web site) are based on the extinction probabilities for of the status and functional roles of birds and a stochastic model threatened species used by International Union for Conserva- for forecasting change. Overall, 21% of bird species are currently tion of Nature and Natural Resources (IUCN). These probabil- extinction-prone and 6.5% are functionally extinct, contributing ities are as follows: 50% chance of extinction in the next 10 years negligibly to ecosystem processes. We show that a quarter or more for critically endangered species, 20% chance of extinction in the of frugivorous and omnivorous species and one-third or more of next 20 years for endangered species, and 10% chance of herbivorous, piscivorous, and scavenger species are extinction- extinction in the next 100 years for vulnerable species. We report prone. Furthermore, our projections indicate that by 2100, 6–14% the averages of 10,000 simulations run for each decade from 2010 of all bird species will be extinct, and 7–25% (28–56% on oceanic to 2100. -
Wkdivextinct Report 2018
ICES WKDIVEXTINCT REPORT 2018 ICES ADVISORY COMMITTEE ICES CM 2018/ACOM:48 REF. ACOM Report of the Workshop on extinction risk of MSFD biodiversity approach (WKDIVExtinct) 12–15 June 2018 ICES HQ, Copenhagen, Denmark International Council for the Exploration of the Sea Conseil International pour l’Exploration de la Mer H. C. Andersens Boulevard 44–46 DK-1553 Copenhagen V Denmark Telephone (+45) 33 38 67 00 Telefax (+45) 33 93 42 15 www.ices.dk [email protected] Recommended format for purposes of citation: ICES. 2018. Report of the Workshop on extinction risk of MSFD biodiversity ap- proach (WKDIVExtinct), 12–15 June 2018, ICES HQ, Copenhagen, Denmark. ICES CM 2018/ACOM:48. 43 pp. The material in this report may be reused using the recommended citation. ICES may only grant usage rights of information, data, images, graphs, etc. of which it has own- ership. For other third-party material cited in this report, you must contact the original copyright holder for permission. For citation of datasets or use of data to be included in other databases, please refer to the latest ICES data policy on the ICES website. All extracts must be acknowledged. For other reproduction requests please contact the General Secretary. The document is a report of an Expert Group under the auspices of the International Council for the Exploration of the Sea and does not necessarily represent the views of the Council. © 2018 International Council for the Exploration of the Sea ICES WKDIVExtinct REPORT 2018 | i Contents Executive summary 1 1 Introduction .................................................................................................................... 2 1.1 Background ........................................................................................................... 2 1.2 Findings from the workshop WKDIVAgg ....................................................... -
Ecosystem Impact of the Decline of Large Whales in the North Pacific
SIXTEEN Ecosystem Impact of the Decline of Large Whales in the North Pacific DONALD A. CROLL, RAPHAEL KUDELA, AND BERNIE R. TERSHY Biodiversity loss can significantly alter ecosystem processes over a 150-year period (Springer et al. 2003). Although large (Chapin et al. 2000), and ecological extinction can have whales are significant consumers of pelagic prey, such as similar effects (Jackson et al. 2001). For marine vertebrates, schooling fish and euphausiids (krill), the trophic impacts of overharvesting is the main driver of ecological extinction, their removal is not clear (Trites et al. 1999). Indeed, it is and the expansion of fishing fleets into the open ocean has possible that the biomass of prey consumed by large whales precipitated rapid declines in pelagic apex predators such as prior to exploitation exceeded that currently taken by com- whales (Baker and Clapham 2002), sharks (Baum et al. 2003), mercial fisheries (Baker and Clapham 2002), but estimates of tuna, and billfishes (Cox et al. 2002; Christensen et al. 2003), prey consumption by large whales before and after the period leading to a trend in global fisheries toward exploitation of of intense human exploitation are lacking. Given the large lower trophic levels (Pauly et al. 1998a). Globally, many fish biomass of pre-exploitation whale populations (see, e.g., stocks are overexploited (Steneck 1998), and the resulting Whitehead 1995; Roman and Palumbi 2003), their high ecological extinctions have been implicated in the collapse mammalian metabolic rate, and their relatively high trophic of numerous nearshore coastal ecosystems (Jackson et al. position (Trites 2001), it is likely that the removal of large 2001). -
The Extinction and De-Extinction of Species
Linfield University DigitalCommons@Linfield Faculty Publications Faculty Scholarship & Creative Works 2017 The Extinction and De-Extinction of Species Helena Siipi University of Turku Leonard Finkelman Linfield College Follow this and additional works at: https://digitalcommons.linfield.edu/philfac_pubs Part of the Biology Commons, and the Philosophy of Science Commons DigitalCommons@Linfield Citation Siipi, Helena and Finkelman, Leonard, "The Extinction and De-Extinction of Species" (2017). Faculty Publications. Accepted Version. Submission 3. https://digitalcommons.linfield.edu/philfac_pubs/3 This Accepted Version is protected by copyright and/or related rights. It is brought to you for free via open access, courtesy of DigitalCommons@Linfield, with permission from the rights-holder(s). Your use of this Accepted Version must comply with the Terms of Use for material posted in DigitalCommons@Linfield, or with other stated terms (such as a Creative Commons license) indicated in the record and/or on the work itself. For more information, or if you have questions about permitted uses, please contact [email protected]. The extinction and de-extinction of species I. Introduction WhendeathcameforCelia,ittooktheformoftree.Heedlessofthedangerposed bybranchesoverladenwithsnow,CeliawanderedthroughthelandscapeofSpain’s OrdesanationalparkinJanuary2000.branchfellonherskullandcrushedit.So deathcameandtookher,leavingbodytobefoundbyparkrangersandlegacyto bemournedbyconservationistsaroundtheworld. Theconservationistsmournednotonlythedeathoftheorganism,butalsoan -
The Oyster : Contributions to Habitat, Biodiversity, & Ecological Resiliency
The Oyster : Contributions to Habitat, Biodiversity, & Ecological Resiliency Factors Affecting Oyster Distribution & Abundance Physical = salinity, temperature Salinity & Temperature •S - dynamic change ~daily basis; T - changes seasonally •Affects community organization - high S & T= predators, disease By Steve Morey, FAMU ‘Oysters suffered significant disease- related mortality under high-salinity, drought conditions, particularly in the summer.’ Dermo Perkinsus marinus Petes et al. 2012. Impacts of upstream drought and water withdrawals on the health & survival of downstream estuarine oyster populations. Ecology & Evolution 2(7):1712-1724 Factors Affecting Oyster Distribution & Abundance Physical = River flow Seasonal River Flow •Major influence on physical & biological relationships •Delivers low salinity H2O, turbidity, high nutrient & detritus concentrations •River flow, when high, can extend far offshore influencing shelf-edge productivity Factors Affecting Oyster Distribution & Abundance Competition for space & food at different life stages • Can be intraspecific -oysters competing with oysters- or interspecific - other species competing with oysters) Oysters • Can affect settlement patterns, and so alter community structure • Can reduce oyster density, growth, or physical condition Oysters eat phytoplankton & other organisms within a small size range, competing with other Barnacles filter feeders Mussels & Tunicates Factors Affecting Oyster Distribution & Abundance Species interactions – predation & disease •Habitat complexity -
Maintaining Humanity's Life Support Systems in the 21St Century
Scientific Consensus on Maintaining Humanity’s Life Support Systems in the 21st Century Information for Policy Makers 02 Contents Essential PointS for PoliCy MakErS ii One-Page Executive Summary ovErviEw of thE fivE Key Problems iii One-Page Overview of Problems and Broad-Brush Solutions Preface: Purpose of this Consensus Statement 1 background information: Dangerous Trends in our Life Support Systems 2 rising to the Challenge 3 Climate Disruption 4 Extinctions 7 Ecosystem Transformation 11 Pollution 14 Population Growth and Resource Consumption 16 Interactions 19 Cited Supporting Studies 21 Some other relevant reports 26 liSt of Supporting-SCiEntiSt Signatures 27 i ESSEntial PointS FOR PoliCy MakErS Scientific Consensus on Maintaining Humanity’s Life Support Systems in the 21st Century Earth is rapidly approaching a tipping point. Human impacts are causing alarming levels of harm to our planet. As scientists who study the interaction of people with the rest of the biosphere using a wide range of approaches, we agree that the evidence that humans are damaging their ecological life-support systems is overwhelming. We further agree that, based on the best scientific information available, human quality of life will suffer substantial degradation by the year 2050 if we continue on our current path. Science unequivocally demonstrates the human impacts of key concern: • Climate disruption — more, faster climate change than since humans first became a species • Extinctions — not since the dinosaurs went extinct have so many species and populations died out so fast, both on land and in the oceans. • Wholesale loss of diverse ecosystems — we have plowed, paved, or otherwise transformed more than 40% of Earth’s ice-free land, and no place on land or in the sea is free of our direct or indirect influences. -
Memoria 2013
Estación Biológica de Doñana - Memoria 2013 1 Estación Biológica de Doñana - Memoria 2013 Portada: Experimentación con picudo rojo (Rhinchophorus ferrugineus), especie invasora, actualmente en expasión en España, que ha supuesto una plaga, principalmente para la palmera canaria. 2 Estación Biológica de Doñana - Memoria 2013 ESTACIÓN BIOLÓGICA DE DOÑANA CONSEJO SUPERIOR DE INVESTIGACIONES CIENTÍFICAS MEMORIA 2013 COORDINACIÓN Guyonne Janss Rocío Astasio Rosa Rodríguez RECOPILACIÓN INFORMACIÓN Begoña Arrizabalaga José Carlos Soler Olga Guerrero Carmen Mª Velasco Tomás Perera Antonio Páez María Antonia Orduña Ana Ruíz Sonia Velasco Angelines Soto María Cabot Sofía Conradi FOTOGRAFÍAS Héctor Garrido DISEÑO Y MAQUETACIÓN Héctor Garrido Sevilla, Noviembre de 2014 Estación Biológica de Doñana/CSIC C/ Américo Vespucio, s/n 41092 SEVILLA www.ebd.csic.es 3 Estación Biológica de Doñana - Memoria 2013 4 Estación Biológica de Doñana - Memoria 2013 5 Estación Biológica de Doñana - Memoria 2013 6 Estación Biológica de Doñana - Memoria 2013 Contenidos Presentación 9 Introducción 10 Misión 10 Sedes 10 Organización y Estructura 12 Departamentos y grupos de investigación 12 Organigrama de la Estación Biológica de Doñana 13 Líneas de Investigación 14 Servicios científicos 18 Actividades 2013 31 Actividad Investigadora de la EBD 32 Recursos económicos y humanos 38 Otras actividades a destacar 42 Proyectos de Investigación 45 Publicaciones 103 Congresos 120 Tesis doctorales y maestrias 121 Cursos 124 Premios y distinciones 125 Recursos humanos 127 7 Estación Biológica de Doñana - Memoria 2013 8 Estación Biológica de Doñana - Memoria 2013 Presentación 9 Estación Biológica de Doñana - Memoria 2013 Sedes La Estación Biológica de Doñana consta de un centro de investigación con sede en Sevilla, dos estaciones de campo (El Palacio y Huer- ta Tejada) junto a las Reservas Biológicas de Doñana en Almonte (Huelva) y del Guadiamar en Aznalcazar (Sevilla) y de una Estación de Campo en Roblehondo, en el Parque Natural de las Sierras de Cazorla, Segura y Las Villas (Jaén). -
Sea Turtles : the Importance of Sea Turtles to Marine Ecosystems
PHOTO TIM CALVER WHY HEALTHY OCEANS NEED SEA TURTLES : THE IMPORTANCE OF SEA TURTLES TO MARINE ECOSYSTEMS Wilson, E.G., Miller, K.L., Allison, D. and Magliocca, M. oceana.org/seaturtles S E L T R U T Acknowledgements The authors would like to thank Karen Bjorndal for her review of this report. We would also like to thank The Streisand Foundation for their support of Oceana’s work to save sea turtles. PHOTO MICHAEL STUBBLEFIELD OCEANA | Protecting the World’s Oceans TABLE OF CONTENTS WHY HEALTHY OCEANS NEED SEA TURTLES 3 Executive Summary 4 U.S. Sea Turtles 5 Importance of Sea Turtles to Healthy Oceans 6 Maintaining Habitat Importance of Green Sea Turtles on Seagrass Beds Impact of Hawksbill Sea Turtles on Coral Reefs Benefit of Sea Turtles to Beach Dunes 9 Maintaining a Balanced Food Web Sea Turtles and Jellyfish Sea Turtles Provide Food for Fish 11 Nutrient Cycling Loggerheads Benefit Ocean Floor Ecosystems Sea Turtles Improve Nesting Beaches 12 Providing Habitat 14 The Risk of Ecological Extinction 15 Conclusions oceana.org/seaturtles 1 S E L T R U T PHOTO TIM CALVER 2 OCEANA | Protecting the World’s Oceans EXECUTIVE SUMMARY Sea turtles have played vital roles in maintaining the health of the world’s oceans for more than 100 million years. These roles range from maintaining productive coral reef ecosystems to transporting essential nutrients from the oceans to beaches and coastal dunes. Major changes have occurred in the oceans because sea turtles have been virtually eliminated from many areas of the globe. Commercial fishing, loss of nesting habitat and climate change are among the human-caused threats pushing sea turtles towards extinction. -
Future of the Sea: Marine Biodiversity
Future of the Sea: Marine Biodiversity Foresight – Future of the Sea Evidence Review Foresight, Government Office for Science Marine biodiversity The future of marine biodiversity and marine ecosystem functioning in UK coastal and territorial waters (including UK Overseas Territories) Frithjof C. Küpper & Nicholas A. Kamenos November 2017 This review has been commissioned as part of the UK government’s Foresight Future of the Sea project. The views expressed do not represent policy of any government or organisation. Marine biodiversity Contents Contents ..................................................................................................................................................3 Executive summary ................................................................................................................................5 1. Current trends and effects on UK interests ......................................................................................7 1.1 Biodiversity loss and implications for ecosystem functioning ...........................................................7 1.2 Ocean warming due to climate change ...........................................................................................7 1.3 Overexploitation ..............................................................................................................................8 1.4 Plastic pollution ...............................................................................................................................9 1.5 Invasive -
Understanding the Ecology of Extinction: Are We Close to the Critical Threshold?
Ann. Zool. Fennici 40: 71–80 ISSN 0003-455X Helsinki 30 April 2003 © Finnish Zoological and Botanical Publishing Board 2003 Understanding the ecology of extinction: are we close to the critical threshold? Tim G. Benton Institute of Biological Sciences, University of Stirling, FK9 4LA, UK (e-mail: [email protected]) Received 25 Nov. 2002, revised version received 20 Jan. 2003, accepted 21 Jan. 2003 Benton, T. G. 2003: Understanding the ecology of extinction: are we close to the critical threshold? — Ann. Zool. Fennici 40: 71–80. How much do we understand about the ecology of extinction? A review of recent lit- erature, and a recent conference in Helsinki gives a snapshot of the “state of the art”*. This “snapshot” is important as it highlights what we currently know, the tools avail- able for studying the process of extinction, its ecological correlates, and the theory concerning extinction thresholds. It also highlights that insight into the ecology of extinction can come from areas as diverse as the study of culture, the fossil record and epidemiology. Furthermore, it indicates where the gaps in knowledge and understand- ing exist. Of particular note is the need either to generate experimental data, or to make use of existing empirical data — perhaps through meta-analyses, to test general theory and guide its future development. Introduction IUCNʼs 2002 Red List, a total of 11 167 species are currently known to be threatened (http:// Few would argue that managing natural popu- www.redlist.org/info/tables/table1.html), though lations and their habitats is one of the greatest this is a gross underestimate of the true value, as, challenges for humans in the 21st century.