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Smith MD, Wilkins KD, Holdrege MC, Wilfahrt P, Collins SL, Knapp AK, Sala OE, Dukes JS, Phillips RP, Yahdjian L, Gherardi LA, Ohlert T, Beier C, Fraser LH, Jentsch A, Loik ME, Maestre FT, Power SA, Yu Q, Felton AJ, Munson SM, Luo Y, Abdoli H, Abedi M, Alados CL, Alberti J, Alon M, An H, Anacker B, Anderson M, Auge H, Bachle S, Bahalkeh K, Bahn M, Batbaatar A, Bauerle T, Beard KH, Behn K, Beil I, Biancari L, Blindow I, Bondaruk VF, Borer ET, Bork EW, Bruschetti CM, Byrne KM, Cahill Jr. JF, Calvo DA, Carbognani M, Cardoni A, Carlyle CN, Castillo-Garcia M, Chang SX, Chieppa J, Cianciaruso MV, Cohen O, Cordeiro AL, Cusack DF, Dahlke S, Daleo P, D'Antonio CM, Dietterich LH, S. Doherty T, Dubbert M, Ebeling A, Eisenhauer N, Fischer FM, Forte TGW, Gebauer T, Gozalo B, Greenville AC, Guidoni-Martins KG, Hannusch HJ, Vatsø Haugum S, Hautier Y, Hefting M, Henry HAL, Hoss D, Ingrisch J, Iribarne O, Isbell F, Johnson Y, Jordan S, Kelly EF, Kimmel K, Kreyling J, Kröel-Dulay G, Kröpfl A, Kübert A, Kulmatiski A, Lamb EG, Larsen KS, Larson J, Lawson J, Leder CV, Linstädter A, Liu J, Liu S, Lodge AG, Longo G, Loydi A, Luan J, Curtis Lubbe F, Macfarlane C, Mackie-Haas K, Malyshev AV, Maturano-Ruiz A, Merchant T, Metcalfe DB, Mori AS, Mudongo E, Newman GS, Nielsen UN, Nimmo D, Niu Y, Nobre P, O'Connor RC, Ogaya R, Oñatibia GR, Orbán I, Osborne B, Otfinowski R, Pärtel M, Penuelas J, Peri PL, Peter G, Petraglia A, Picon-Cochard C, Pillar VD, Piñeiro-Guerra JM, Ploughe LW, Plowes RM, Portales-Reyes C, Prober SM, Pueyo Y, Reed SC, Ritchie EG, Rodríguez DA, Rogers WE, Roscher C, Sánchez AM, Santos BA, Cecilia Scarfó M, Seabloom EW, Shi B, Souza L, Stampfli A, Standish RJ, Sternberg M, Sun W, Sünnemann M, Tedder M, Thorvaldsen P, Tian D, Tielbörger K, Valdecantos A, van den Brink L, Vandvik V, Vankoughnett MR, Guri Velle L, Wang C, Wang Y, Wardle GM, Werner C, Wei C, Wiehl G, Williams JL, Wolf AA, Zeiter M, Zhang F, Zhu J, Zong N, Zuo X. Extreme drought impacts have been underestimated in grasslands and shrublands globally. Proc Natl Acad Sci U S A 2024; 121:e2309881120. [PMID: 38190514 PMCID: PMC10823251 DOI: 10.1073/pnas.2309881120] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Grants] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 06/12/2023] [Accepted: 10/06/2023] [Indexed: 01/10/2024] Open
Abstract
Climate change is increasing the frequency and severity of short-term (~1 y) drought events-the most common duration of drought-globally. Yet the impact of this intensification of drought on ecosystem functioning remains poorly resolved. This is due in part to the widely disparate approaches ecologists have employed to study drought, variation in the severity and duration of drought studied, and differences among ecosystems in vegetation, edaphic and climatic attributes that can mediate drought impacts. To overcome these problems and better identify the factors that modulate drought responses, we used a coordinated distributed experiment to quantify the impact of short-term drought on grassland and shrubland ecosystems. With a standardized approach, we imposed ~a single year of drought at 100 sites on six continents. Here we show that loss of a foundational ecosystem function-aboveground net primary production (ANPP)-was 60% greater at sites that experienced statistically extreme drought (1-in-100-y event) vs. those sites where drought was nominal (historically more common) in magnitude (35% vs. 21%, respectively). This reduction in a key carbon cycle process with a single year of extreme drought greatly exceeds previously reported losses for grasslands and shrublands. Our global experiment also revealed high variability in drought response but that relative reductions in ANPP were greater in drier ecosystems and those with fewer plant species. Overall, our results demonstrate with unprecedented rigor that the global impacts of projected increases in drought severity have been significantly underestimated and that drier and less diverse sites are likely to be most vulnerable to extreme drought.
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Affiliation(s)
- Melinda D. Smith
- Department of Biology, Colorado State University, Fort Collins, CO80523
- Graduate Degree Program in Ecology, Colorado State University, Fort Collins, CO80523
| | | | - Martin C. Holdrege
- Department of Wildland Resource and the Ecology Center, Utah State University, Logan, UT84322
| | - Peter Wilfahrt
- Department of Ecology, Evolution, and Behavior, University of Minnesota, Saint Paul, MN55108
| | - Scott L. Collins
- Department of Biology, University of New Mexico, Albuquerque, NM87131
| | - Alan K. Knapp
- Department of Biology, Colorado State University, Fort Collins, CO80523
- Graduate Degree Program in Ecology, Colorado State University, Fort Collins, CO80523
| | - Osvaldo E. Sala
- School of Life Sciences, Global Drylands Center, Arizona State University, Tempe, AZ85281
| | - Jeffrey S. Dukes
- Department of Global Ecology, Carnegie Institution for Science, Stanford, CA94305
| | | | - Laura Yahdjian
- Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura (IFEVA), National Scientific and Technical Research Council (CONICET), Faculty of Agronomy, University of Buenos Aires, Buenos AiresC1417DSE, Argentina
| | - Laureano A. Gherardi
- Department of Environmental Science, Policy, and Management, University of California, Berkeley, CA94720
| | - Timothy Ohlert
- Department of Biology, Colorado State University, Fort Collins, CO80523
| | - Claus Beier
- Department of Geosciences and Natural Resource Management, University of Copenhagen, Frederiksberg C1958, Denmark
| | - Lauchlan H. Fraser
- Department of Natural Resource Science, Thompson Rivers University, Kamloops, BCV2C 0C8, Canada
| | - Anke Jentsch
- Department of Disturbance Ecology and Vegetation Dynamics, Bayreuth Center of Ecology and Environmental Research, University of Bayreuth, Bayreuth95447, Germany
| | - Michael E. Loik
- Department of Environmental Studies, University of California, Santa Cruz, CA95064
| | - Fernando T. Maestre
- Departamento de Ecologia, Universidad de Alicante, 03690 Alicante, Spain
- Instituto Multidisciplinar para el Estudio del Medio “Ramón Margalef”, Universidad de Alicante, 03690 Alicante, Spain
| | - Sally A. Power
- Hawkesbury Institute for the Environment, Western Sydney University, Penrith, NSW2751, Australia
| | - Qiang Yu
- School of Grassland Science, Beijing Forestry University, Beijing100083, China
| | - Andrew J. Felton
- Department of Land Resources and Environmental Sciences, Montana State University, Bozeman, MT59717
| | - Seth M. Munson
- U.S. Geological Survey, Southwest Biological Science Center, Flagstaff, AZ86001
| | - Yiqi Luo
- Soil and Crop Sciences Section, School of Integrative Plant Science, Cornell University, Ithaca, NY14853
| | - Hamed Abdoli
- Department of Range Management, Faculty of Natural Resources and Marine Sciences, Tarbiat Modares University, Noor46417-76489, Iran
| | - Mehdi Abedi
- Department of Range Management, Faculty of Natural Resources and Marine Sciences, Tarbiat Modares University, Noor46417-76489, Iran
| | - Concepción L. Alados
- Departamento de Biodiversidad y Restauración, Instituto Pirenaico de Ecología, Consejo Superior de Investigaciones Científicas (CSIC), Zaragoza50059, Spain
| | - Juan Alberti
- Laboratorio de Ecología, Instituto de Investigaciones Marinas y Costeras (IIMyC), Universidad Nacional de Mar del Plata (UNMdP)-Consejo Nacional de Investigación Ciencia y Técnica (CONICET), CC 1260 Correo Central, Mar del PlataB7600WAG, Argentina
| | - Moshe Alon
- School of Plant Sciences and Food Security, Faculty of Life Sciences, Tel Aviv University, Tel Aviv69978, Israel
| | - Hui An
- School of Ecology and Environment, Ningxia University, Yinchuan750021, China
| | - Brian Anacker
- City of Boulder Open Space and Mountain Parks, Boulder, CO80301
| | - Maggie Anderson
- Department of Ecology, Evolution, and Behavior, University of Minnesota, Saint Paul, MN55108
| | - Harald Auge
- Department of Community Ecology, Helmholtz-Centre for Environmental Research–UFZ, Halle06120, Germany
- German Centre for Integrative Biodiversity Research (iDiv) Halle-Jena-Leipzig, Leipzig04103, Germany
| | - Seton Bachle
- Division of Biology, Kansas State University, Manhattan, KS66506
- LI-COR Biosciences, 4647 Superior Street, Lincoln, NE68505
| | - Khadijeh Bahalkeh
- Department of Range Management, Faculty of Natural Resources and Marine Sciences, Tarbiat Modares University, Noor46417-76489, Iran
| | - Michael Bahn
- Department of Ecology, University of Innsbruck, Innsbruck6020, Austria
| | - Amgaa Batbaatar
- Department of Biological Sciences, University of Alberta, Edmonton, ABT6G 2E9, Canada
- Department of Agricultural, Food and Nutritional Science, University of Alberta, Edmonton, ABT6G 2P5, Canada
| | - Taryn Bauerle
- Soil and Crop Sciences Section, School of Integrative Plant Science, Cornell University, Ithaca, NY14853
| | - Karen H. Beard
- Department of Wildland Resource and the Ecology Center, Utah State University, Logan, UT84322
| | - Kai Behn
- Institute of Crop Science and Resource Conservation, Department of Plant Nutrition, University of Bonn, Bonn53115, Germany
| | - Ilka Beil
- Institute of Botany and Landscape Ecology, Department of Experimental Plant Ecology, University of Greifswald, GreifswaldD-17498, Germany
| | - Lucio Biancari
- Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura (IFEVA), National Scientific and Technical Research Council (CONICET), Faculty of Agronomy, University of Buenos Aires, Buenos AiresC1417DSE, Argentina
| | - Irmgard Blindow
- Biological Station of Hiddensee, Department of Biology, University of Greifswald, KlosterD-18565, Germany
| | - Viviana Florencia Bondaruk
- Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura (IFEVA), National Scientific and Technical Research Council (CONICET), Faculty of Agronomy, University of Buenos Aires, Buenos AiresC1417DSE, Argentina
| | - Elizabeth T. Borer
- Department of Ecology, Evolution, and Behavior, University of Minnesota, Saint Paul, MN55108
| | - Edward W. Bork
- Department of Agricultural, Food and Nutritional Science, University of Alberta, Edmonton, ABT6G 2P5, Canada
| | - Carlos Martin Bruschetti
- Laboratorio de Ecología, Instituto de Investigaciones Marinas y Costeras (IIMyC), Universidad Nacional de Mar del Plata (UNMdP)-Consejo Nacional de Investigación Ciencia y Técnica (CONICET), CC 1260 Correo Central, Mar del PlataB7600WAG, Argentina
| | - Kerry M. Byrne
- Department of Environmental Science and Management, California State Polytechnic University, Humboldt, Arcata, CA95521
| | - James F. Cahill Jr.
- Department of Biological Sciences, University of Alberta, Edmonton, ABT6G 2E9, Canada
| | - Dianela A. Calvo
- Universidad Nacional de Río Negro, Centro de Estudios Ambientales desde la NorPatagonia (CEANPa), Sede Atlántica–CONICET, Viedma8500, Argentina
| | - Michele Carbognani
- Department of Chemistry, Life Sciences and Environmental Sustainability, University of Parma, ParmaI-43124, Italy
| | - Augusto Cardoni
- Laboratorio de Ecología, Instituto de Investigaciones Marinas y Costeras (IIMyC), Universidad Nacional de Mar del Plata (UNMdP)-Consejo Nacional de Investigación Ciencia y Técnica (CONICET), CC 1260 Correo Central, Mar del PlataB7600WAG, Argentina
| | - Cameron N. Carlyle
- Department of Agricultural, Food and Nutritional Science, University of Alberta, Edmonton, ABT6G 2P5, Canada
| | - Miguel Castillo-Garcia
- Departamento de Biodiversidad y Restauración, Instituto Pirenaico de Ecología, Consejo Superior de Investigaciones Científicas (CSIC), Zaragoza50059, Spain
| | - Scott X. Chang
- Department of Renewable Resources, University of Alberta, Edmonton, ABT6G 2E3, Canada
| | - Jeff Chieppa
- Hawkesbury Institute for the Environment, Western Sydney University, Penrith, NSW2751, Australia
| | | | - Ofer Cohen
- School of Plant Sciences and Food Security, Faculty of Life Sciences, Tel Aviv University, Tel Aviv69978, Israel
| | - Amanda L. Cordeiro
- Department of Ecosystem Science and Sustainability, Colorado State University, Fort Collins, CO80523
| | - Daniela F. Cusack
- Department of Ecosystem Science and Sustainability, Colorado State University, Fort Collins, CO80523
| | - Sven Dahlke
- Biological Station of Hiddensee, Department of Biology, University of Greifswald, KlosterD-18565, Germany
| | - Pedro Daleo
- Laboratorio de Ecología, Instituto de Investigaciones Marinas y Costeras (IIMyC), Universidad Nacional de Mar del Plata (UNMdP)-Consejo Nacional de Investigación Ciencia y Técnica (CONICET), CC 1260 Correo Central, Mar del PlataB7600WAG, Argentina
| | - Carla M. D'Antonio
- Department of Ecology, Evolution, and Marine Biology, University of California, Santa Barbara, CA93106
| | - Lee H. Dietterich
- Department of Ecosystem Science and Sustainability, Colorado State University, Fort Collins, CO80523
- US Army Engineer Research and Development Center, Environmental Laboratory, Vicksburg, MS39180
| | - Tim S. Doherty
- School of Life and Environmental Sciences, The University of Sydney, Camperdown, NSW2006, Australia
| | - Maren Dubbert
- Isotope Biogeochemistry and GasFluxes, Leibniz-Zentrum fürAgrarlandschaftsforschung (ZALF), Müncheberg15374, Germany
| | - Anne Ebeling
- Institute of Ecology and Evolution, Friedrich Schiller University Jena, Jena07743, Germany
| | - Nico Eisenhauer
- German Centre for Integrative Biodiversity Research (iDiv) Halle-Jena-Leipzig, Leipzig04103, Germany
- Institute of Biology, Leipzig University, Leipzig04103, Germany
| | - Felícia M. Fischer
- Institute of Biology, Leipzig University, Leipzig04103, Germany
- Centro de Investigaciones sobre Desertificación, Consejo Superior de Investigaciones Científicas (CSIC)-Universitat Valencia (UV) - Generalitat Valenciana (GV),Valencia46113, Spain
| | - T'ai G. W. Forte
- Department of Chemistry, Life Sciences and Environmental Sustainability, University of Parma, ParmaI-43124, Italy
| | - Tobias Gebauer
- Geobotany, Faculty of Biology, University of Freiburg, FreiburgD-79104, Germany
| | - Beatriz Gozalo
- Instituto Multidisciplinar para el Estudio del Medio “Ramón Margalef”, Universidad de Alicante, 03690 Alicante, Spain
| | - Aaron C. Greenville
- School of Life and Environmental Sciences, The University of Sydney, Camperdown, NSW2006, Australia
| | | | - Heather J. Hannusch
- Department of Ecology and Conservation Biology, Texas A&M University, College Station, TX77843
| | - Siri Vatsø Haugum
- Department of Biological Sciences, University of Bergen, Bergen5007, Norway
| | - Yann Hautier
- Ecology and Biodiversity Group, Department of Biology, Utrecht University, Utrecht, 3584 CH, Netherlands
| | - Mariet Hefting
- Ecology and Biodiversity Group, Department of Biology, Utrecht University, Utrecht, 3584 CH, Netherlands
| | - Hugh A. L. Henry
- Department of Biology, University of Western Ontario, London, ONN6A 5B7, Canada
| | - Daniela Hoss
- German Centre for Integrative Biodiversity Research (iDiv) Halle-Jena-Leipzig, Leipzig04103, Germany
- Institute of Biology, Leipzig University, Leipzig04103, Germany
- Department of Ecology, Universidade Federal do Rio Grande do Sul, Porto Alegre91501-970, Brazil
| | - Johannes Ingrisch
- Department of Ecology, University of Innsbruck, Innsbruck6020, Austria
| | - Oscar Iribarne
- Laboratorio de Ecología, Instituto de Investigaciones Marinas y Costeras (IIMyC), Universidad Nacional de Mar del Plata (UNMdP)-Consejo Nacional de Investigación Ciencia y Técnica (CONICET), CC 1260 Correo Central, Mar del PlataB7600WAG, Argentina
| | - Forest Isbell
- Department of Ecology, Evolution, and Behavior, University of Minnesota, Saint Paul, MN55108
| | - Yari Johnson
- U.S. Army Corps of Engineers, Sacramento, CA95814
| | - Samuel Jordan
- School of Life Sciences, Global Drylands Center, Arizona State University, Tempe, AZ85281
| | - Eugene F. Kelly
- Department of Soil and Crop Sciences, Colorado State University, Fort Collins, CO80523
| | - Kaitlin Kimmel
- Global Water Security Center, The University of Alabama, Tuscaloosa, AL35487
| | - Juergen Kreyling
- Institute of Botany and Landscape Ecology, Department of Experimental Plant Ecology, University of Greifswald, GreifswaldD-17498, Germany
| | - György Kröel-Dulay
- Centre for Ecological Research, Institute of Ecology and Botany, Vácrátót2163, Hungary
| | - Alicia Kröpfl
- Departamento de Gestión Agropecuaria, Universidad Nacional del Comahue, Centro Universitario Regional Zona Atlántica, Viedma85009, Argentina
| | - Angelika Kübert
- Ecosystem Physiology, Faculty of Environment and Natural Resources, Albert-Ludwig-University of Freiburg, Freiburg79110, Germany
| | - Andrew Kulmatiski
- Department of Wildland Resource and the Ecology Center, Utah State University, Logan, UT84322
| | - Eric G. Lamb
- Department of Plant Sciences, University of Saskatchewan, Saskatoon, SKS7N5A8, Canada
| | - Klaus Steenberg Larsen
- Department of Geosciences and Natural Resource Management, University of Copenhagen, Frederiksberg C1958, Denmark
| | - Julie Larson
- Range and Meadow Forage Management Research, Eastern Oregon Agricultural Research Center, US Department of Agriculture (USDA)-Agricultural Research Service, Burns, OR97720
| | - Jason Lawson
- Brackenridge Field Laboratory, University of Texas, Austin, TX78747
| | - Cintia V. Leder
- Universidad Nacional de Río Negro, Centro de Estudios Ambientales desde la NorPatagonia (CEANPa), Sede Atlántica–CONICET, Viedma8500, Argentina
| | - Anja Linstädter
- Department of Biodiversity Research and Systematic Botany, University of Potsdam, Potsdam14469, Germany
| | - Jielin Liu
- Prataculture Research Institute, Heilongjiang Academy of Agricultural Sciences, Haerbin150086, China
| | - Shirong Liu
- Key Laboratory of Forest Ecology and Environment of National Forestry and Grassland Administration, Ecology and Nature Conservation Institute, Chinese Academy of Forestry, Beijing100091, China
| | - Alexandra G. Lodge
- Department of Ecology and Conservation Biology, Texas A&M University, College Station, TX77843
| | - Grisel Longo
- Programa de Posgrado en Desarrollo y Medio Ambiente–Universidade Federal da Paraíba, Cidade Universitária, Castelo Branco, João Pessoa, PB58051-900, Brazil
| | - Alejandro Loydi
- Centro de Recursos Naturales Renovables de la Zona Semiárida–CONICET, Departamento de Biología, Bioquímica y Farmacia, Universidad Nacional del Sur,Bahía Blanca8000FTN, Argentina
| | - Junwei Luan
- Institute of Resources and Environment, International Centre for Bamboo and Rattan, Key Laboratory of National Forestry and Grassland Administration and Beijing for Bamboo and Rattan Science and Technology, Beijing100102, China
| | | | - Craig Macfarlane
- Commonwealth Scientific and Industrial Research Organization (CSIRO) Environment, Wembley, WA6913, Australia
| | - Kathleen Mackie-Haas
- School of Agricultural, Forest and Food Sciences, Bern University of Applied Sciences,Zollikofen3052, Switzerland
| | - Andrey V. Malyshev
- Institute of Botany and Landscape Ecology, Department of Experimental Plant Ecology, University of Greifswald, GreifswaldD-17498, Germany
| | - Adrián Maturano-Ruiz
- Instituto Multidisciplinar para el Estudio del Medio “Ramón Margalef”, Universidad de Alicante, 03690 Alicante, Spain
| | - Thomas Merchant
- Department of Ecology and Evolutionary Biology, Institute for Arctic and Alpine Research, University of Colorado,Boulder, CO80309
| | - Daniel B. Metcalfe
- Department of Ecology and Environmental Science, Umeå University, UmeåS-901 87, Sweden
| | - Akira S. Mori
- Research Center for Advanced Science and Technology, University of Tokyo,Meguro, Tokyo153-8904, Japan
- Graduate School of Environment and Information Sciences, Yokohama National University, Yokohama240-8501, Japan
| | - Edwin Mudongo
- Conservancy-Communities Living Among Wildlife Sustainably (CLAWS) Botswana, Seronga00000, Botswana
| | - Gregory S. Newman
- School of Biological Sciences, University of Oklahoma, Norman, OK73019
| | - Uffe N. Nielsen
- Hawkesbury Institute for the Environment, Western Sydney University, Penrith, NSW2751, Australia
| | - Dale Nimmo
- Gulbali Institute, Charles Sturt University, Albury, NSW2640, Australia
| | - Yujie Niu
- Department of Disturbance Ecology and Vegetation Dynamics, Bayreuth Center of Ecology and Environmental Research, University of Bayreuth, Bayreuth95447, Germany
| | - Paola Nobre
- Department of Ecology, Universidade Federal de Goiás, Goiânia, GO74690-900, Brazil
| | - Rory C. O'Connor
- Range and Meadow Forage Management Research, Eastern Oregon Agricultural Research Center, US Department of Agriculture (USDA)-Agricultural Research Service, Burns, OR97720
| | - Romà Ogaya
- Global Ecology Unit Center for Ecological Research and Forestry Applications (CREAF)-National Research Council (CSIC)-Universitat Autonoma de Barcelona (UAB), National Research Council (CSIC), Bellaterra, Catalonia08194, Spain
- Center for Ecological Research and Forestry Applications (CREAF), Cerdanyola del Vallès, Barcelona, Catalonia08193, Spain
| | - Gastón R. Oñatibia
- Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura (IFEVA), National Scientific and Technical Research Council (CONICET), Faculty of Agronomy, University of Buenos Aires, Buenos AiresC1417DSE, Argentina
| | - Ildikó Orbán
- Centre for Ecological Research, Institute of Ecology and Botany, Vácrátót2163, Hungary
- Department of Biodiversity Research and Systematic Botany, University of Potsdam, Potsdam14469, Germany
| | - Brooke Osborne
- Department of Environment and Society, Utah State University, Moab, UT84532
| | - Rafael Otfinowski
- Department of Biology, The University of Winnipeg, Winnipeg, MBR3B 2E9, Canada
| | - Meelis Pärtel
- Institute of Ecology and Earth Sciences, University of Tartu, TartuEE50409, Estonia
| | - Josep Penuelas
- Global Ecology Unit Center for Ecological Research and Forestry Applications (CREAF)-National Research Council (CSIC)-Universitat Autonoma de Barcelona (UAB), National Research Council (CSIC), Bellaterra, Catalonia08194, Spain
- Center for Ecological Research and Forestry Applications (CREAF), Cerdanyola del Vallès, Barcelona, Catalonia08193, Spain
| | - Pablo L. Peri
- Instituto Nacional de Tecnología Agropecuaria–Universidad Nacional d ela Patagonia Austral–CONICET, Río Gallegos, Caleta OliviaZ9011, Argentina
| | - Guadalupe Peter
- Universidad Nacional de Río Negro, Centro de Estudios Ambientales desde la NorPatagonia (CEANPa), Sede Atlántica–CONICET, Viedma8500, Argentina
| | - Alessandro Petraglia
- Department of Chemistry, Life Sciences and Environmental Sustainability, University of Parma, ParmaI-43124, Italy
| | - Catherine Picon-Cochard
- Université Clermont Auvergne, National Research Institute for Agriculture, Food and the Environment, VetAgro Sup, Research Unit for Grassland Ecosystems, Clermont-Ferrand63000, France
| | - Valério D. Pillar
- Department of Ecology, Universidade Federal do Rio Grande do Sul, Porto Alegre91501-970, Brazil
| | - Juan Manuel Piñeiro-Guerra
- Instituto de Investigaciones Fisiológicas y Ecológicas Vinculadas a la Agricultura (IFEVA), National Scientific and Technical Research Council (CONICET), Faculty of Agronomy, University of Buenos Aires, Buenos AiresC1417DSE, Argentina
- Laboratório de Ecologia Aplicada e Conservação, Departamento de Sistemática e Ecologia, Universidade Federal da Paraíba, Cidade Universitária, Castelo Branco, João Pessoa, PB58051-900, Brazil
| | - Laura W. Ploughe
- Department of Biological Sciences, Purdue University, West Lafayette, IN47907
| | - Robert M. Plowes
- Brackenridge Field Laboratory, University of Texas, Austin, TX78747
| | | | - Suzanne M. Prober
- Commonwealth Scientific and Industrial Research Organization (CSIRO) Environment, Wembley, WA6913, Australia
| | - Yolanda Pueyo
- Departamento de Biodiversidad y Restauración, Instituto Pirenaico de Ecología, Consejo Superior de Investigaciones Científicas (CSIC), Zaragoza50059, Spain
| | - Sasha C. Reed
- U.S. Geological Survey, Southwest Biological Science Center, Moab, UT84532
| | - Euan G. Ritchie
- Centre for Integrative Ecology, School of Life and Environmental Sciences, Deakin University, Burwood, VIC3125, Australia
| | - Dana Aylén Rodríguez
- Centro de Recursos Naturales Renovables de la Zona Semiárida–CONICET, Departamento de Biología, Bioquímica y Farmacia, Universidad Nacional del Sur,Bahía Blanca8000FTN, Argentina
| | - William E. Rogers
- Department of Ecology and Conservation Biology, Texas A&M University, College Station, TX77843
| | - Christiane Roscher
- German Centre for Integrative Biodiversity Research (iDiv) Halle-Jena-Leipzig, Leipzig04103, Germany
- Department of Physiological Diversity, Helmholtz-Centre for Environmental Research–UFZ, Leipzig04318, Germany
| | - Ana M. Sánchez
- Department of Biology and Geology, Rey Juan Carlos University, Madrid28032, Spain
| | - Bráulio A. Santos
- Departamento de Sistemática e Ecologia, Universidade Federal da Paraíba, Cidade Universitária, Castelo Branco, João Pessoa, PB58051-900, Brazil
| | - María Cecilia Scarfó
- Centro de Recursos Naturales Renovables de la Zona Semiárida–CONICET, Departamento de Biología, Bioquímica y Farmacia, Universidad Nacional del Sur,Bahía Blanca8000FTN, Argentina
| | - Eric W. Seabloom
- Department of Ecology, Evolution, and Behavior, University of Minnesota, Saint Paul, MN55108
| | - Baoku Shi
- Institute of Grassland Science, Key Laboratory of Vegetation Ecology of the Ministry of Education, Jilin Songnen Grassland Ecosystem National Observation and Research Station, Northeast Normal University, Changchun130024, China
| | - Lara Souza
- School of Biological Sciences, University of Oklahoma, Norman, OK73019
- Oklahoma Biological Survey, University of Oklahoma, Norman, OK73019
| | - Andreas Stampfli
- School of Agricultural, Forest and Food Sciences, Bern University of Applied Sciences,Zollikofen3052, Switzerland
- Institute of Plant Sciences, University of Bern, Bern3013, Switzerland
- Oeschger Center for Climate Change Research, University of Bern, Bern3012, Switzerland
| | - Rachel J. Standish
- Institute of Plant Sciences, University of Bern, Bern3013, Switzerland
- Environmental and Conservation Sciences, Murdoch University,Murdoch, WA6150, Australia
| | - Marcelo Sternberg
- School of Plant Sciences and Food Security, Faculty of Life Sciences, Tel Aviv University, Tel Aviv69978, Israel
| | - Wei Sun
- Institute of Grassland Science, Key Laboratory of Vegetation Ecology of the Ministry of Education, Jilin Songnen Grassland Ecosystem National Observation and Research Station, Northeast Normal University, Changchun130024, China
| | - Marie Sünnemann
- German Centre for Integrative Biodiversity Research (iDiv) Halle-Jena-Leipzig, Leipzig04103, Germany
- Institute of Biology, Leipzig University, Leipzig04103, Germany
| | - Michelle Tedder
- School of Life Sciences, University of Kwazulu-Natal, Pietermaritzburg3201, South Africa
| | - Pål Thorvaldsen
- Norwegian Institute of Bioeconomy Research, Department of Landscape and Biodiversity, Tjøtta8860, Norway
| | - Dashuan Tian
- Key Laboratory of Ecosystem Network Observation and Modeling, Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing100101, China
| | - Katja Tielbörger
- Plant Ecology Group, Department of Biology, University of Tübingen, Tübingen72076, Germany
| | - Alejandro Valdecantos
- Departamento de Ecologia, Universidad de Alicante, 03690 Alicante, Spain
- Instituto Multidisciplinar para el Estudio del Medio “Ramón Margalef”, Universidad de Alicante, 03690 Alicante, Spain
| | - Liesbeth van den Brink
- Plant Ecology Group, Department of Biology, University of Tübingen, Tübingen72076, Germany
| | - Vigdis Vandvik
- Department of Biological Sciences, University of Bergen, Bergen5007, Norway
| | - Mathew R. Vankoughnett
- Nova Scotia Community College, Annapolis Valley Campus, Applied Research, Middleton,NSB0S 1P0, Canada
| | | | - Changhui Wang
- College of Grassland Science, Shanxi Agricultural University, Jinzhong030801, China
| | - Yi Wang
- Institute of Resources and Environment, International Centre for Bamboo and Rattan, Key Laboratory of National Forestry and Grassland Administration and Beijing for Bamboo and Rattan Science and Technology, Beijing100102, China
| | - Glenda M. Wardle
- School of Life and Environmental Sciences, The University of Sydney, Camperdown, NSW2006, Australia
| | - Christiane Werner
- Ecosystem Physiology, Faculty of Environment and Natural Resources, Albert-Ludwig-University of Freiburg, Freiburg79110, Germany
| | - Cunzheng Wei
- State Key Laboratory of Vegetation and Environmental Change, Institute of Botany, Chinese Academy of Sciences, Beijing100093, China
| | - Georg Wiehl
- Commonwealth Scientific and Industrial Research Organization (CSIRO) Environment, Wembley, WA6913, Australia
| | - Jennifer L. Williams
- Department of Geography and Biodiversity Research Centre, University of British Columbia, Vancouver, BCV6T 1Z4, Canada
| | - Amelia A. Wolf
- Department of Integrative Biology, University of Texas, Austin, TX78712
| | - Michaela Zeiter
- School of Agricultural, Forest and Food Sciences, Bern University of Applied Sciences,Zollikofen3052, Switzerland
- Institute of Plant Sciences, University of Bern, Bern3013, Switzerland
- Oeschger Center for Climate Change Research, University of Bern, Bern3012, Switzerland
| | - Fawei Zhang
- Key Laboratory of Adaptation and Evolution of Plateau Biota, Northwest Institute of Plateau Biology, Chinese Academy of Sciences, Xining, Qinghai810008, China
| | - Juntao Zhu
- Key Laboratory of Ecosystem Network Observation and Modeling, Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing100101, China
| | - Ning Zong
- Key Laboratory of Ecosystem Network Observation and Modeling, Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing100101, China
| | - Xiaoan Zuo
- Urat Desert-grassland Research Station, Northwest Institute of Eco-Environment and Resources, Chinese Academy of Science, Lanzhou730000, China
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Dewees SL, D'Antonio CM, Molinari N. Determining potential drivers of vegetation change in a Mediterranean environment. Ecosphere 2022. [DOI: 10.1002/ecs2.4313] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 12/15/2022] Open
Affiliation(s)
- Shane L. Dewees
- University of California, Santa Barbara Santa Barbara California USA
| | | | - Nicole Molinari
- United States Forest Service, Los Padres National Forest Goleta California USA
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Drake-Schultheis L, D'Antonio CM, Oono R. Patterns and Distribution of Botryosphaeriaceae Fungi Related to Dieback in Big Berry Manzanita. Phytopathology 2022; 112:2341-2350. [PMID: 35731020 DOI: 10.1094/phyto-02-22-0044-r] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 06/15/2023]
Abstract
Dieback and mortality in wildland plant species due to climate change have been on the rise in recent decades, and latent fungal pathogens might play a significant role in these events. During a severe multiyear drought, canopy dieback associated with latent pathogens in the Botryosphaeriaceae (Bot) family was observed in stands of a dominant shrub species, big berry manzanita (Arctostaphylos glauca), across chaparral landscapes in California. These fungi are significant pathogens of woody agricultural species, especially in hosts experiencing stress, and have become a threat to economically important crops worldwide. However, little is known regarding their occurrence, distribution, and impact in wildland systems. We conducted a field survey of 300 A. glauca shrubs across an elevational gradient to identify Bot species infection as it relates to (i) A. glauca dieback severity and (ii) landscape variables associated with plant drought stress. Our results show that Bots are widely infecting A. glauca across the landscape, and there is a significant correlation between elevation and dieback severity. Dieback severity was significantly higher at lower elevations, suggesting that infected shrubs at lower elevations are at greater risk than those at higher elevations. Furthermore, two Bot species, Neofusicoccum australe and Botryosphaeria dothidea, were most frequently isolated, with N. australe being the most common and, based on haplotype analysis, likely the most recently introduced of the two. Our results confirm the wide distribution of latent Bot fungi in a wild shrubland system and provide valuable insight into areas of greatest risk for future shrub dieback and mortality. These findings could be particularly useful for informing future wildlands management strategies with regard to introduced latent pathogens.
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Affiliation(s)
- Laura Drake-Schultheis
- Ecology, Evolution, and Marine Biology Department, University of California, Santa Barbara, CA 93106
- Life Sciences Department, Westmont College, Santa Barbara, CA 93108
| | - Carla M D'Antonio
- Ecology, Evolution, and Marine Biology Department, University of California, Santa Barbara, CA 93106
| | - Ryoko Oono
- Ecology, Evolution, and Marine Biology Department, University of California, Santa Barbara, CA 93106
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Yelenik SG, Rehm EM, D'Antonio CM. Can the impact of canopy trees on soil and understory be altered using litter additions? Ecol Appl 2022; 32:e02477. [PMID: 34657347 DOI: 10.1002/eap.2477] [Citation(s) in RCA: 3] [Impact Index Per Article: 1.5] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 03/18/2021] [Revised: 05/13/2021] [Accepted: 07/07/2021] [Indexed: 06/13/2023]
Abstract
Trees can have large effects on soil nutrients in ways that alter succession, particularly in the case of nitrogen-(N)-fixing trees. In Hawai'i, forest restoration relies heavily on use of a native N-fixing tree, Acacia koa (koa), but this species increases soil-available N and likely facilitates competitive dominance of exotic pasture grasses. In contrast, Metrosideros polymorpha ('ōhi'a), the dominant native tree in Hawai'i, is less often planted because it is slow growing; yet it is typically associated with lower soil N and grass biomass, and greater native understory recruitment. We experimentally tested whether it is possible to reverse high soil N under koa by adding 'ōhi'a litter, using additions of koa litter or no litter as controls, over 2.5 yr. We then quantified natural litterfall and decomposition rates of 'ōhi'a and koa litter to place litter additions in perspective. Finally, we quantified whether litter additions altered grass biomass and if this had effects on native outplants. Adding 'ōhi'a litter increased soil carbon, but increased rather than decreased inorganic soil N pools. Contrary to expectations, koa litter decomposed more slowly than 'ōhi'a, although it released more N per unit of litter. We saw no reduction in grass biomass due to 'ōhi'a litter addition, and no change in native outplanted understory survival or growth. We conclude that the high N soil conditions under koa are difficult to reverse. However, we also found that outplanted native woody species were able to decrease exotic grass biomass over time, regardless of the litter environment, making this a better strategy for lowering exotic species impacts.
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Affiliation(s)
- Stephanie G Yelenik
- U.S. Geological Survey, Pacific Island Ecosystems Research Center, Hawai'i National Park, Hawai'i, 96718, USA
| | - Evan M Rehm
- Department of Ecology, Evolution and Marine Biology, University of California at Santa Barbara, Santa Barbara, California, 93106, USA
| | - Carla M D'Antonio
- Department of Ecology, Evolution and Marine Biology, University of California at Santa Barbara, Santa Barbara, California, 93106, USA
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Long RW, Dudley TL, D'Antonio CM, Grady KC, Bush SE, Hultine KR. Spenders versus savers: Climate‐induced carbon allocation trade‐offs in a recently introduced woody plant. Funct Ecol 2021. [DOI: 10.1111/1365-2435.13862] [Citation(s) in RCA: 3] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 01/28/2023]
Affiliation(s)
- Randall W. Long
- Department of Ecology, Evolution and Marine Biology University of California‐Santa Barbara Santa Barbara CA USA
| | - Tom L. Dudley
- Marine Science Institute University of California‐Santa Barbara Santa Barbara CA USA
| | - Carla M. D'Antonio
- Department of Ecology, Evolution and Marine Biology University of California‐Santa Barbara Santa Barbara CA USA
| | - Kevin C. Grady
- School of Forestry Northern Arizona University Flagstaff AZ USA
| | - Susan E. Bush
- Department of Research, Conservation and Collections Desert Botanical Garden Phoenix AZ USA
| | - Kevin R. Hultine
- Department of Research, Conservation and Collections Desert Botanical Garden Phoenix AZ USA
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Drake-Schultheis L, Oono R, D'Antonio CM. Mechanisms of severe dieback and mortality in a classically drought-tolerant shrubland species (Arctostaphylos glauca). Am J Bot 2020; 107:1136-1147. [PMID: 32864741 DOI: 10.1002/ajb2.1522] [Citation(s) in RCA: 1] [Impact Index Per Article: 0.3] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 08/01/2019] [Accepted: 05/06/2020] [Indexed: 06/11/2023]
Abstract
PREMISE Mortality events involving drought and pathogens in natural plant systems are on the rise due to global climate change. In Santa Barbara, California, United States, big berry manzanita (Arctostaphylos glauca) has experienced canopy dieback related to a multi-year drought and infection from fungal pathogens in the Botryosphaeriaceae family. A greenhouse experiment was conducted using Neofusicoccum australe to test the specific influences of drought and fungal infection on A. glauca. METHODS A full factorial design was used to compare four treatment groups (drought + inoculation; drought - inoculation; watering + inoculation; and control: watering - inoculation). Data were collected for 10 weeks on stress symptoms, changes in leaf fluorescence and photosynthesis, and mortality. RESULTS Results indicated significant effects of watering and inoculation treatments on net photosynthesis, dark-adapted fluorescence, and disease symptom severity (P < 0.05), and a strong correlation was found between physiological decline and visible stress (P < 0.0001). Mortality differed between treatments, with all groups except for the control experiencing mortality (43% mortality in drought - inoculation, 83% in watering - inoculation, and 100% in drought + inoculation). A Kaplan-Meier survival analysis showed drought + inoculation to have the least estimated survivorship compared to all other treatment groups. CONCLUSIONS In addition to a possible synergistic interaction between drought and fungal infection in disease onset and mortality rates in A. glauca, these results indicate that young, non-drought-stressed plants are susceptible to mortality from N. australe infection, with important implications for the future of wildland shrub communities.
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Affiliation(s)
- Laura Drake-Schultheis
- Department of Ecology, Evolution, and Marine Biology, University of California, Santa Barbara, CA, 93106, USA
| | - Ryoko Oono
- Department of Ecology, Evolution, and Marine Biology, University of California, Santa Barbara, CA, 93106, USA
| | - Carla M D'Antonio
- Department of Ecology, Evolution, and Marine Biology, University of California, Santa Barbara, CA, 93106, USA
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Affiliation(s)
- Nathan C. Emery
- Michigan State University 220 Trowbridge Road East Lansing Michigan 48824 USA
| | - Carla M. D'Antonio
- University of California Santa Barbara Santa Barbara California 93106 USA
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Abstract
Most ecosystems have multiple-plant invaders rather than single-plant invaders, yet ecological studies and management actions focus largely on single invader species. There is a need for general principles regarding invader interactions across varying environmental conditions, so that secondary invasions can be anticipated and managers can allocate resources toward pretreatment or postremoval actions. By reviewing removal experiments conducted in three Hawaiian ecosystems (a dry tropical forest, a seasonally dry mesic forest, and a lowland wet forest), we evaluate the roles environmental harshness, priority effects, productivity potential, and species interactions have in influencing secondary invasions, defined here as invasions that are influenced either positively (facilitation) or negatively (inhibition/priority effects) by existing invaders. We generate a conceptual model with a surprise index to describe whether long-term plant invader composition and dominance is predictable or stochastic after a system perturbation such as a removal experiment. Under extremely low resource availability, the surprise index is low, whereas under intermediate-level resource environments, invader dominance is more stochastic and the surprise index is high. At high resource levels, the surprise index is intermediate: Invaders are likely abundant in the environment but their response to a perturbation is more predictable than at intermediate resource levels. We suggest further testing across environmental gradients to determine key variables that dictate the predictability of postremoval invader composition.
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Affiliation(s)
- Carla M. D'Antonio
- Environmental Studies Program and Department of Ecology, Evolution, and Marine Biology, University of California, Santa Barbara, California 93106
| | - Rebecca Ostertag
- Department of Biology, University of Hawai‘i, Hilo, Hawai‘i 96720
| | - Susan Cordell
- Institute of Pacific Islands Forestry, USDA Forest Service, Hilo, Hawai‘i 96720
| | - Stephanie Yelenik
- USGS Pacific Islands Ecosystem Research Center, Volcano, Hawai‘i 96718
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Flores-Moreno H, Reich PB, Lind EM, Sullivan LL, Seabloom EW, Yahdjian L, MacDougall AS, Reichmann LG, Alberti J, Báez S, Bakker JD, Cadotte MW, Caldeira MC, Chaneton EJ, D'Antonio CM, Fay PA, Firn J, Hagenah N, Harpole WS, Iribarne O, Kirkman KP, Knops JMH, La Pierre KJ, Laungani R, Leakey ADB, McCulley RL, Moore JL, Pascual J, Borer ET. Climate modifies response of non-native and native species richness to nutrient enrichment. Philos Trans R Soc Lond B Biol Sci 2017; 371:rstb.2015.0273. [PMID: 27114575 DOI: 10.1098/rstb.2015.0273] [Citation(s) in RCA: 29] [Impact Index Per Article: 4.1] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Accepted: 02/01/2016] [Indexed: 01/17/2023] Open
Abstract
Ecosystem eutrophication often increases domination by non-natives and causes displacement of native taxa. However, variation in environmental conditions may affect the outcome of interactions between native and non-native taxa in environments where nutrient supply is elevated. We examined the interactive effects of eutrophication, climate variability and climate average conditions on the success of native and non-native plant species using experimental nutrient manipulations replicated at 32 grassland sites on four continents. We hypothesized that effects of nutrient addition would be greatest where climate was stable and benign, owing to reduced niche partitioning. We found that the abundance of non-native species increased with nutrient addition independent of climate; however, nutrient addition increased non-native species richness and decreased native species richness, with these effects dampened in warmer or wetter sites. Eutrophication also altered the time scale in which grassland invasion responded to climate, decreasing the importance of long-term climate and increasing that of annual climate. Thus, climatic conditions mediate the responses of native and non-native flora to nutrient enrichment. Our results suggest that the negative effect of nutrient addition on native abundance is decoupled from its effect on richness, and reduces the time scale of the links between climate and compositional change.
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Affiliation(s)
- Habacuc Flores-Moreno
- Department of Ecology, Evolution, and Behavior, University of Minnesota, St Paul, MN 55108, USA Department of Forest Resources, University of Minnesota, St Paul, MN 55108, USA
| | - Peter B Reich
- Department of Forest Resources, University of Minnesota, St Paul, MN 55108, USA Hawkesbury Institute for the Environment, Western Sydney University, Penrith, New South Wales 2751, Australia
| | - Eric M Lind
- Department of Ecology, Evolution, and Behavior, University of Minnesota, St Paul, MN 55108, USA
| | - Lauren L Sullivan
- Department of Ecology, Evolution, and Behavior, University of Minnesota, St Paul, MN 55108, USA
| | - Eric W Seabloom
- Department of Ecology, Evolution, and Behavior, University of Minnesota, St Paul, MN 55108, USA
| | - Laura Yahdjian
- IFEVA-CONICET and Facultad de Agronomía, Universidad de Buenos Aires, 1417 Buenos Aires, Argentina
| | - Andrew S MacDougall
- Department of Integrative Biology, University of Guelph, Guelph, Ontario, Canada N1G 2W1
| | - Lara G Reichmann
- USDA-ARS Grassland, Soil and Water Research Laboratory, Temple, TX, TX 76502, USA
| | - Juan Alberti
- Instituto de Investigaciones Marinas y Costeras (IIMyC), Consejo Nacional de Investigaciones Científicas y Técnicas (CONICET), Universidad Nacional de Mar del Plata, Mar del Plata 7600, Argentina
| | - Selene Báez
- Consorcio para el Desarrollo Sostenible de la Ecoregión Andina (CONDESAN), Quito, Ecuador
| | - Jonathan D Bakker
- School of Environmental and Forest Sciences, University of Washington, Seattle, WA 98195, USA
| | - Marc W Cadotte
- Department of Biological Sciences, University of Toronto-Scarborough, 1265 Military Trail, Toronto, Ontario, Canada M1C 2M2
| | - Maria C Caldeira
- Centro de Estudos Florestais, Instituto Superior de Agronomia, Universidade de Lisboa, Tapada da Ajuda, 1349-017 Lisbon, Portugal
| | - Enrique J Chaneton
- IFEVA-CONICET and Facultad de Agronomía, Universidad de Buenos Aires, 1417 Buenos Aires, Argentina
| | - Carla M D'Antonio
- Environmental Studies Program, University of CA, Santa Barbara, CA 93106, USA
| | - Philip A Fay
- USDA-ARS Grassland, Soil and Water Research Laboratory, Temple, TX, TX 76502, USA
| | - Jennifer Firn
- School of Earth, Environmental and Biological Sciences, Queensland University of Technology, Brisbane, Queensland 4001, Australia
| | - Nicole Hagenah
- School of Life Sciences, University of KwaZulu-Natal, Pietermaritzburg, South Africa
| | - W Stanley Harpole
- Department of Physiological Diversity, Helmholtz Center for Environmental Research-UFZ, Permoserstrasse 15, 04318 Leipzig, Germany German Centre for Integrative Biodiversity Research (iDiv), Deutscher Platz 5e, 04103 Leipzig, Germany Martin Luther University Halle-Wittenberg, Am Kirchtor 1, 06108 Halle (Saale), Germany
| | - Oscar Iribarne
- Instituto de Investigaciones Marinas y Costeras (IIMyC), Consejo Nacional de Investigaciones Científicas y Técnicas (CONICET), Universidad Nacional de Mar del Plata, Mar del Plata 7600, Argentina
| | - Kevin P Kirkman
- School of Life Sciences, University of KwaZulu-Natal, Pietermaritzburg, South Africa
| | - Johannes M H Knops
- School of Biological Sciences, University of Nebraska, Lincoln, NE 68588, USA
| | - Kimberly J La Pierre
- Department of Integrative Biology, University of California, Berkeley, CA 94720, USA
| | | | - Andrew D B Leakey
- Department of Plant Biology and Institute for Genomic Biology, University of Illinois at Urbana-Champaign, Urbana, IL 61801, USA
| | - Rebecca L McCulley
- Department of Plant and Soil Science, University of Kentucky, Lexington, KY 40546-0091, USA
| | - Joslin L Moore
- School of Biological Sciences, Monash University, Clayton, VIC 3800, Australia
| | - Jesus Pascual
- Instituto de Investigaciones Marinas y Costeras (IIMyC), Consejo Nacional de Investigaciones Científicas y Técnicas (CONICET), Universidad Nacional de Mar del Plata, Mar del Plata 7600, Argentina
| | - Elizabeth T Borer
- Department of Ecology, Evolution, and Behavior, University of Minnesota, St Paul, MN 55108, USA
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Strayer DL, D'Antonio CM, Essl F, Fowler MS, Geist J, Hilt S, Jarić I, Jöhnk K, Jones CG, Lambin X, Latzka AW, Pergl J, Pyšek P, Robertson P, Schmalensee M, Stefansson RA, Wright J, Jeschke JM. Boom‐bust dynamics in biological invasions: towards an improved application of the concept. Ecol Lett 2017; 20:1337-1350. [DOI: 10.1111/ele.12822] [Citation(s) in RCA: 65] [Impact Index Per Article: 9.3] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 11/11/2016] [Revised: 12/19/2016] [Accepted: 07/20/2017] [Indexed: 01/08/2023]
Affiliation(s)
- David L. Strayer
- Cary Institute of Ecosystem Studies Millbrook NY USA
- Freie Universität Berlin Berlin Germany
| | - Carla M. D'Antonio
- Department of Ecology, Evolution, and Marine Biology University of California Santa Barbara Santa Barbara CA USA
| | - Franz Essl
- Division of Conservation Vegetation and Landscape Ecology University of Vienna Vienna Austria
| | - Mike S. Fowler
- Department of Biosciences Swansea University Singleton Park UK
| | - Juergen Geist
- Aquatic Systems Biology Unit Technical University of Munich Freising Germany
| | - Sabine Hilt
- Leibniz‐Institute of Freshwater Ecology and Inland Fisheries (IGB) Berlin Germany
| | - Ivan Jarić
- Leibniz‐Institute of Freshwater Ecology and Inland Fisheries (IGB) Berlin Germany
- Institute for Multidisciplinary Research University of Belgrade BelgradeSerbia
| | - Klaus Jöhnk
- Commonwealth Scientific and Industrial Research Organisation Land and Water Black Mountain Canberra Australia
| | | | - Xavier Lambin
- School of Biological Sciences University of Aberdeen Aberdeen UK
| | - Alexander W. Latzka
- Department of Natural Resource Sciences McGill University‐MacDonald Campus Saint‐Anne‐de‐Bellevue Canada
| | - Jan Pergl
- Institute of Botany Department of Invasion Ecology The Czech Academy of Sciences Průhonice Czech Republic
| | - Petr Pyšek
- Department of Invasion Ecology Institute of Botany The Czech Academy of Sciences Průhonice Czech Republic
- Department of Ecology Faculty of Science Charles University Viničná 7 Prague 2 Czech Republic
- Centre for Invasion Biology Department of Botany & Zoology Stellenbosch University Matieland7602 South Africa
| | | | - Menja Schmalensee
- West Iceland Nature Research Centre Stykkishólmur Iceland
- Faculty of Life and Environmental Sciences University of Iceland Reykjavík Iceland
| | | | | | - Jonathan M. Jeschke
- Freie Universität Berlin Berlin Germany
- Leibniz‐Institute of Freshwater Ecology and Inland Fisheries (IGB) Berlin Germany
- Berlin‐Brandenburg Institute of Advanced Biodiversity Research (BBIB) Berlin Germany
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11
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Long RW, Bush SE, Grady KC, Smith DS, Potts DL, D'Antonio CM, Dudley TL, Fehlberg SD, Gaskin JF, Glenn EP, Hultine KR. Can local adaptation explain varying patterns of herbivory tolerance in a recently introduced woody plant in North America? Conserv Physiol 2017; 5:cox016. [PMID: 28852513 PMCID: PMC5570027 DOI: 10.1093/conphys/cox016] [Citation(s) in RCA: 6] [Impact Index Per Article: 0.9] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [Track Full Text] [Subscribe] [Scholar Register] [Received: 09/21/2016] [Revised: 02/14/2017] [Accepted: 02/23/2017] [Indexed: 05/30/2023]
Abstract
Patterns of woody-plant mortality have been linked to global-scale environmental changes, such as extreme drought, heat stress, more frequent and intense fires, and episodic outbreaks of insects and pathogens. Although many studies have focussed on survival and mortality in response to specific physiological stresses, little attention has been paid to the role of genetic heritability of traits and local adaptation in influencing patterns of plant mortality, especially in non-native species. Tamarix spp. is a dominant, non-native riparian tree in western North America that is experiencing dieback in some areas of its range due to episodic herbivory by the recently introduced northern tamarisk leaf beetle (Diorhabda carinulata). We propose that genotype × environment interactions largely underpin current and future patterns of Tamarix mortality. We anticipate that (i) despite its recent introduction, and the potential for significant gene flow, Tamarix in western North America is generally adapted to local environmental conditions across its current range in part due to hybridization of two species; (ii) local adaptation to specific climate, soil and resource availability will yield predictable responses to episodic herbivory; and (iii) the ability to cope with a combination of episodic herbivory and increased aridity associated with climate change will be largely based on functional tradeoffs in resource allocation. This review focusses on the potential heritability of plant carbon allocation patterns in Tamarix, focussing on the relative contribution of acquired carbon to non-structural carbohydrate (NSC) pools versus other sinks as the basis for surviving episodic disturbance. Where high aridity and/or poor edaphic position lead to chronic stress, NSC pools may fall below a minimum threshold because of an imbalance between the supply of carbon and its demand by various sinks. Identifying patterns of local adaptation of traits related to resource allocation will improve forecasting of Tamarix population susceptibility to episodic herbivory.
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Affiliation(s)
- Randall W. Long
- Department of Ecology, Evolution and Marine Biology, University of California-Santa Barbara, Bldg 520, RM 4001, Fl 4L, Santa Barbara, CA 93106, USA
| | - Susan E. Bush
- School of Forestry, Northern Arizona University, S San Francisco St, Flagstaff, AZ 86011, USA
| | - Kevin C. Grady
- School of Forestry, Northern Arizona University, S San Francisco St, Flagstaff, AZ 86011, USA
| | - David S. Smith
- Keck Science Department, Claremont McKenna, Pitzer and Scripps Colleges, 925 N. Mills Ave, Claremont, CA 91711, USA
| | - Daniel L. Potts
- Biology Department, SUNY Buffalo State, 1300 Elmwood Ave, Buffalo, NY 14222, USA
| | - Carla M. D'Antonio
- School of Forestry, Northern Arizona University, S San Francisco St, Flagstaff, AZ 86011, USA
| | - Tom L. Dudley
- Marine Science Institute, University of California-Santa Barbara, Bldg 520, RM 4001, Fl 4L, Santa Barbara, CA 93106, USA
| | - Shannon D. Fehlberg
- Department of Research, Conservation and Collections, Desert Botanical Garden, 1201 N Galvin Pkwy, Phoenix, AZ 85008, USA
| | - John F. Gaskin
- USDA Agricultural Research Service, 1500 North Central Avenue, Sidney, MT 59270, USA
| | - Edward P. Glenn
- Department of Soil, Water and Environmental Science, University of Arizona, 1428 E University Blvd, Tucson, AZ 85719, USA
| | - Kevin R. Hultine
- Department of Research, Conservation and Collections, Desert Botanical Garden, 1201 N Galvin Pkwy, Phoenix, AZ 85008, USA
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Liao H, D'Antonio CM, Chen B, Huang Q, Peng S. How much do phenotypic plasticity and local genetic variation contribute to phenotypic divergences along environmental gradients in widespread invasive plants? A meta-analysis. OIKOS 2016. [DOI: 10.1111/oik.02372] [Citation(s) in RCA: 38] [Impact Index Per Article: 4.8] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/30/2022]
Affiliation(s)
- Huixuan Liao
- State Key Laboratory of Biocontrol and Guangdong Key Laboratory of Plant Resources, School of Life Sciences, Sun Yat-sen Univ.; CN-510006 Guangzhou PR China
| | - Carla M. D'Antonio
- Ecology Evolution and Marine Biology; Univ. of California; Santa Barbara CA 93106-4160 USA
| | - Baoming Chen
- State Key Laboratory of Biocontrol and Guangdong Key Laboratory of Plant Resources, School of Life Sciences, Sun Yat-sen Univ.; CN-510006 Guangzhou PR China
| | - Qiaoqiao Huang
- Inst. of Environment and Plant Protection, Chinese Academy of Tropical Agricultural Sciences; CN-571737 Danzhou PR China
| | - Shaolin Peng
- State Key Laboratory of Biocontrol and Guangdong Key Laboratory of Plant Resources, School of Life Sciences, Sun Yat-sen Univ.; CN-510006 Guangzhou PR China
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Stahlheber KA, Crispin KL, Anton C, D'Antonio CM. The ghosts of trees past: savanna trees create enduring legacies in plant species composition. Ecology 2015; 96:2510-22. [DOI: 10.1890/14-2035.1] [Citation(s) in RCA: 18] [Impact Index Per Article: 2.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Track Full Text] [Journal Information] [Submit a Manuscript] [Subscribe] [Scholar Register] [Indexed: 11/18/2022]
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Flory SL, D'Antonio CM. Taking the long view on the ecological effects of plant invasions. Am J Bot 2015; 102:817-818. [PMID: 26101408 DOI: 10.3732/ajb.1500105] [Citation(s) in RCA: 9] [Impact Index Per Article: 1.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 03/16/2015] [Accepted: 05/12/2015] [Indexed: 06/04/2023]
Affiliation(s)
- S Luke Flory
- Agronomy Department, University of Florida, Gainesville, Florida 32611 USA
| | - Carla M D'Antonio
- Department of Ecology, Evolution, and Marine Biology, University of California, Santa Barbara, Santa Barbara, California 93106 USA
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15
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Yelenik SG, DiManno N, D'Antonio CM. Evaluating nurse plants for restoring native woody species to degraded subtropical woodlands. Ecol Evol 2014; 5:300-13. [PMID: 25709807 PMCID: PMC4314263 DOI: 10.1002/ece3.1294] [Citation(s) in RCA: 21] [Impact Index Per Article: 2.1] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 07/21/2014] [Revised: 08/29/2014] [Accepted: 09/04/2014] [Indexed: 11/17/2022] Open
Abstract
Harsh habitats dominated by invasive species are difficult to restore. Invasive grasses in arid environments slow succession toward more desired composition, yet grass removal exacerbates high light and temperature, making the use of “nurse plants” an appealing strategy. In this study of degraded subtropical woodlands dominated by alien grasses in Hawai'i, we evaluated whether individuals of two native (Dodonaea viscosa, Leptocophylla tameiameia) and one non-native (Morella faya) woody species (1) act as natural nodes of recruitment for native woody species and (2) can be used to enhance survivorship of outplanted native woody species. To address these questions, we quantified the presence and persistence of seedlings naturally recruiting beneath adult nurse shrubs and compared survival and growth of experimentally outplanted seedlings of seven native woody species under the nurse species compared to intact and cleared alien-grass plots. We found that the two native nurse shrubs recruit their own offspring, but do not act as establishment nodes for other species. Morella faya recruited even fewer seedlings than native shrubs. Thus, outplanting will be necessary to increase abundance and diversity of native woody species. Outplant survival was the highest under shrubs compared to away from them with few differences between nurse species. The worst habitat for native seedling survival and growth was within the unmanaged invasive grass matrix. Although the two native nurse species did not differentially affect outplant survival, D. viscosa is the most widespread and easily propagated and is thus more likely to be useful as an initial nurse species. The outplanted species showed variable responses to nurse habitats that we attribute to resource requirements resulting from their typical successional stage and nitrogen fixation capability.
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Affiliation(s)
- Stephanie G Yelenik
- U.S. Geological Survey, Pacific Island Ecosystems Research Center Hawai'i National Park, Hawai'i
| | - Nicole DiManno
- Hawai'i Cooperative Studies Unit, University of Hawai'i Hilo, Hawai'i
| | - Carla M D'Antonio
- Environmental Studies, University of California Santa Barbara, California
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16
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Meng R, Dennison PE, D'Antonio CM, Moritz MA. Remote sensing analysis of vegetation recovery following short-interval fires in Southern California shrublands. PLoS One 2014; 9:e110637. [PMID: 25337785 PMCID: PMC4206446 DOI: 10.1371/journal.pone.0110637] [Citation(s) in RCA: 38] [Impact Index Per Article: 3.8] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Track Full Text] [Download PDF] [Figures] [Journal Information] [Subscribe] [Scholar Register] [Received: 12/17/2013] [Accepted: 09/24/2014] [Indexed: 11/18/2022] Open
Abstract
Increased fire frequency has been shown to promote alien plant invasions in the western United States, resulting in persistent vegetation type change. Short interval fires are widely considered to be detrimental to reestablishment of shrub species in southern California chaparral, facilitating the invasion of exotic annuals and producing "type conversion". However, supporting evidence for type conversion has largely been at local, site scales and over short post-fire time scales. Type conversion has not been shown to be persistent or widespread in chaparral, and past range improvement studies present evidence that chaparral type conversion may be difficult and a relatively rare phenomenon across the landscape. With the aid of remote sensing data covering coastal southern California and a historical wildfire dataset, the effects of short interval fires (<8 years) on chaparral recovery were evaluated by comparing areas that burned twice to adjacent areas burned only once. Twelve pairs of once- and twice-burned areas were compared using normalized burn ratio (NBR) distributions. Correlations between measures of recovery and explanatory factors (fire history, climate and elevation) were analyzed by linear regression. Reduced vegetation cover was found in some lower elevation areas that were burned twice in short interval fires, where non-sprouting species are more common. However, extensive type conversion of chaparral to grassland was not evident in this study. Most variables, with the exception of elevation, were moderately or poorly correlated with differences in vegetation recovery.
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Affiliation(s)
- Ran Meng
- Department of Geography, University of Utah, Salt Lake City, Utah, United States of America
| | - Philip E Dennison
- Department of Geography, University of Utah, Salt Lake City, Utah, United States of America
| | - Carla M D'Antonio
- Department of Ecology, Evolution and Marine Biology, University of California Santa Barbara, Santa Barbara, California, United States of America
| | - Max A Moritz
- Department of Environmental Science, Policy, and Management, University of California, Berkeley, California, United States of America
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17
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Affiliation(s)
- Karen A. Stahlheber
- Department of Ecology, Evolution and Marine Biology; University of California Santa Barbara; Santa Barbara CA 93106 U.S.A
| | - Carla M. D'Antonio
- Department of Ecology, Evolution and Marine Biology; University of California Santa Barbara; Santa Barbara CA 93106 U.S.A
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18
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Affiliation(s)
- Nicole A. Molinari
- Department of Ecology, Evolution and Marine Biology University of California Santa Barbara CA 93106 USA
| | - Carla M. D'Antonio
- Department of Environmental Studies University of California Santa Barbara CA 93106 USA
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19
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Ibáñez I, Diez JM, Miller LP, Olden JD, Sorte CJB, Blumenthal DM, Bradley BA, D'Antonio CM, Dukes JS, Early RI, Grosholz ED, Lawler JJ. Integrated assessment of biological invasions. Ecol Appl 2014; 24:25-37. [PMID: 24640532 DOI: 10.1890/13-0776.1] [Citation(s) in RCA: 24] [Impact Index Per Article: 2.4] [Reference Citation Analysis] [What about the content of this article? (0)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 06/03/2023]
Abstract
As the main witnesses of the ecological and economic impacts of invasions on ecosystems around the world, ecologists seek to provide the relevant science that informs managers about the potential for invasion of specific organisms in their region(s) of interest. Yet, the assorted literature that could inform such forecasts is rarely integrated to do so, and further, the diverse nature of the data available complicates synthesis and quantitative prediction. Here we present a set of analytical tools for synthesizing different levels of distributional and/or demographic data to produce meaningful assessments of invasion potential that can guide management at multiple phases of ongoing invasions, from dispersal to colonization to proliferation. We illustrate the utility of data-synthesis and data-model assimilation approaches with case studies of three well-known invasive species--a vine, a marine mussel, and a freshwater crayfish--under current and projected future climatic conditions. Results from the integrated assessments reflect the complexity of the invasion process and show that the most relevant climatic variables can have contrasting effects or operate at different intensities across habitat types. As a consequence, for two of the study species climate trends will increase the likelihood of invasion in some habitats and decrease it in others. Our results identified and quantified both bottlenecks and windows of opportunity for invasion, mainly related to the role of human uses of the landscape or to disruption of the flow of resources. The approach we describe has a high potential to enhance model realism, explanatory insight, and predictive capability, generating information that can inform management decisions and optimize phase-specific prevention and control efforts for a wide range of biological invasions.
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20
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Seabloom EW, Borer ET, Buckley Y, Cleland EE, Davies K, Firn J, Harpole WS, Hautier Y, Lind E, MacDougall A, Orrock JL, Prober SM, Adler P, Alberti J, Anderson TM, Bakker JD, Biederman LA, Blumenthal D, Brown CS, Brudvig LA, Caldeira M, Chu C, Crawley MJ, Daleo P, Damschen EI, D'Antonio CM, DeCrappeo NM, Dickman CR, Du G, Fay PA, Frater P, Gruner DS, Hagenah N, Hector A, Helm A, Hillebrand H, Hofmockel KS, Humphries HC, Iribarne O, Jin VL, Kay A, Kirkman KP, Klein JA, Knops JMH, La Pierre KJ, Ladwig LM, Lambrinos JG, Leakey ADB, Li Q, Li W, McCulley R, Melbourne B, Mitchell CE, Moore JL, Morgan J, Mortensen B, O'Halloran LR, Pärtel M, Pascual J, Pyke DA, Risch AC, Salguero-Gómez R, Sankaran M, Schuetz M, Simonsen A, Smith M, Stevens C, Sullivan L, Wardle GM, Wolkovich EM, Wragg PD, Wright J, Yang L. Predicting invasion in grassland ecosystems: is exotic dominance the real embarrassment of richness? Glob Chang Biol 2013; 19:3677-3687. [PMID: 24038796 DOI: 10.1111/gcb.12370] [Citation(s) in RCA: 31] [Impact Index Per Article: 2.8] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 04/22/2013] [Revised: 07/16/2013] [Accepted: 08/14/2013] [Indexed: 06/02/2023]
Abstract
Invasions have increased the size of regional species pools, but are typically assumed to reduce native diversity. However, global-scale tests of this assumption have been elusive because of the focus on exotic species richness, rather than relative abundance. This is problematic because low invader richness can indicate invasion resistance by the native community or, alternatively, dominance by a single exotic species. Here, we used a globally replicated study to quantify relationships between exotic richness and abundance in grass-dominated ecosystems in 13 countries on six continents, ranging from salt marshes to alpine tundra. We tested effects of human land use, native community diversity, herbivore pressure, and nutrient limitation on exotic plant dominance. Despite its widespread use, exotic richness was a poor proxy for exotic dominance at low exotic richness, because sites that contained few exotic species ranged from relatively pristine (low exotic richness and cover) to almost completely exotic-dominated ones (low exotic richness but high exotic cover). Both exotic cover and richness were predicted by native plant diversity (native grass richness) and land use (distance to cultivation). Although climate was important for predicting both exotic cover and richness, climatic factors predicting cover (precipitation variability) differed from those predicting richness (maximum temperature and mean temperature in the wettest quarter). Herbivory and nutrient limitation did not predict exotic richness or cover. Exotic dominance was greatest in areas with low native grass richness at the site- or regional-scale. Although this could reflect native grass displacement, a lack of biotic resistance is a more likely explanation, given that grasses comprise the most aggressive invaders. These findings underscore the need to move beyond richness as a surrogate for the extent of invasion, because this metric confounds monodominance with invasion resistance. Monitoring species' relative abundance will more rapidly advance our understanding of invasions.
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Affiliation(s)
- Eric W Seabloom
- Department of Ecology, Evolution, and Behavior, University of MN, St. Paul, MN, 55108, USA
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21
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Abstract
Returning native species to habitats degraded by biological invasions is a critical conservation goal. A leading hypothesis poses that exotic plant dominance is self-reinforced by impacts on ecosystem processes, leading to persistent stable states. Invaders have been documented to modify fire regimes, alter soil nutrients or shift microbial communities in ways that feed back to benefit themselves over competitors. However, few studies have followed invasions through time to ask whether ecosystem impacts and feedbacks persist. Here we return to woodland sites in Hawai'i Volcanoes National Park that were invaded by exotic C4 grasses in the 1960s, the ecosystem impacts of which were studied intensively in the 1990s. We show that positive feedbacks between exotic grasses and soil nitrogen cycling have broken down, but rather than facilitating native vegetation, the weakening feedbacks facilitate new exotic species. Data from the 1990s showed that exotic grasses increased nitrogen-mineralization rates by two- to fourfold, but were nitrogen-limited. Thus, the impacts of the invader created a positive feedback early in the invasion. We now show that annual net soil nitrogen mineralization has since dropped to pre-invasion levels. In addition, a seedling outplanting experiment that varied soil nitrogen and grass competition demonstrates that the changing impacts of grasses do not favour native species re-establishment. Instead, decreased nitrogen availability most benefits another aggressive invader, the nitrogen-fixing tree Morella faya. Long-term studies of invasions may reveal that ecosystem impacts and feedbacks shift over time, but that this may not benefit native species recovery.
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Affiliation(s)
- Stephanie G Yelenik
- 1] Department of Ecology, Evolution, and Marine Biology, University of California, Santa Barbara, California 93106, USA [2] US Geological Survey, Pacific Island Ecosystems Research Center, Hawai'i Volcanoes National Park, Hawai'i 96718, USA
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22
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Moritz MA, Hurteau MD, Suding KN, D'Antonio CM. Bounded ranges of variation as a framework for future conservation and fire management. Ann N Y Acad Sci 2013; 1286:92-107. [DOI: 10.1111/nyas.12104] [Citation(s) in RCA: 38] [Impact Index Per Article: 3.5] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/29/2022]
Affiliation(s)
- Max A. Moritz
- Department of Environmental Science; Policy, and Management; University of California; Berkeley; California
| | - Matthew D. Hurteau
- Department of Ecosystem Science and Management; The Pennsylvania State University; University Park; Pennsylvania
| | - Katharine N. Suding
- Department of Environmental Science; Policy, and Management; University of California; Berkeley; California
| | - Carla M. D'Antonio
- Environmental Studies Program; University of California; Santa Barbara; Santa Barbara, California
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23
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Balch JK, Bradley BA, D'Antonio CM, Gómez-Dans J. Introduced annual grass increases regional fire activity across the arid western USA (1980-2009). Glob Chang Biol 2013; 19:173-183. [PMID: 23504729 DOI: 10.1111/gcb.12046] [Citation(s) in RCA: 209] [Impact Index Per Article: 19.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 05/11/2012] [Accepted: 07/09/2012] [Indexed: 06/01/2023]
Abstract
Non-native, invasive grasses have been linked to altered grass-fire cycles worldwide. Although a few studies have quantified resulting changes in fire activity at local scales, and many have speculated about larger scales, regional alterations to fire regimes remain poorly documented. We assessed the influence of large-scale Bromus tectorum (hereafter cheatgrass) invasion on fire size, duration, spread rate, and interannual variability in comparison to other prominent land cover classes across the Great Basin, USA. We compared regional land cover maps to burned area measured using the Moderate Resolution Imaging Spectroradiometer (MODIS) for 2000-2009 and to fire extents recorded by the USGS registry of fires from 1980 to 2009. Cheatgrass dominates at least 6% of the central Great Basin (650 000 km(2) ). MODIS records show that 13% of these cheatgrass-dominated lands burned, resulting in a fire return interval of 78 years for any given location within cheatgrass. This proportion was more than double the amount burned across all other vegetation types (range: 0.5-6% burned). During the 1990s, this difference was even more extreme, with cheatgrass burning nearly four times more frequently than any native vegetation type (16% of cheatgrass burned compared to 1-5% of native vegetation). Cheatgrass was also disproportionately represented in the largest fires, comprising 24% of the land area of the 50 largest fires recorded by MODIS during the 2000s. Furthermore, multi-date fires that burned across multiple vegetation types were significantly more likely to have started in cheatgrass. Finally, cheatgrass fires showed a strong interannual response to wet years, a trend only weakly observed in native vegetation types. These results demonstrate that cheatgrass invasion has substantially altered the regional fire regime. Although this result has been suspected by managers for decades, this study is the first to document recent cheatgrass-driven fire regimes at a regional scale.
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Affiliation(s)
- Jennifer K Balch
- Department of Geography, The Pennsylvania State University, Walker Building, University Park, PA, USA.
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24
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Sorte CJB, Ibáñez I, Blumenthal DM, Molinari NA, Miller LP, Grosholz ED, Diez JM, D'Antonio CM, Olden JD, Jones SJ, Dukes JS. Poised to prosper? A cross-system comparison of climate change effects on native and non-native species performance. Ecol Lett 2012; 16:261-70. [PMID: 23062213 DOI: 10.1111/ele.12017] [Citation(s) in RCA: 135] [Impact Index Per Article: 11.3] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 07/11/2012] [Revised: 08/14/2012] [Accepted: 09/17/2012] [Indexed: 11/26/2022]
Abstract
Climate change and biological invasions are primary threats to global biodiversity that may interact in the future. To date, the hypothesis that climate change will favour non-native species has been examined exclusively through local comparisons of single or few species. Here, we take a meta-analytical approach to broadly evaluate whether non-native species are poised to respond more positively than native species to future climatic conditions. We compiled a database of studies in aquatic and terrestrial ecosystems that reported performance measures of non-native (157 species) and co-occurring native species (204 species) under different temperature, CO(2) and precipitation conditions. Our analyses revealed that in terrestrial (primarily plant) systems, native and non-native species responded similarly to environmental changes. By contrast, in aquatic (primarily animal) systems, increases in temperature and CO(2) largely inhibited native species. There was a general trend towards stronger responses among non-native species, including enhanced positive responses to more favourable conditions and stronger negative responses to less favourable conditions. As climate change proceeds, aquatic systems may be particularly vulnerable to invasion. Across systems, there could be a higher risk of invasion at sites becoming more climatically hospitable, whereas sites shifting towards harsher conditions may become more resistant to invasions.
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Affiliation(s)
- Cascade J B Sorte
- Department of Environmental, Earth and Ocean Sciences, University of Massachusetts, Boston, MA, USA.
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25
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Abstract
Human management activities have altered the frequency and intensity of ecosystem disturbance often with enormous impacts on landscape structure and composition. One additional and under-appreciated way in which humans have altered disturbance regimes is through the introduction of invasive non-native species, themselves capable of modifying existing disturbance regimes or introducing entirely new disturbances. In many cases, modifications of disturbance regimes results in maintenance of ecosystems in a new or transitional state. There is now evidence that alteration of disturbance regime may be the most profound effect that a species or functional group can have on ecosystem structure and function.
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26
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Templer PH, Mack MC, Chapin FS, Christenson LM, Compton JE, Crook HD, Currie WS, Curtis CJ, Dail DB, D'Antonio CM, Emmett BA, Epstein HE, Goodale CL, Gundersen P, Hobbie SE, Holland K, Hooper DU, Hungate BA, Lamontagne S, Nadelhoffer KJ, Osenberg CW, Perakis SS, Schleppi P, Schimel J, Schmidt IK, Sommerkorn M, Spoelstra J, Tietema A, Wessel WW, Zak DR. Sinks for nitrogen inputs in terrestrial ecosystems: a meta-analysis of 15N tracer field studies. Ecology 2012; 93:1816-29. [PMID: 22928411 DOI: 10.1890/11-1146.1] [Citation(s) in RCA: 167] [Impact Index Per Article: 13.9] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Track Full Text] [Journal Information] [Submit a Manuscript] [Subscribe] [Scholar Register] [Indexed: 11/18/2022]
Abstract
Effects of anthropogenic nitrogen (N) deposition and the ability of terrestrial ecosystems to store carbon (C) depend in part on the amount of N retained in the system and its partitioning among plant and soil pools. We conducted a meta-analysis of studies at 48 sites across four continents that used enriched 15N isotope tracers in order to synthesize information about total ecosystem N retention (i.e., total ecosystem 15N recovery in plant and soil pools) across natural systems and N partitioning among ecosystem pools. The greatest recoveries of ecosystem 15N tracer occurred in shrublands (mean, 89.5%) and wetlands (84.8%) followed by forests (74.9%) and grasslands (51.8%). In the short term (< 1 week after 15N tracer application), total ecosystem 15N recovery was negatively correlated with fine-root and soil 15N natural abundance, and organic soil C and N concentration but was positively correlated with mean annual temperature and mineral soil C:N. In the longer term (3-18 months after 15N tracer application), total ecosystem 15N retention was negatively correlated with foliar natural-abundance 15N but was positively correlated with mineral soil C and N concentration and C:N, showing that plant and soil natural-abundance 15N and soil C:N are good indicators of total ecosystem N retention. Foliar N concentration was not significantly related to ecosystem 15N tracer recovery, suggesting that plant N status is not a good predictor of total ecosystem N retention. Because the largest ecosystem sinks for 15N tracer were below ground in forests, shrublands, and grasslands, we conclude that growth enhancement and potential for increased C storage in aboveground biomass from atmospheric N deposition is likely to be modest in these ecosystems. Total ecosystem 15N recovery decreased with N fertilization, with an apparent threshold fertilization rate of 46 kg N x ha(-1) x yr(-1) above which most ecosystems showed net losses of applied 15N tracer in response to N fertilizer addition.
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Affiliation(s)
- P H Templer
- Department of Biology, Boston University, 5 Cummington Street, Boston, Massachusetts 02215, USA.
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27
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Drenovsky RE, Grewell BJ, D'Antonio CM, Funk JL, James JJ, Molinari N, Parker IM, Richards CL. A functional trait perspective on plant invasion. Ann Bot 2012; 110:141-53. [PMID: 22589328 PMCID: PMC3380596 DOI: 10.1093/aob/mcs100] [Citation(s) in RCA: 138] [Impact Index Per Article: 11.5] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/03/2023]
Abstract
BACKGROUND AND AIMS Global environmental change will affect non-native plant invasions, with profound potential impacts on native plant populations, communities and ecosystems. In this context, we review plant functional traits, particularly those that drive invader abundance (invasiveness) and impacts, as well as the integration of these traits across multiple ecological scales, and as a basis for restoration and management. SCOPE We review the concepts and terminology surrounding functional traits and how functional traits influence processes at the individual level. We explore how phenotypic plasticity may lead to rapid evolution of novel traits facilitating invasiveness in changing environments and then 'scale up' to evaluate the relative importance of demographic traits and their links to invasion rates. We then suggest a functional trait framework for assessing per capita effects and, ultimately, impacts of invasive plants on plant communities and ecosystems. Lastly, we focus on the role of functional trait-based approaches in invasive species management and restoration in the context of rapid, global environmental change. CONCLUSIONS To understand how the abundance and impacts of invasive plants will respond to rapid environmental changes it is essential to link trait-based responses of invaders to changes in community and ecosystem properties. To do so requires a comprehensive effort that considers dynamic environmental controls and a targeted approach to understand key functional traits driving both invader abundance and impacts. If we are to predict future invasions, manage those at hand and use restoration technology to mitigate invasive species impacts, future research must focus on functional traits that promote invasiveness and invader impacts under changing conditions, and integrate major factors driving invasions from individual to ecosystem levels.
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Affiliation(s)
- Rebecca E Drenovsky
- Biology Department, John Carroll University, University Heights, OH 44118-4581, USA.
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28
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Bowman DMJS, Balch J, Artaxo P, Bond WJ, Cochrane MA, D'Antonio CM, DeFries R, Johnston FH, Keeley JE, Krawchuk MA, Kull CA, Mack M, Moritz MA, Pyne S, Roos CI, Scott AC, Sodhi NS, Swetnam TW, Whittaker R. The human dimension of fire regimes on Earth. J Biogeogr 2011; 38:2223-2236. [PMID: 22279247 PMCID: PMC3263421 DOI: 10.1111/j.1365-2699.2011.02595.x] [Citation(s) in RCA: 269] [Impact Index Per Article: 20.7] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/02/2023]
Abstract
Humans and their ancestors are unique in being a fire-making species, but 'natural' (i.e. independent of humans) fires have an ancient, geological history on Earth. Natural fires have influenced biological evolution and global biogeochemical cycles, making fire integral to the functioning of some biomes. Globally, debate rages about the impact on ecosystems of prehistoric human-set fires, with views ranging from catastrophic to negligible. Understanding of the diversity of human fire regimes on Earth in the past, present and future remains rudimentary. It remains uncertain how humans have caused a departure from 'natural' background levels that vary with climate change. Available evidence shows that modern humans can increase or decrease background levels of natural fire activity by clearing forests, promoting grazing, dispersing plants, altering ignition patterns and actively suppressing fires, thereby causing substantial ecosystem changes and loss of biodiversity. Some of these contemporary fire regimes cause substantial economic disruptions owing to the destruction of infrastructure, degradation of ecosystem services, loss of life, and smoke-related health effects. These episodic disasters help frame negative public attitudes towards landscape fires, despite the need for burning to sustain some ecosystems. Greenhouse gas-induced warming and changes in the hydrological cycle may increase the occurrence of large, severe fires, with potentially significant feedbacks to the Earth system. Improved understanding of human fire regimes demands: (1) better data on past and current human influences on fire regimes to enable global comparative analyses, (2) a greater understanding of different cultural traditions of landscape burning and their positive and negative social, economic and ecological effects, and (3) more realistic representations of anthropogenic fire in global vegetation and climate change models. We provide an historical framework to promote understanding of the development and diversification of fire regimes, covering the pre-human period, human domestication of fire, and the subsequent transition from subsistence agriculture to industrial economies. All of these phases still occur on Earth, providing opportunities for comparative research.
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Affiliation(s)
- David M J S Bowman
- School of Plant Science, Private Bag 55, University of TasmaniaHobart, Tas., Australia
| | - Jennifer Balch
- NCEAS735 State Street, Suite 300University of Santa BarbaraSanta Barbara, CA, USA
| | - Paulo Artaxo
- Instituto de Física, Universidade de São Paulo 1516Rua do Matão, Travessa R, 187, São Paulo, SP, Brazil
| | - William J Bond
- Botany Department, University of Cape TownRondebosch, South Africa
| | - Mark A Cochrane
- Geographic Information Science Center of Excellence (GIScCE) South Dakota State UniversityBrookings, SD, USA
| | - Carla M D'Antonio
- Environmental Studies Program and Department of Ecology, Evolution and Marine Biology, University of CaliforniaSanta Barbara, CA, USA
| | - Ruth DeFries
- Ecology, Evolution & Environmental Biology, Columbia UniversityNew York, NY, USA
| | - Fay H Johnston
- Menzies Research Institute, University of TasmaniaPrivate Bag 23, Hobart, Tas., Australia
| | - Jon E Keeley
- US Geological Survey, Western Ecological Research Center, Sequoia-Kings Canyon Field StationThree Rivers, CA, USA
- Department of Ecology and Evolutionary Biology, University of CaliforniaLos Angeles, CA, USA
| | - Meg A Krawchuk
- Department of Environmental Science, Policy and Management, University of CaliforniaBerkeley, CA, USA
| | - Christian A Kull
- School of Geography and Environmental Science, Monash UniversityMelbourne, Vic., Australia
| | - Michelle Mack
- Department of Biology, University of FloridaGainesville, FL, USA
| | - Max A Moritz
- Environmental Science, Policy, and Management Department, University of CaliforniaBerkeley, CA, USA
| | - Stephen Pyne
- School of Life Sciences, Arizona State UniversityTempe, AZ, USA
| | - Christopher I Roos
- Department of Anthropology, Southern Methodist UniversityDallas, TX, USA
| | - Andrew C Scott
- Department of Earth Sciences, Royal Holloway University of LondonEgham, UK
| | - Navjot S Sodhi
- Department of Biological Sciences, Faculty of Science, National University of SingaporeSingapore
| | - Thomas W Swetnam
- Laboratory of Tree-Ring Research, The University of ArizonaTucson, AZ, USA
| | - Robert Whittaker
- Laboratory of Tree-Ring Research, The University of ArizonaTucson, AZ, USA
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29
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D'Antonio CM, Hughes RF, Tunison JT. Long-term impacts of invasive grasses and subsequent fire in seasonally dry Hawaiian woodlands. Ecol Appl 2011; 21:1617-1628. [PMID: 21830706 DOI: 10.1890/10-0638.1] [Citation(s) in RCA: 23] [Impact Index Per Article: 1.8] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/31/2023]
Abstract
Invasive nonnative grasses have altered the composition of seasonally dry shrublands and woodlands throughout the world. In many areas they coexist with native woody species until fire occurs, after which they become dominant. Yet it is not clear how long their impacts persist in the absence of further fire. We evaluated the long-term impacts of grass invasions and subsequent fire in seasonally dry submontane habitats on Hawai'i, USA. We recensused transects in invaded unburned woodland and woodland that had burned in exotic grass-fueled fires in 1970 and 1987 and had last been censused in 1991. In the unburned woodlands, we found that the dominant understory grass invader, Schizachyrium condensatum, had declined by 40%, while native understory species were abundant and largely unchanged from measurements 17 years ago. In burned woodland, exotic grass cover also declined, but overall values remained high and recruitment of native species was poor. Sites that had converted to exotic grassland after a 1970 fire remained dominated by exotic grasses with no increase in native cover despite 37 years without fire. Grass-dominated sites that had burned twice also showed limited recovery despite 20 years of fire suppression. We found limited evidence for "invasional meltdown": Exotic richness remained low across burned sites, and the dominant species in 1991, Melinis minutiflora, is still dominant today. Twice-burned sites are, however, being invaded by the nitrogen-fixing tree Morella faya, an introduced species with the potential to greatly alter the successional trajectory on young volcanic soils. In summary, despite decades of fire suppression, native species show little recovery in burned Hawaiian woodlands. Thus, burned sites appear to be beyond a threshold for "natural recovery" (e.g., passive restoration).
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Affiliation(s)
- Carla M D'Antonio
- Environmental Studies Program, 4312L Bren, University of California, Santa Barbara, California 93106, USA.
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Firn J, Moore JL, MacDougall AS, Borer ET, Seabloom EW, HilleRisLambers J, Harpole WS, Cleland EE, Brown CS, Knops JMH, Prober SM, Pyke DA, Farrell KA, Bakker JD, O'Halloran LR, Adler PB, Collins SL, D'Antonio CM, Crawley MJ, Wolkovich EM, La Pierre KJ, Melbourne BA, Hautier Y, Morgan JW, Leakey ADB, Kay A, McCulley R, Davies KF, Stevens CJ, Chu CJ, Holl KD, Klein JA, Fay PA, Hagenah N, Kirkman KP, Buckley YM. Abundance of introduced species at home predicts abundance away in herbaceous communities. Ecol Lett 2011; 14:274-81. [PMID: 21281419 DOI: 10.1111/j.1461-0248.2010.01584.x] [Citation(s) in RCA: 81] [Impact Index Per Article: 6.2] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/27/2022]
Abstract
Many ecosystems worldwide are dominated by introduced plant species, leading to loss of biodiversity and ecosystem function. A common but rarely tested assumption is that these plants are more abundant in introduced vs. native communities, because ecological or evolutionary-based shifts in populations underlie invasion success. Here, data for 26 herbaceous species at 39 sites, within eight countries, revealed that species abundances were similar at native (home) and introduced (away) sites - grass species were generally abundant home and away, while forbs were low in abundance, but more abundant at home. Sites with six or more of these species had similar community abundance hierarchies, suggesting that suites of introduced species are assembling similarly on different continents. Overall, we found that substantial changes to populations are not necessarily a pre-condition for invasion success and that increases in species abundance are unusual. Instead, abundance at home predicts abundance away, a potentially useful additional criterion for biosecurity programmes.
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Affiliation(s)
- Jennifer Firn
- CSIRO Ecosystem Sciences, St. Lucia, Qld 4067, Australia.
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Bowman DMJS, Balch JK, Artaxo P, Bond WJ, Carlson JM, Cochrane MA, D'Antonio CM, Defries RS, Doyle JC, Harrison SP, Johnston FH, Keeley JE, Krawchuk MA, Kull CA, Marston JB, Moritz MA, Prentice IC, Roos CI, Scott AC, Swetnam TW, van der Werf GR, Pyne SJ. Fire in the Earth system. Science 2009; 324:481-4. [PMID: 19390038 DOI: 10.1126/science.1163886] [Citation(s) in RCA: 705] [Impact Index Per Article: 47.0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/02/2022]
Abstract
Fire is a worldwide phenomenon that appears in the geological record soon after the appearance of terrestrial plants. Fire influences global ecosystem patterns and processes, including vegetation distribution and structure, the carbon cycle, and climate. Although humans and fire have always coexisted, our capacity to manage fire remains imperfect and may become more difficult in the future as climate change alters fire regimes. This risk is difficult to assess, however, because fires are still poorly represented in global models. Here, we discuss some of the most important issues involved in developing a better understanding of the role of fire in the Earth system.
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DiVittorio CT, Corbin JD, D'Antonio CM. Spatial and temporal patterns of seed dispersal: an important determinant of grassland invasion. Ecol Appl 2007; 17:311-6. [PMID: 17489239 DOI: 10.1890/06-0610] [Citation(s) in RCA: 29] [Impact Index Per Article: 1.7] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Indexed: 05/15/2023]
Abstract
We measured spatial and temporal patterns of seed dispersal and seedling recruitment for 58 species in a grassland community to test whether seed dispersal could predict patterns of invasion after disturbance. For the 12 most abundant grasses, recruitment of native species was dependent on the propagule supply of both native and exotic species. Variability in seed rain on small spatial (1-10 m) and temporal (within season) scales led to qualitative differences in the outcome of disturbance colonization such that native species dominated disturbances when exotic seed supply was low but failed to establish when exotic seed supply was high. Local dispersal and spatial heterogeneity in species composition promoted coexistence of native and exotic species by creating refuges from high exotic seed supply within native dominated patches. Despite this, copious exotic seed production strongly limited recruitment of native species in exotic dominated patches. Most grasslands in California are presently dominated by exotic species, suggesting that competition at the seedling stage is a major barrier to native species restoration.
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Thomsen MA, D'Antonio CM, Suttle KB, Sousa WP. Ecological resistance, seed density and their interactions determine patterns of invasion in a California coastal grassland. Ecol Lett 2006; 9:160-70. [PMID: 16958881 DOI: 10.1111/j.1461-0248.2005.00857.x] [Citation(s) in RCA: 92] [Impact Index Per Article: 5.1] [Reference Citation Analysis] [What about the content of this article? (0)] [Abstract] [MESH Headings] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/30/2022]
Abstract
Relatively little experimental evidence is available regarding how ecological resistance and propagule density interact in their effects on the establishment of invasive exotic species. We examined the independent and interactive effects of neighbour cover (biotic resistance), winter vs. spring water addition (abiotic resistance) and seed density on the invasion of the European perennial grass Holcus lanatus into a California coastal grassland dominated by exotic annual grasses. We found that decreased competition from resident exotic grasses had no effect. In contrast, increased late-season water availability eroded the abiotic resistance offered by naturally dry conditions, facilitating invasion. Finally, watering treatment and seed density interacted strongly in determining seedling survival: while seedling mortality was close to 100% in ambient and winter water addition plots, survivor numbers increased with seed density in spring-watered plots. Thus, decreased abiotic resistance can amplify the effect of increased propagule density on seedling establishment, thereby increasing the likelihood of invasion.
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Thomsen MA, D'Antonio CM. Mechanisms of resistance to invasion in a California grassland: the roles of competitor identity, resource availability, and environmental gradients. OIKOS 2006. [DOI: 10.1111/j.2006.0030-1299.14929.x] [Citation(s) in RCA: 37] [Impact Index Per Article: 2.1] [Reference Citation Analysis] [What about the content of this article? (0)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/30/2022]
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Corbin JD, Thomsen MA, Dawson TE, D'Antonio CM. Summer water use by California coastal prairie grasses: fog, drought, and community composition. Oecologia 2005; 145:511-21. [PMID: 16001220 DOI: 10.1007/s00442-005-0152-y] [Citation(s) in RCA: 91] [Impact Index Per Article: 4.8] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [MESH Headings] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Received: 10/29/2004] [Accepted: 05/03/2005] [Indexed: 10/25/2022]
Abstract
Plants in the Mediterranean climate region of California typically experience summer drought conditions, but correlations between zones of frequent coastal fog inundation and certain species' distributions suggest that water inputs from fog may influence species composition in coastal habitats. We sampled the stable H and O isotope ratios of water in non-photosynthetic plant tissue from a variety of perennial grass species and soil in four sites in northern California in order to determine the proportion of water deriving from winter rains and fog during the summer. The relationship between H and O stable isotopes from our sample sites fell to the right of the local meteoric water line (LMWL) during the summer drought, providing evidence that evaporation of water from the soil had taken place prior to the uptake of water by vegetation. We developed a novel method to infer the isotope values of water before it was subjected to evaporation in which we used experimental data to calculate the slope of the deltaH versus deltaO line versus the LMWL. After accounting for evaporation, we then used a two-source mixing model to evaluate plant usage of fog water. The model indicated that 28-66% of the water taken up by plants via roots during the summer drought came from fog rather than residual soil water from winter rain. Fog use decreased as distance from the coast increased, and there were significant differences among species in the use of fog. Rather than consistent differences in fog use by species whose distributions are limited to the coast versus those with broader distributions, species responded individualistically to summer fog. We conclude that fogwater inputs can mitigate the summer drought in coastal California for many species, likely giving an advantage to species that can use it over species that cannot.
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Affiliation(s)
- Jeffrey D Corbin
- Department of Integrative Biology, University of California-Berkeley, Berkeley, CA 94720-3140, USA.
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Alexander JM, D'Antonio CM. Seed Bank Dynamics of French Broom in Coastal California Grasslands: Effects of Stand Age and Prescribed Burning on Control and Restoration. Restor Ecol 2003. [DOI: 10.1046/j.1526-100x.2003.00169.x] [Citation(s) in RCA: 37] [Impact Index Per Article: 1.8] [Reference Citation Analysis] [What about the content of this article? (0)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/20/2022]
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Abstract
Although the impacts of exotic plant invasions on community structure and ecosystem processes are well appreciated, the pathways or mechanisms that underlie these impacts are poorly understood. Better exploration of these processes is essential to understanding why exotic plants impact only certain systems, and why only some invaders have large impacts. Here, we review over 150 studies to evaluate the mechanisms underlying the impacts of exotic plant invasions on plant and animal community structure, nutrient cycling, hydrology and fire regimes. We find that, while numerous studies have examined the impacts of invasions on plant diversity and composition, less than 5% test whether these effects arise through competition, allelopathy, alteration of ecosystem variables or other processes. Nonetheless, competition was often hypothesized, and nearly all studies competing native and alien plants against each other found strong competitive effects of exotic species. In contrast to studies of the impacts on plant community structure and higher trophic levels, research examining impacts on nitrogen cycling, hydrology and fire regimes is generally highly mechanistic, often motivated by specific invader traits. We encourage future studies that link impacts on community structure to ecosystem processes, and relate the controls over invasibility to the controls over impact.
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Affiliation(s)
- Jonathan M Levine
- Department of Organismic Biology, Ecology and Evolution, 621 Charles E. Young Drive South, Box 951606, University of California, Los Angeles, CA 90095-1606, USA.
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Abstract
Many introduced plant species rely on mutualisms in their new habitats to overcome barriers to establishment and to become naturalized and, in some cases, invasive. Mutualisms involving animal-mediated pollination and seed dispersal, and symbioses between plant roots and microbiota often facilitate invasions. The spread of many alien plants, particularly woody ones, depends on pollinator mutualisms. Most alien plants are well served by generalist pollinators (insects and birds), and pollinator limitation does not appear to be a major barrier for the spread of introduced plants (special conditions relating to Ficus and orchids are described). Seeds of many of the most notorious plant invaders are dispersed by animals, mainly birds and mammals. Our review supports the view that tightly coevolved, plant-vertebrate seed dispersal systems are extremely rare. Vertebrate-dispersed plants are generally not limited reproductively by the lack of dispersers. Most mycorrhizal plants form associations with arbuscular mycorrhizal fungi which, because of their low specificity, do not seem to play a major role in facilitating or hindering plant invasions (except possibly on remote islands such as the Galapagos which are poor in arbuscular mycorrhizal fungi). The lack of symbionts has, however, been a major barrier for many ectomycorrhizal plants, notably for Pinus spp. in parts of the southern hemisphere. The roles of nitrogen-fixing associations between legumes and rhizobia and between actinorhizal plants and Frankia spp. in promoting or hindering invasions have been virtually ignored in the invasions literature. Symbionts required to induce nitrogen fixation in many plants are extremely widespread, but intentional introductions of symbionts have altered the invasibility of many, if not most, systems. Some of the world's worst invasive alien species only invaded after the introduction of symbionts. Mutualisms in the new environment sometimes re-unite the same species that form partnerships in the native range of the plant. Very often, however, different species are involved, emphasizing the diffuse nature of many (most) mutualisms. Mutualisms in new habitats usually duplicate functions or strategies that exist in the natural range of the plant. Occasionally, mutualisms forge totally novel combinations, with profound implications for the behaviour of the introduced plant in the new environment (examples are seed dispersal mutualisms involving wind-dispersed pines and cockatoos in Australia; and mycorrhizal associations involving plant roots and fungi). Many ecosystems are becoming more susceptible to invasion by introduced plants because: (a) they contain an increasing array of potential mutualistic partners (e.g. generalist frugivores and pollinators, mycorrhizal fungi with wide host ranges, rhizobia strains with infectivity across genera); and (b) conditions conductive for the establishment of various alien/alien synergisms are becoming more abundant. Incorporating perspectives on mutualisms in screening protocols will improve (but not perfect) our ability to predict whether a given plant species could invade a particular habitat.
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Affiliation(s)
- D M Richardson
- Botany Department, University of Cape Town, Rondebosch, South Africa.
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Weber E, D'Antonio CM. Germination and growth responses of hybridizing Carpobrotus species (Aizoaceae) from coastal California to soil salinity. Am J Bot 1999; 86:1257-1263. [PMID: 10487813] [Citation(s) in RCA: 0] [Impact Index Per Article: 0] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Subscribe] [Scholar Register] [Indexed: 05/23/2023]
Abstract
Germination, growth, and physiological responses of hybridizing Carpobrotus from coastal California to soil salinity were studied. Hybrids are presumably the result of hybridization and introgression between the exotic Carpobrotus edulis, a succulent perennial invading coastal habitats, and the native or long-naturalized C. chilensis. Germination responses were investigated at 0, 10, 20, and 50% seawater. Seedling growth and physiology were compared by irrigating seedlings with solutions of the same seawater concentrations and in low and high nutrients. Germination was inhibited in the presence of salt, but recovered after transferring the seeds to fresh water. Seeds exposed to salt had higher final germination rates than control. Growth of Carpobrotus was slightly enhanced by low seawater concentrations but reduced at high salinity at both nutrient regimes. Leaf cell sap osmolarity increased with increasing soil salinity, and taxa did not differ significantly in this physiological adjustment. Leaf carbon isotope ratios (∂(13)C) ranged from -28 to -22‰ and became less negative at higher salinities, indicating an improved water use efficiency in the seedlings at high salt concentrations. In addition, ∂(13)C values were generally less negative at high than at low nutrients. Differences among taxa were generally small. The results show that salinity affects both establishment and growth of hybridizing Carpobrotus. The overall weak species differences in salt tolerance indicate that the exotic C. edulis can occupy the same sites as C. chilensis in terms of salinity. The similarity of hybrids in their response to salinity suggests that they may contribute to the invasion by Carpobrotus.
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Affiliation(s)
- E Weber
- Department of Integrative Biology, University of California, Berkeley, California 94720-3140
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Ewel JJ, O'Dowd DJ, Bergelson J, Daehler CC, D'Antonio CM, Gómez LD, Gordon DR, Hobbs RJ, Holt A, Hopper KR, Hughes CE, LaHart M, Leakey RRB, Lee WG, Loope LL, Lorence DH, Louda SM, Lugo AE, McEvoy PB, Richardson DM, Vitousek PM. Deliberate Introductions of Species: Research Needs. Bioscience 1999. [DOI: 10.2307/1313438] [Citation(s) in RCA: 164] [Impact Index Per Article: 6.6] [Reference Citation Analysis] [What about the content of this article? (0)] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/10/2022] Open
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