Community Assembly Theory As a Framework for Biological Invasions
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Biogeography, Community Structure and Biological Habitat Types of Subtidal Reefs on the South Island West Coast, New Zealand
Biogeography, community structure and biological habitat types of subtidal reefs on the South Island West Coast, New Zealand SCIENCE FOR CONSERVATION 281 Biogeography, community structure and biological habitat types of subtidal reefs on the South Island West Coast, New Zealand Nick T. Shears SCIENCE FOR CONSERVATION 281 Published by Science & Technical Publishing Department of Conservation PO Box 10420, The Terrace Wellington 6143, New Zealand Cover: Shallow mixed turfing algal assemblage near Moeraki River, South Westland (2 m depth). Dominant species include Plocamium spp. (yellow-red), Echinothamnium sp. (dark brown), Lophurella hookeriana (green), and Glossophora kunthii (top right). Photo: N.T. Shears Science for Conservation is a scientific monograph series presenting research funded by New Zealand Department of Conservation (DOC). Manuscripts are internally and externally peer-reviewed; resulting publications are considered part of the formal international scientific literature. Individual copies are printed, and are also available from the departmental website in pdf form. Titles are listed in our catalogue on the website, refer www.doc.govt.nz under Publications, then Science & technical. © Copyright December 2007, New Zealand Department of Conservation ISSN 1173–2946 (hardcopy) ISSN 1177–9241 (web PDF) ISBN 978–0–478–14354–6 (hardcopy) ISBN 978–0–478–14355–3 (web PDF) This report was prepared for publication by Science & Technical Publishing; editing and layout by Lynette Clelland. Publication was approved by the Chief Scientist (Research, Development & Improvement Division), Department of Conservation, Wellington, New Zealand. In the interest of forest conservation, we support paperless electronic publishing. When printing, recycled paper is used wherever possible. CONTENTS Abstract 5 1. Introduction 6 2. -
Genetic Methods for Estimating the Effective Size of Cetacean Populations
Genetic Methods for Estimating the Effective Size of Cetacean Populations Robin S. Waples Northwest Fisheries Center, National Marine Fisheries Service, 2725 Montlake Boulevard East, Seattle, Washington 98112, USA ABSTRACT Some indirect (genetic) methods for estimating effective population size (N,) are evaluated for their suitability in studyingcetacean populations. The methodscan be grouped into those that (1) estimate current N,, (2) estimate long-term N, and (3) provide information about recent genetic bottlenecks. The methods that estimate current effective size are best suited for the analysis of small populations. and nonrandom sampling and population subdivision are probably the most serious sources of potential bias. Methods that estimate long-term N, are best suited to the analysis of large populations or entire species, may be more strongly influenced by natural selection and depend on accurate estimates of mutation or DNA base substitution rates. Precision of the estimates of N, is likely to be a limiting factor in many applications of the indirect methods. Keywords: genetics; assessment: cetaceans - general: evolution. INTRODUCTION Population size is one of the most important factors that determine the rate of various evolutionary processes, and it appears as a parameter in many of the fundamental equations of population genetics. However, knowledge merely of the total number of individuals (N) in a population is not sufficient for an accurate description of these evolutionary processes. Because of the influence of demographic parameters, two populations of the same total size may experience very different rates of genetic change. Wright (1931; 1938) developed the concept of effective population size (N,) as a way of summarising relevant demographic information so that one can predict the evolutionary consequences of finite population size (see Fig. -
Ecological Principles and Function of Natural Ecosystems by Professor Michel RICARD
Intensive Programme on Education for sustainable development in Protected Areas Amfissa, Greece, July 2014 ------------------------------------------------------------------------ Ecological principles and function of natural ecosystems By Professor Michel RICARD Summary 1. Hierarchy of living world 2. What is Ecology 3. The Biosphere - Lithosphere - Hydrosphere - Atmosphere 4. What is an ecosystem - Ecozone - Biome - Ecosystem - Ecological community - Habitat/biotope - Ecotone - Niche 5. Biological classification 6. Ecosystem processes - Radiation: heat, temperature and light - Primary production - Secondary production - Food web and trophic levels - Trophic cascade and ecology flow 7. Population ecology and population dynamics 8. Disturbance and resilience - Human impacts on resilience 9. Nutrient cycle, decomposition and mineralization - Nutrient cycle - Decomposition 10. Ecological amplitude 11. Ecology, environmental influences, biological interactions 12. Biodiversity 13. Environmental degradation - Water resources degradation - Climate change - Nutrient pollution - Eutrophication - Other examples of environmental degradation M. Ricard: Summer courses, Amfissa July 2014 1 1. Hierarchy of living world The larger objective of ecology is to understand the nature of environmental influences on individual organisms, populations, communities and ultimately at the level of the biosphere. If ecologists can achieve an understanding of these relationships, they will be well placed to contribute to the development of systems by which humans -
Community Ecology
Schueller 509: Lecture 12 Community ecology 1. The birds of Guam – e.g. of community interactions 2. What is a community? 3. What can we measure about whole communities? An ecology mystery story If birds on Guam are declining due to… • hunting, then bird populations will be larger on military land where hunting is strictly prohibited. • habitat loss, then the amount of land cleared should be negatively correlated with bird numbers. • competition with introduced black drongo birds, then….prediction? • ……. come up with a different hypothesis and matching prediction! $3 million/yr Why not profitable hunting instead? (Worked for the passenger pigeon: “It was the demographic nightmare of overkill and impaired reproduction. If you’re killing a species far faster than they can reproduce, the end is a mathematical certainty.” http://www.audubon.org/magazine/may-june- 2014/why-passenger-pigeon-went-extinct) Community-wide effects of loss of birds Schueller 509: Lecture 12 Community ecology 1. The birds of Guam – e.g. of community interactions 2. What is a community? 3. What can we measure about whole communities? What is an ecological community? Community Ecology • Collection of populations of different species that occupy a given area. What is a community? e.g. Microbial community of one human “YOUR SKIN HARBORS whole swarming civilizations. Your lips are a zoo teeming with well- fed creatures. In your mouth lives a microbiome so dense —that if you decided to name one organism every second (You’re Barbara, You’re Bob, You’re Brenda), you’d likely need fifty lifetimes to name them all. -
And Belowground Insect Herbivory Mediates Invasion Dynamics and Impact of an Exotic Plant
plants Article Release from Above- and Belowground Insect Herbivory Mediates Invasion Dynamics and Impact of an Exotic Plant Lotte Korell 1,2,3,4,* , Martin Schädler 3,4, Roland Brandl 5, Susanne Schreiter 6 and Harald Auge 3,4 1 Plant Ecology and Geobotany, Department of Ecology, University of Marburg, Karl-von-Frisch-Str. 8, 35032 Marburg, Germany 2 Institute of Biology, Martin Luther University Halle-Wittenberg, Am Kirchtor 1, 06108 Halle (Saale), Germany 3 Department of Community Ecology, Helmholtz-Centre for Environmental Research -UFZ, Theodor-Lieser-Str. 4, 06120 Halle, Germany; [email protected] (M.S.); [email protected] (H.A.) 4 German Centre for Integrative Biodiversity Research (iDiv), Halle-Jena-Leipzig, Deutscher Platz 5e, 04103 Leipzig, Germany 5 Animal Ecology, Department of Ecology, University of Marburg, Karl-von-Frisch-Str. 8, 35032 Marburg, Germany; [email protected] 6 Department of Soil System Science, Helmholtz-Centre for Environmental Research - UFZ, Theodor-Lieser-Str. 4, 06120 Halle, Germany; [email protected] * Correspondence: [email protected] Received: 28 October 2019; Accepted: 21 November 2019; Published: 26 November 2019 Abstract: The enemy-release hypothesis is one of the most popular but also most discussed hypotheses to explain invasion success. However, there is a lack of explicit, experimental tests of predictions of the enemy-release hypothesis (ERH), particularly regarding the effects of above- and belowground herbivory. Long-term studies investigating the relative effect of herbivores on invasive vs. native plant species within a community are still lacking. Here, we report on a long-term field experiment in an old-field community, invaded by Solidago canadensis s. -
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Caesar Kleberg A Publication of the Caesar Kleberg Wildlife ResearchTracks Institute CAESAR KLEBERG WILDLIFE RESEARCH INSTITUTE TEXAS A&M UNIVERSITY - KINGSVILLE 1 Caesar Kleberg Volume 5 | Issue 2 | Fall 2020 In This Issue 3 From the Director Tracks 4 Restoration: Just What Do You Mean By That? 8 The Unique Nature of Colonial-nesting Waterbirds 12 Texas Horned Lizard 8 Detectives Learn More About CKWRI The Caesar Kleberg Wildlife Research Institute at 16 Donor Spotlight: Texas A&M University-Kingsville is a Master’s and Mike Reynolds Ph.D. Program and is the leading wildlife research organization in Texas and one of the finest in the nation. Established in 1981 by a grant from the Caesar Kleberg 20 Fawn Survival and Foundation for Wildlife Conservation, its mission is Recruitment in South Texas to provide science-based information for enhancing the conservation and management of Texas wildlife. 23 Alumni Spotlight: J. Dale James Visit our Website www.ckwri.tamuk.edu Caesar Kleberg Wildlife Research Institute Texas A&M University-Kingsville 700 University Blvd., MSC 218 Kingsville, Texas 78363 4 (361) 593-3922 Follow us! Facebook: @CKWRI Twitter: @CKWRI Instagram: ckwri_official Cover Photo by iStock 2 Magazine Design and Layout by Gina Cavazos Caesar Kleberg From the Director The overarching mission of the Caesar Kleberg Wildlife Research Institute is to promote wildlife conservation. We do this primarily by conducting research and producing knowledge to benefit wildlife managers and land stewards. We also promote wildlife conservation by training the next generation of wildlife biologists Tracks through our graduate education programs. However, producing knowledge and trained professionals is not enough. -
Can More K-Selected Species Be Better Invaders?
Diversity and Distributions, (Diversity Distrib.) (2007) 13, 535–543 Blackwell Publishing Ltd BIODIVERSITY Can more K-selected species be better RESEARCH invaders? A case study of fruit flies in La Réunion Pierre-François Duyck1*, Patrice David2 and Serge Quilici1 1UMR 53 Ӷ Peuplements Végétaux et ABSTRACT Bio-agresseurs en Milieu Tropical ӷ CIRAD Invasive species are often said to be r-selected. However, invaders must sometimes Pôle de Protection des Plantes (3P), 7 chemin de l’IRAT, 97410 St Pierre, La Réunion, France, compete with related resident species. In this case invaders should present combina- 2UMR 5175, CNRS Centre d’Ecologie tions of life-history traits that give them higher competitive ability than residents, Fonctionnelle et Evolutive (CEFE), 1919 route de even at the expense of lower colonization ability. We test this prediction by compar- Mende, 34293 Montpellier Cedex, France ing life-history traits among four fruit fly species, one endemic and three successive invaders, in La Réunion Island. Recent invaders tend to produce fewer, but larger, juveniles, delay the onset but increase the duration of reproduction, survive longer, and senesce more slowly than earlier ones. These traits are associated with higher ranks in a competitive hierarchy established in a previous study. However, the endemic species, now nearly extinct in the island, is inferior to the other three with respect to both competition and colonization traits, violating the trade-off assumption. Our results overall suggest that the key traits for invasion in this system were those that *Correspondence: Pierre-François Duyck, favoured competition rather than colonization. CIRAD 3P, 7, chemin de l’IRAT, 97410, Keywords St Pierre, La Réunion Island, France. -
National Wildlife Federation's Community Wildlife Habitat
National Wildlife Federation’s Community Wildlife Habitat Certification Requirements To achieve certification through the National Wildlife Federation’s Community Wildlife Habitat program, you must create or restore wildlife habitat in your community and do education and outreach. First, a certain number of homes, schools and common areas must become National Wildlife Federation Certified Wildlife Habitats by providing the four basic elements that all wildlife need: food, water, cover and places to raise young. The NWF Certified Wildlife Habitat program also requires sustainable gardening practices such as using rain barrels, reducing water usage, removing invasive plants, using native plants and eliminating pesticides. These requirements are based on population – see chart below. Second, communities earn education and outreach points through a flexible checklist that includes educating citizens at community events, hosting a native plant sale, organizing a stream clean up, bringing new partners to the effort and hosting workshops – see pages 2 and 3. Property Certification Requirements: Minimum Habitat Sliding Scale Based on Activity / Type of Certification Points Certification Points Population Size For each home certified, including townhomes and apartments 1 20 500 or Less For each common area certified, including public parks, HOA common 40 501-1,000 areas, businesses, places of worship, farms, universities and municipal 3 100 1,001-5000 buildings 150 5,001-10,000 For each school certified as an NWF Schoolyard Habitat - Pre-K - 12 or 175 10,001-15,000 5 nature center 200 15,001-20,000 225 20,001-25,000 250 25,001-50,000 VERIFICATION: Each home or common area must be certified within 15 300 50,001-100,000 years of a community's registration date to count for points. -
Shell Crushing Resistance of Alien and Native Thiarid Gastropods to Predatory Crabs in South Africa
Aquatic Invasions (2016) Volume 11, Issue 3: 303–311 DOI: http://dx.doi.org/10.3391/ai.2016.11.3.08 Open Access © 2016 The Author(s). Journal compilation © 2016 REABIC Research Article Shell crushing resistance of alien and native thiarid gastropods to predatory crabs in South Africa 1, 2 1 1 1 Nelson A.F. Miranda *, G. John Measey , Nasreen Peer , Jacqueline L. Raw , Renzo Perissinotto 3 and Christopher C. Appleton 1DST/NRF Research Chair in Shallow Water Ecosystems, Nelson Mandela Metropolitan University, Port Elizabeth 6031, South Africa 2Centre for Invasion Biology, Department of Botany & Zoology, Stellenbosch University, Stellenbosch, South Africa 3School of Life Sciences, Westville Campus, University of KwaZulu-Natal, Durban, South Africa *Corresponding author E-mail: [email protected] Received: 22 September 2015 / Accepted: 10 March 2016 / Published online: 11 April 2016 Handling editor: Kenneth Hayes Abstract The successful invasion of freshwater and coastal lakes of South Africa by the recently introduced thiarid snail Tarebia granifera may be due in part to release from predatory pressure. This study aimed to determine the comparative vulnerability of T. granifera and the widespread native aquatic thiarid Melanoides tuberculata to predation. These species also account for many thiarid invasions in the Americas, Europe and parts of Africa. We quantified the shell crushing resistance of these snails, as well as the maximal shell crushing capability of native freshwater crab predators, Potamonautes sidneyi and P. perlatus. Using an Instron isometric transducer, we showed that Tarebia granifera shells were significantly stronger than Melanoides shells, and exceeded the crushing strength we documented for both potential predatory crabs. -
History of Insular Ecology and Biogeography - Harold Heatwole
OCEANS AND AQUATIC ECOSYSTEMS- Vol. II - History of Insular Ecology and Biogeography - Harold Heatwole HISTORY OF INSULAR ECOLOGY AND BIOGEOGRAPHY Harold Heatwole North Carolina State University, Raleigh, North Carolina, USA Keywords: islands; insular dynamics; One Tree Island; Aristotle; Darwin; Wallace; equilibrium theory; biogeography; immigration; extinction; species-turnover; stochasticism; determinism; null hypotheses; trophic structure; transfer organisms; assembly rules; energetics. Contents 1. Ancient and Medieval Concepts: the Birth of Insular Biogeography 2. Darwin and Wallace: the Dawn of the Modern Era 3. Genetics and Insular Biogeography 4. MacArthur and Wilson: the Equilibrium Theory of Insular Biogeography 5. Documenting and Testing the Equilibrium Theory 6. Modifying the Equilibrium Theory 7. Determinism versus Stochasticism in Insular Communities 8. Insular Energetics and Trophic Structure Stability Glossary Bibliography Biographical Sketch Summary In ancient times, belief in spontaneous generation and divine creation dominated thinking about insular biotas. Weaknesses in these theories let to questioning of those ideas, first by clergy and later by scientists, culminating in Darwin's and Wallace's postulation of evolution through natural selection. MacArthur and Wilson presented a dynamic equilibrium model of insular ecology and biogeography that represented the number of species on an island as an equilibrium between immigration and extinction rates, as influenced by insular sizes and distances from mainlands. This model has been tested and found generally true but requiring minor modifications, such as accounting for disturbancesUNESCO affecting the equilibrium nu–mber. EOLSS There has been basic controversy as to whether insular biotas reflect deterministic or stochastic processes. It is likely that neither extreme SAMPLEis completely correct but rather CHAPTERS the two kinds of processes interact. -
Integrating Community and Ecosystem-Based Approaches in Climate
Integrating Community and Ecosystem-Based Approaches in Climate Change Adaptation i Responses This paper is the result of extensive discussions led by adaptation professionals coming from different backgrounds and facilitated by the Ecosystem and Livelihoods Adaptation Network (ELAN).ii ELAN is an innovative alliance between two conservation organisations (International Union for the Conservation of Nature [IUCN] and WWF) and two development organisations (CARE International and the International Institute for Environment and Development [IIED]). The objective of ELAN is to establish a global network to develop, evaluate, synthesize and share successful strategies for adapting to climate change, build capacity for such strategies to be assessed and implemented at national and sub-national levels, and advance policies and knowledge sharing platforms that will facilitate the scaling up of effective strategies. Two emerging approaches to adaptation have gained currency over the past few years, namely Community-based Adaptation (CBA) and Ecosystem-based Adaptation (EBA). Each has its specific emphasis, the first on empowering local communities to reduce their vulnerabilities, and the latter on harnessing the management of ecosystems as a means to provide goods and services in the face of climate change. In this paper, ELAN argues for a more truly “integrated approach” to adaptation that addresses and seeks to reconcile differences between CBA and EBA. ELAN has developed a conceptual framework for an approach to adaptation, which empowers -
Chapter 11A Structuring Herbivore Communities
CHAPTER 11A STRUCTURING HERBIVORE COMMUNITIES The role of habitat and diet SIPKE E. VAN WIEREN AND FRANK VAN LANGEVELDE Resource Ecology Group, Wageningen University, P.O. Box 47, 6700 AA Wageningen, The Netherlands E-mail: [email protected] Abstract. This chapter tries to address the question “Why are there so many species?” with a focus on the diversity of herbivore species. We review several mechanisms of resource specialisation between herbivore species that allow coexistence, ranging from diet specialisation, habitat selection to spatial heterogeneity in resources. We use the ungulate community in Kruger National Park to illustrate approaches in niche differentiation. The habitat overlap of the ungulate species is analysed, continued with the overlap in diet and the spatial heterogeneity in resources. This focus on the constraints on species’ exclusive resources is a useful tool for understanding how competitive interactions structure communities and limit species diversity. In explaining community structure of mobile animals, we argue that the existence of exclusive resources governed by spatial heterogeneity plays an important role. Trade- offs between food availability and quality, food availability and predation risk, or food and abiotic conditions (different habitat types) may constrain competitive interactions among mobile animals and allow the existence of exclusive resources. We propose that body mass of the animals considered is crucial here as animals with different body mass use different resources and perceive spatial heterogeneity in resources differently. A functional explanation of the role of body mass in the structuring of communities is still lacking while the study of how much dissimilarity is minimally needed to permit coexistence between strongly overlapping species is still in its infancy.