Creating Chains and Webs to Model Ecological Relationships
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Effects of Interactions Between the Green and Brown Food Webs on Ecosystem Functioning Kejun Zou
Effects of interactions between the green and brown food webs on ecosystem functioning Kejun Zou To cite this version: Kejun Zou. Effects of interactions between the green and brown food webs on ecosystem functioning. Ecosystems. Université Pierre et Marie Curie - Paris VI, 2016. English. NNT : 2016PA066266. tel-01445570 HAL Id: tel-01445570 https://tel.archives-ouvertes.fr/tel-01445570 Submitted on 1 Jun 2017 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Université Pierre et Marie Curie Ecole doctorale : 227 Science de la Nature et de l’Homme Laboratoire : Institut d’Ecologie et des Sciences de l’Environnement de Paris Effects of interactions between the green and brown food webs on ecosystem functioning Effets des interactions entre les réseaux vert et brun sur le fonctionnement des ecosystèmes Par Kejun ZOU Thèse de doctorat d’Ecologie Dirigée par Dr. Sébastien BAROT et Dr. Elisa THEBAULT Présentée et soutenue publiquement le 26 septembre 2016 Devant un jury composé de : M. Sebastian Diehl Rapporteur M. José Montoya Rapporteur Mme. Emmanuelle Porcher Examinatrice M. Eric Edeline Examinateur M. Simon Bousocq Examinateur M. Sébastien Barot Directeur de thèse Mme. Elisa Thébault Directrice de thèse 2 Acknowledgements At the end of my thesis I would like to thank all those people who made this thesis possible and an unforgettable experience for me. -
Effects of Human Disturbance on Terrestrial Apex Predators
diversity Review Effects of Human Disturbance on Terrestrial Apex Predators Andrés Ordiz 1,2,* , Malin Aronsson 1,3, Jens Persson 1 , Ole-Gunnar Støen 4, Jon E. Swenson 2 and Jonas Kindberg 4,5 1 Grimsö Wildlife Research Station, Department of Ecology, Swedish University of Agricultural Sciences, SE-730 91 Riddarhyttan, Sweden; [email protected] (M.A.); [email protected] (J.P.) 2 Faculty of Environmental Sciences and Natural Resource Management, Norwegian University of Life Sciences, Postbox 5003, NO-1432 Ås, Norway; [email protected] 3 Department of Zoology, Stockholm University, SE-10691 Stockholm, Sweden 4 Norwegian Institute for Nature Research, NO-7485 Trondheim, Norway; [email protected] (O.-G.S.); [email protected] (J.K.) 5 Department of Wildlife, Fish, and Environmental Studies, Swedish University of Agricultural Sciences, SE-901 83 Umeå, Sweden * Correspondence: [email protected] Abstract: The effects of human disturbance spread over virtually all ecosystems and ecological communities on Earth. In this review, we focus on the effects of human disturbance on terrestrial apex predators. We summarize their ecological role in nature and how they respond to different sources of human disturbance. Apex predators control their prey and smaller predators numerically and via behavioral changes to avoid predation risk, which in turn can affect lower trophic levels. Crucially, reducing population numbers and triggering behavioral responses are also the effects that human disturbance causes to apex predators, which may in turn influence their ecological role. Some populations continue to be at the brink of extinction, but others are partially recovering former ranges, via natural recolonization and through reintroductions. -
Trophic Levels
Trophic Levels Douglas Wilkin, Ph.D. Jean Brainard, Ph.D. Say Thanks to the Authors Click http://www.ck12.org/saythanks (No sign in required) AUTHORS Douglas Wilkin, Ph.D. To access a customizable version of this book, as well as other Jean Brainard, Ph.D. interactive content, visit www.ck12.org CK-12 Foundation is a non-profit organization with a mission to reduce the cost of textbook materials for the K-12 market both in the U.S. and worldwide. Using an open-content, web-based collaborative model termed the FlexBook®, CK-12 intends to pioneer the generation and distribution of high-quality educational content that will serve both as core text as well as provide an adaptive environment for learning, powered through the FlexBook Platform®. Copyright © 2015 CK-12 Foundation, www.ck12.org The names “CK-12” and “CK12” and associated logos and the terms “FlexBook®” and “FlexBook Platform®” (collectively “CK-12 Marks”) are trademarks and service marks of CK-12 Foundation and are protected by federal, state, and international laws. Any form of reproduction of this book in any format or medium, in whole or in sections must include the referral attribution link http://www.ck12.org/saythanks (placed in a visible location) in addition to the following terms. Except as otherwise noted, all CK-12 Content (including CK-12 Curriculum Material) is made available to Users in accordance with the Creative Commons Attribution-Non-Commercial 3.0 Unported (CC BY-NC 3.0) License (http://creativecommons.org/ licenses/by-nc/3.0/), as amended and updated by Creative Com- mons from time to time (the “CC License”), which is incorporated herein by this reference. -
Food Chains in Woodland Habitats. All Animals Need to Eat Food to Survive
Science Lesson Living Things and their Habitats- Food chains in woodland habitats. Key Learning • A food chain shows the links between different living things and where they get their energy from. • Living things can be classified as producers or consumers according to their place in the food chain. • A predator is an animal that feeds on other animals (its prey). • Animals can be described as carnivores, herbivores or omnivores. All animals need to eat food to survive. • Talk about what you already know about the kind of food different animals eat. • What is the name of an animal that only eats plants? • What is the name of an animal that only eats other animals? • What is the name of an animal that eats both plants and other animals? Watch this clip about birds. What kind of food do they eat? https://www.bbc.co.uk/bitesize/clips/z9nhfg8 Animals can be described as herbivores, carnivores or omnivores. Birds like robins, blue tits and house sparrows have a very varied diet! worms spiders slugs flies mealworms berries Robins, blue tits and house sparrows are omnivores because they eat plants and other animals. Describing a food chain. Watch this clip describing a food chain. https://www.bbc.co.uk/bitesize/clips/zjshfg8 Caterpillar cat magpie Think about these questions as you watch • Where does a food chain start? • Which animals are herbivores? • Which animals are carnivores? A food chain starts with energy from the Sun because plants need the Sun’s light energy to make their own food in their leaves. Plants are eaten by animals. -
Ecology (Pyramids, Biomagnification, & Succession
ENERGY PYRAMIDS & Freshmen Biology FOOD CHAINS/FOOD WEBS May 4 – May 8 Lecture ENERGY FLOW •Energy → powers life’s processes •Energy = ATP! •Flow of energy determines the system’s ability to sustain life FEEDING RELATIONSHIPS • Energy flows through an ecosystem in one direction • Sun → autotrophs (producers) → heterotrophs (consumers) FOOD CHAIN VS. FOOD WEB FOOD CHAINS • Energy stored by producers → passed through an ecosystem by a food chain • Food chain = series of steps in which organisms transfer energy by eating and being eaten FOOD WEBS •Feeding relationships are more complex than can be shown in a food chain •Food Web = network of complex interactions •Food webs link all the food chains in an ecosystem together ECOLOGICAL PYRAMIDS • Used to show the relationships in Ecosystems • There are different types: • Energy Pyramid • Biomass Pyramid • Pyramid of numbers ENERGY PYRAMID • Only part of the energy that is stored in one trophic level can be passed on to the next level • Much of the energy that is consumed is used for the basic functions of life (breathing, moving, reproducing) • Only 10% is used to produce more biomass (10 % moves on) • This is what can be obtained from the next trophic level • All of the other energy is lost 10% RULE • Only 10% of energy (from organisms) at one trophic level → the next level • EX: only 10% of energy/calories from grasses is available to cows • WHY? • Energy used for bodily processes (growth/development and repair) • Energy given off as heat • Energy used for daily functioning/movement • Only 10% of energy you take in should be going to your actual biomass/weight which another organism could eat BIOMASS PYRAMID • Total amount of living tissue within a given trophic level = biomass • Represents the amount of potential food available for each trophic level in an ecosystem PYRAMID OF NUMBERS •Based on the number of individuals at each trophic level. -
Plants Are Producers! Draw the Different Producers Below
Name: ______________________________ The Unique Producer Every food chain begins with a producer. Plants are producers. They make their own food, which creates energy for them to grow, reproduce and survive. Being able to make their own food makes them unique; they are the only living things on Earth that can make their own source of food energy. Of course, they require sun, water and air to thrive. Given these three essential ingredients, you will have a healthy plant to begin the food chain. All plants are producers! Draw the different producers below. Apple Tree Rose Bushes Watermelon Grasses Plant Blueberry Flower Fern Daisy Bush List the three essential needs that every producer must have in order to live. © 2009 by Heather Motley Name: ______________________________ Producers can make their own food and energy, but consumers are different. Living things that have to hunt, gather and eat their food are called consumers. Consumers have to eat to gain energy or they will die. There are four types of consumers: omnivores, carnivores, herbivores and decomposers. Herbivores are living things that only eat plants to get the food and energy they need. Animals like whales, elephants, cows, pigs, rabbits, and horses are herbivores. Carnivores are living things that only eat meat. Animals like owls, tigers, sharks and cougars are carnivores. You would not catch a plant in these animals’ mouths. Then, we have the omnivores. Omnivores will eat both plants and animals to get energy. Whichever food source is abundant or available is what they will eat. Animals like the brown bear, dogs, turtles, raccoons and even some people are omnivores. -
Restoration of Heterogeneous Disturbance Regimes for the Preservation of Endangered Species Steven D
RESEARCH ARTICLE Restoration of Heterogeneous Disturbance Regimes for the Preservation of Endangered Species Steven D. Warren and Reiner Büttner ABSTRACT Disturbance is a natural component of ecosystems. All species, including threatened and endangered species, evolved in the presence of, and are adapted to natural disturbance regimes that vary in the kind, frequency, severity, and duration of disturbance. We investigated the relationship between the level of visible soil disturbance and the density of four endan- gered plant species on U.S. Army training lands in the German state of Bavaria. Two species, gray hairgrass (Corynephorus canescens) and mudwort (Limosella aquatica), showed marked affinity for or dependency on high levels of recent soil disturbance. The density of fringed gentian (Gentianella ciliata) and shepherd’s cress (Teesdalia nudicaulis) declined with recent disturbance, but appeared to favor older disturbance which could not be quantified by the methods employed in this study. The study illustrates the need to restore and maintain disturbance regimes that are heterogeneous in terms of the intensity of and time since disturbance. Such a restoration strategy has the potential to favor plant species along the entire spectrum of ecological succession, thereby maximizing plant biodiversity and ecosystem stability. Keywords: fringed gentian, gray hairgrass, heterogeneous disturbance hypothesis, mudwort, shepherd’s cress cosystems and the species that create and maintain conditions neces- When the European Commission Einhabit them typically evolve in sary for survival. issued Directive 92/43/EEC (Euro- the presence of quasi-stable distur- The grasslands of northern Europe pean Economic Community 1992) bance regimes which are characterized lie within what would be mostly forest requiring all European Union nations by general patterns of perturbation, in the absence of disturbance. -
Disturbance Processes and Ecosystem Management
Vegetation Management and Protection Research DISTURBANCE PROCESSES AND ECOSYSTEM MANAGEMENT The paper was chartered by the Directors of Forest Fire and Atmospheric Sciences Research, Fire and Aviation Management, Forest Pest Management, and Forest Insect and Disease Research in response to an action item identified in the National Action Plan for Implementing Ecosystem Management (February 24, 1994). The authors are: Robert D. Averill, Group Leader, Forest Health Management, Renewable Resources, USDA Forest Service Region 2, 740 Sims St., Lakewood, CO 80225 Louise Larson, Forest Fuels Management Specialist, USDA Forest Service Sierra National Forest, 1600 Tollhouse Road, Clovis, CA 93612 Jim Saveland, Fire Ecologist, USDA Forest Service Forest Fire & Atmospheric Sciences Research P.O. Box 96090, Washington, DC 20090 Philip Wargo, Principal Plant Pathologist, USDA Forest Service Northeastern Center for Forest Health Research, 51 Mill Pond Road, Hamden, CT 06514 Jerry Williams, Assistant Director, Fire Operations, USDA Forest Service Fire & Aviation Management Staff, P.O. Box 96090, Washington, DC 20090 Melvin Bellinger, retired, made significant contributions. Abstract This paper is intended to broaden awareness and help develop consensus among USDA Forest Service scientists and resource managers about the role and significance of disturbance in ecosystem dynamics and, hence, resource management. To have an effective ecosystem management policy, resource managers and the public must understand the nature of ecological resiliency and stability and the role of natural disturbance on sustainability. Disturbances are common and important in virtually all ecosystems. Executive Summary "Ecosystems are not defined so much by the objects they contain as by the processes that regulate them" -- Christensen and others 1989 Awareness and understanding of disturbance ecology and the role disturbance plays in ecosystem dynamics, and the ability to communicate that information, is essential in understanding ecosystem potentials and the consequences of management choices. -
1 Changing Disturbance Regimes, Ecological Memory, and Forest Resilience 2 3 4 Authors: Jill F
1 Changing disturbance regimes, ecological memory, and forest resilience 2 3 4 Authors: Jill F. Johnstone1*§, Craig D. Allen2, Jerry F. Franklin3, Lee E. Frelich4, Brian J. 5 Harvey5, Philip E. Higuera6, Michelle C. Mack7, Ross K. Meentemeyer8, Margaret R. Metz9, 6 George L. W. Perry10, Tania Schoennagel11, and Monica G. Turner12§ 7 8 Affiliations: 9 1. Department of Biology, University of Saskatchewan, Saskatoon, SK S7N 5E2 Canada 10 2. U.S. Geological Survey, Fort Collins Science Center, Jemez Mountains Field Station, Los 11 Alamos, NM 87544 USA 12 3. College of Forest Resources, University of Washington, Seattle, WA 98195 USA 13 4. Department of Forest Resources, University of Minnesota, St. Paul, MN 55108 USA 14 5. Department of Geography, University of Colorado-Boulder, Boulder, CO 80309 USA 15 6. Department of Ecosystem and Conservation Sciences, University of Montana, Missoula, MT 16 59812 USA 17 7. Center for Ecosystem Science and Society and Department of Biology, Northern Arizona 18 University, Flagstaff, AZ 86011 USA 19 8. Department of Forestry & Environmental Resources, North Carolina State University, 20 Raleigh, NC 27695 USA 21 9. Department of Biology, Lewis and Clark College, Portland, OR 97219 USA 22 10. School of Environment, University of Auckland, Private Bag 92019, Auckland, New Zealand 23 11. Department of Geography and INSTAAR, University of Colorado-Boulder, Boulder, CO 24 80309 USA 25 12. Department of Zoology, University of Wisconsin-Madison, Madison, WI 53717 26 27 * corresponding author: [email protected]; 28 § co-leaders of this manuscript 29 30 Running title: Changing disturbance and forest resilience 31 1 32 33 Abstract 34 Ecological memory is central to ecosystem response to disturbance. -
Disturbance Versus Restoration
Disturbance and Restoration of Streams P. S. Lake Prelude “One of the penalties of an ecological education is that one lives alone in a world of wounds. Much of the damage inflicted on land is quite invisible to laymen.” Aldo Leopold “Round River. From the Journals of Aldo Leopold” ed., L. B. Leopold. Oxford U.P. 1953. Read: 1963. Lake George Mining Co., 1952, Captains Flat, N.S.W. Molonglo River. Heavy metals (Z+Cu) + AMD. Black (Lake 1963) clear (Norris 1985) ---Sloane & Norris (2002) Aberfoyle Tin NL, 1982. Rossarden, Tasmania. Tin and Tungsten (W). Cd, Zn. South Esk River, 1974 Lake Pedder, south west Tasmania. • Pristine, remote lake with a remarkable, glacial sand beach, endemic fish (Galaxias pedderensis) and ~5 spp., of invertebrates. • Flooded by two dams to produce hydro-electricity in 1973 • Sampled annually for 21 years. • Initial “trophic upsurge” then a steady decline to paucity. Ecological Disturbance • Interest triggered by Connell J.H (1978) Intermediate Disturbance Hypothesis • Disturbances are forces with the potential capability to disrupt populations, communities and ecosystems. Defined by their type, strength, duration and spatial extent---not by their impacts. • Pulse, Press (Bender et al., 1984) and Ramp disturbances (Lake 2000) and responses. Disturbances within Disturbances • Distinct disturbances nested within enveloping disturbances. – Droughts—ramps of water loss, high temperatures, low water quality, loss of connectivity etc. – Climate change with ramps (sea level rise, temperature increase, acidification). Compound Disturbances • Natural e.g. drought and fire – Effect on streams: recovery from catchment-riparian fire impact exacerbated by drought cf., fire alone. (Verkaik et al., 2015). – Sites: Idaho, Catalonia, Victoria, Australia. -
Detrital Food Chain As a Possible Mechanism to Support the Trophic Structure of the Planktonic Community in the Photic Zone of a Tropical Reservoir
Limnetica, 39(1): 511-524 (2020). DOI: 10.23818/limn.39.33 © Asociación Ibérica de Limnología, Madrid. Spain. ISSN: 0213-8409 Detrital food chain as a possible mechanism to support the trophic structure of the planktonic community in the photic zone of a tropical reservoir Edison Andrés Parra-García1,*, Nicole Rivera-Parra2, Antonio Picazo3 and Antonio Camacho3 1 Grupo de Investigación en Limnología Básica y Experimental y Biología y Taxonomía Marina, Instituto de Biología, Universidad de Antioquia. 050010 Medellín, Colombia. 2 Grupo de Fundamentos y Enseñanza de la Física y los Sistemas Dinámicos, Instituto de Física, Universidad de Antioquia. 050010 Medellín, Colombia. 3 Instituto Cavanilles de Biodiversidad y Biología Evolutiva. Universidad de Valencia. E–46980 Paterna, Valencia. España. * Corresponding author: [email protected] Received: 31/10/18 Accepted: 10/10/19 ABSTRACT Detrital food chain as a possible mechanism to support the trophic structure of the planktonic community in the photic zone of a tropical reservoir In the photic zone of aquatic ecosystems, where different communities coexist showing different strategies to access one or different resources, the biomass spectra can describe the food transfers and their efficiencies. The purpose of this work is to describe the biomass spectrum and the transfer efficiency, from the primary producers to the top predators of the trophic network, in the photic zone of the Riogrande II reservoir. Data used in the model of the biomass spectrum were taken from several studies carried out between 2010 and 2013 in the reservoir. The analysis of the slope of a biomass spectrum, of the transfer efficiencies, and the omnivory indexes, suggest that most primary production in the photic zone of the Riogrande II reservoir is not directly used by primary consumers, and it appears that detritic mass flows are an indirect way of channeling this production towards zooplankton. -
The Effects of Disturbance and Succession on Wildlife Habitat And
This file was created by scanning the printed publication. Errors identified by the software have been corrected; however, some errors may remain. 11 The Effects of Disturbance K EVIN S. McKELVEY and Succession on Wildlife Habitat and Animal Communities his chapter discusses the study of disturbance and al l affect both the postdisturbance wildlife community Tsuccession as they relate to wildlife. As such, the and, more importantly, the trajectory of the postdistur discussion is confined to those disturbance processes bance community. Even for well-studied species, co that change the physical attributes of habitat, leading herent understandings of their relationships to distur to a postdisturbance trajectory. However, even with bance across time and space are therefore often vague. this narrowing of the scope of disturbances discussed, Commonly, we look at successional changes in habi there remain formidable obstacles prior to any co tat quality by using spatial samples of different ages as if herent discussion of disturbance. The first, and most they were a temporal series, which implies spatiotem fundamental, is definitional: what constitutes distur poral constancy in successional dynamics. This assump bance and succession, and what is habitat? The con tion has served wildlife research well, but in the face of cepts of disturbance, habitat, and succession are highly directional climate change and the nearly continuous scale-dependent; disturbances at one scale become addition of exotic species, this approach is becoming part of continuous processes at a larger scale, and ideas increasingly untenable. We need to embrace the idea associated with succession require assumptions of con that postdisturbance succession is increasingly unlikely stancy, which become highly problematic as spatiotem to produce communities similar to those that the dis poral scales increase.