Ecological Disturbances and Succession
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
Land-Use, Land-Cover Changes and Biodiversity Loss - Helena Freitas
LAND USE, LAND COVER AND SOIL SCIENCES – Vol. I - Land-Use, Land-Cover Changes and Biodiversity Loss - Helena Freitas LAND-USE, LAND-COVER CHANGES AND BIODIVERSITY LOSS Helena Freitas University of Coimbra, Portugal Keywords: land use; habitat fragmentation; biodiversity loss Contents 1. Introduction 2. Primary Causes of Biodiversity Loss 2.1. Habitat Degradation and Destruction 2.2. Habitat Fragmentation 2.3. Global Climate Change 3. Strategies for Biodiversity Conservation 3.1. General 3.2. The European Biodiversity Conservation Strategy 4. Conclusions Glossary Bibliography Biographical Sketch Summary During Earth's history, species extinction has probably been caused by modifications of the physical environment after impacts such as meteorites or volcanic activity. On the contrary, the actual extinction of species is mainly a result of human activities, namely any form of land use that causes the conversion of vast areas to settlement, agriculture, and forestry, resulting in habitat destruction, degradation, and fragmentation, which are among the most important causes of species decline and extinction. The loss of biodiversity is unique among the major anthropogenic changes because it is irreversible. The importance of preserving biodiversity has increased in recent times. The global recognition of the alarming loss of biodiversity and the acceptance of its value resultedUNESCO in the Convention on Biologi – calEOLSS Diversity. In addition, in Europe, the challenge is also the implementation of the European strategy for biodiversity conservation and agricultural policies, though it is increasingly recognized that the strategy is limitedSAMPLE by a lack of basic ecological CHAPTERS information and indicators available to decision makers and end users. We have reached a point where we can save biodiversity only by saving the biosphere. -
Energy Development's Impacts on the Wildlife, Landscapes, And
Losing Ground: Energy Development’s Impacts on the Wildlife, Landscapes, and Hunting Traditions of the American West A Report by the National Wildlife Federation and the Natural Resources Defense Council Barbara Wheeler he iconic game species of the American wildlife are an ecological marker for the health of non- West are in perilous decline, as migratory game species, which are also becoming increasingly T animals lose ground to energy development vulnerable to the effects of energy development. and habitat destruction in southeast Montana and northeast Wyoming. Sage-grouse, mule deer, and Bountiful wildlife populations are a major part of the pronghorn are facing decreasing herd sizes and cultures and economies of Montana and Wyoming. downward long-term population trends, which Deteriorations in habitat quality associated with threaten the continued viability of these species in energy development can negatively affect wildlife the coming decades. Of the species considered, only populations and, in turn, impact hunters, wildlife- elk populations are forecast to rebound and stabilize watchers, and the tourism industry as a whole, which brings millions of people and billions of dollars to that additional habitat loss or degradation from the region every year. These impacts justify the need from historic lows, though there is significant concern energy development could stall population growth and for land management reforms and for wide-scale further displace the species. Simultaneously, big game investments in game and non-game wildlife protection Losing Ground Jack Dempsey at state and federal levels to offset the increasing impact on wildlife from energy development. Oregon Department of Fish and Wildlife A study commissioned by the National Wildlife Federation and the Natural Resources Defense A study commissioned by the Council analyzes trends in population and hunting National Wildlife Federation and opportunities for mule deer, pronghorn, elk, and the Natural Resources Defense greater sage-grouse. -
Intermediate Disturbance Hypothesis
TIEE Teaching Issues and Experiments in Ecology - Volume 1, January 2004 ISSUES – FIGURE SET Ecology of Disturbance Charlene D'Avanzo, School of Natural Sciences Hampshire College, Amherst, MA, 01002 [email protected] Controlled fire, © Konza Prairie LTER, Manhattan, KS {www.konza.ksu.edu/ gallery/hulbert.jpg} Figure Set 1: Intermediate Disturbance Hypothesis Purpose: To illustrate the intermediate disturbance hypothesis with 2 field experiments. Teaching Approach: "Pairs Share" Cognitive Skills: (see Bloom's Taxonomy) — comprehension, interpretation, application, analysis Student Assessment: Take home or in class essay quiz © 2004 – Charlene D’Avanzo and the Ecological Society of America. Teaching Issues and Experiments in Ecology, TIEE Volume 1 © 2004 - Ecological Society of America (www.tiee.ecoed.net). page 2 Charlene D’Avanzo TIEE Volume 1, January 2004 BACKGROUND W. Sousa (1979) In this study, Wayne Sousa tested the intermediate disturbance hypothesis proposed by Connell (1978). In the 70's and 80's ecologists hotly debated factors explaining high diversity in tropical regions and bottom of the deep sea. Popular ideas included: the time hypothesis (older communities are more diverse), the competition hypothesis (in agreeable climates where biological and not physical factors prevail, interspecific competition and niche partitioning results in high diversity), and the environmental stability hypothesis (relatively unchanging physical variables allow more species to exist). Connell questioned all of these and reasoned instead that highest species diversity exists under conditions of intermediate disturbance. He proposed that in recently disturbed communities a few early colonizing species prevail; similarly after a long time diversity is also low, but these few are long-living and competitively dominant organisms. -
7. Shrubland and Young Forest Habitat Management
7. SHRUBLAND AND YOUNG FOREST HABITAT MANAGEMENT hrublands” and “Young Forest” are terms that apply to areas Shrubland habitat and that are transitioning to mature forest and are dominated by young forest differ in “Sseedlings, saplings, and shrubs with interspersed grasses and forbs (herbaceous plants). While some sites such as wetlands, sandy sites vegetation types and and ledge areas can support a relatively stable shrub cover, most shrub communities in the northeast are successional and change rapidly to food and cover they mature forest if left unmanaged. Shrub and young forest habitats in Vermont provide important habitat provide, as well as functions for a variety of wildlife including shrubland birds, butterflies and bees, black bear, deer, moose, snowshoe hare, bobcat, as well as a where and how they variety of reptiles and amphibians. Many shrubland species are in decline due to loss of habitat. Shrubland bird species in Vermont include common are maintained on the species such as chestnut-sided warbler, white-throated sparrow, ruffed grouse, Eastern towhee, American woodcock, brown thrasher, Nashville landscape. warbler, and rarer species such as prairie warbler and golden-winged warbler. These habitat types are used by 29 Vermont Species of Greatest Conservation Need. While small areas of shrub and young forest habitat can be important to some wildlife, managing large patches of 5 acres or more provides much greater benefit to the wildlife that rely on the associated habitat conditions to meet their life requirements. Birds such as the chestnut- sided warbler will use smaller areas of young forest, but less common species such as golden-winged warbler require areas of 25 acres or more. -
Nomadic-Colonial Life Strategies Enable Paradoxical Survival and Growth Despite Habitat Destruction Zhi Xuan Tan1, Kang Hao Cheong2*
RESEARCH ARTICLE Nomadic-colonial life strategies enable paradoxical survival and growth despite habitat destruction Zhi Xuan Tan1, Kang Hao Cheong2* 1Yale University, New Haven, United States; 2Engineering Cluster, Singapore Institute of Technology, Singapore, Singapore Abstract Organisms often exhibit behavioral or phenotypic diversity to improve population fitness in the face of environmental variability. When each behavior or phenotype is individually maladaptive, alternating between these losing strategies can counter-intuitively result in population persistence–an outcome similar to the Parrondo’s paradox. Instead of the capital or history dependence that characterize traditional Parrondo games, most ecological models which exhibit such paradoxical behavior depend on the presence of exogenous environmental variation. Here we present a population model that exhibits Parrondo’s paradox through capital and history- dependent dynamics. Two sub-populations comprise our model: nomads, who live independently without competition or cooperation, and colonists, who engage in competition, cooperation, and long-term habitat destruction. Nomads and colonists may alternate behaviors in response to changes in the colonial habitat. Even when nomadism and colonialism individually lead to extinction, switching between these strategies at the appropriate moments can paradoxically enable both population persistence and long-term growth. Introduction *For correspondence: kanghao.cheong@singaporetech. Behavioral adaptation and phenotypic diversity are evolutionary meta-strategies that can improve edu.sg a population’s fitness in the presence of environmental variability. When behaviors or phenotypes are sufficiently distinct, a population can be understood as consisting of multiple sub-populations, Competing interests: The each following its own strategy. Counter-intuitively, even when each sub-population follows a los- authors declare that no ing strategy that will cause it to go extinct in the long-run, alternating or reallocating organisms competing interests exist. -
Chapter 5 Species Interactions, Ecological Succession, and Population Control How Do Species Interact?
Chapter 5 Species interactions, Ecological Succession, and Population Control How do species interact? Give some limited resources that organisms need in order to survive. Food, shelter, space, mate to reproduce, water, light air How might species interact to get these limited resources? Competition Have you ever competed with another organism to get what you wanted/needed? Interspecific competition is between different species. Intraspecific competition is between a single species. Competition Species need to compete because their niches overlap and they end up sharing the limited resources. When the word “share” is used here, it doesn’t mean equal sharing. Species like to reduce or avoid competition, so they resource partition. Competition Resource partitioning is a way for organisms to share a resource by using the resource at different times or using different parts of the resource. Predator/Prey interactions Predator is the hunter and feeds on the prey (the hunted) This interaction has a strong effect on population sizes. Predator/Prey interactions pg 134- 135 Give a way predators capture their prey. What are some ways prey avoid predators? Birds of prey (predators) and prey Google search ‘Birds of Prey’ – the Nature Conservancy has a great site Google search ‘bluebird, robin, sparrow’ Answer: 1. What differences do you notice regarding placement of the eyes in each group? 2. How might the difference in eye placement benefit each group of birds? What is mimicry? • Mimicry is the similarity of one species to another species which protects one or both organisms. Can be in appearance, behavior, sound, scent and even location. Who are the players? Mimics can be good tasting (easy targets) so they need to gain protection by looking like something bad tasting or dangerous. -
Glossary and Acronyms Glossary Glossary
Glossary andChapter Acronyms 1 ©Kevin Fleming ©Kevin Horseshoe crab eggs Glossary and Acronyms Glossary Glossary 40% Migratory Bird “If a refuge, or portion thereof, has been designated, acquired, reserved, or set Hunting Rule: apart as an inviolate sanctuary, we may only allow hunting of migratory game birds on no more than 40 percent of that refuge, or portion, at any one time unless we find that taking of any such species in more than 40 percent of such area would be beneficial to the species (16 U.S.C. 668dd(d)(1)(A), National Wildlife Refuge System Administration Act; 16 U.S.C. 703-712, Migratory Bird Treaty Act; and 16 U.S.C. 715a-715r, Migratory Bird Conservation Act). Abiotic: Not biotic; often referring to the nonliving components of the ecosystem such as water, rocks, and mineral soil. Access: Reasonable availability of and opportunity to participate in quality wildlife- dependent recreation. Accessibility: The state or quality of being easily approached or entered, particularly as it relates to complying with the Americans with Disabilities Act. Accessible facilities: Structures accessible for most people with disabilities without assistance; facilities that meet Uniform Federal Accessibility Standards; Americans with Disabilities Act-accessible. [E.g., parking lots, trails, pathways, ramps, picnic and camping areas, restrooms, boating facilities (docks, piers, gangways), fishing facilities, playgrounds, amphitheaters, exhibits, audiovisual programs, and wayside sites.] Acetylcholinesterase: An enzyme that breaks down the neurotransmitter acetycholine to choline and acetate. Acetylcholinesterase is secreted by nerve cells at synapses and by muscle cells at neuromuscular junctions. Organophosphorus insecticides act as anti- acetyl cholinesterases by inhibiting the action of cholinesterase thereby causing neurological damage in organisms. -
Mechanism of Ecological Succession
Environmental Biology Prof.(Dr.) Punam Jeswal Head M.Sc semester IV Botany Department MECHANISM OF ECOLOGICAL SUCCESSION ECOLOGICAL SUCCESSION Ecological succession is the gradual and continuous change in the species composition and community structure over time in the same area. Environment is always kept on changing over a period of time due to - i) Variations in climatic and physiographic factors and ii) The activities of the species of the communities themselves. These influences bring changes in the existing community which is sooner or later replaced by another community developed one after another. This process continues and successive communities develop one after another over the same area, until the terminal final community again becomes more or less stable for a period of time. The occurrence of definite sequence of communities over a period of time in the same area is known as Ecological Succession. Succession is a unidirectional progressive series of changes which leads to the established of a relatively stable community. Hult (1885), while studying communities of Southern Sweden used for the first time the term succession for the orderly changes in the communities. Clements (1907, 1916) put forth various principles that governed the process of succession, and while studying plant communities, defined succession as ' the natural process by which the same locality becomes successively colonized by different groups or communities of plants. According to E.P. Odum (1971), the ecological succession is an orderly process of community change in a unity area. It is the process of changes in species composition in an ecosystem over time. In simple terms, it is the process of ecosystem development in nature. -
Is Ecological Succession Predictable?
Is ecological succession predictable? Commissioned by Prof. dr. P. Opdam; Kennisbasis Thema 1. Project Ecosystem Predictability, Projectnr. 232317. 2 Alterra-Report 1277 Is ecological succession predictable? Theory and applications Koen Kramer Bert Brinkman Loek Kuiters Piet Verdonschot Alterra-Report 1277 Alterra, Wageningen, 2005 ABSTRACT Koen Kramer, Bert Brinkman, Loek Kuiters, Piet Verdonschot, 2005. Is ecological succession predictable? Theory and applications. Wageningen, Alterra, Alterra-Report 1277. 80 blz.; 6 figs.; 0 tables.; 197 refs. A literature study is presented on the predictability of ecological succession. Both equilibrium and nonequilibrium theories are discussed in relation to competition between, and co-existence of species. The consequences for conservation management are outlined and a research agenda is proposed focusing on a nonequilibrium view of ecosystem functioning. Applications are presented for freshwater-; marine-; dune- and forest ecosystems. Keywords: conservation management; competition; species co-existence; disturbance; ecological succession; equilibrium; nonequilibrium ISSN 1566-7197 This report can be ordered by paying € 15,- to bank account number 36 70 54 612 by name of Alterra Wageningen, IBAN number NL 83 RABO 036 70 54 612, Swift number RABO2u nl. Please refer to Alterra-Report 1277. This amount is including tax (where applicable) and handling costs. © 2005 Alterra P.O. Box 47; 6700 AA Wageningen; The Netherlands Phone: + 31 317 474700; fax: +31 317 419000; e-mail: [email protected] No part of this publication may be reproduced or published in any form or by any means, or stored in a database or retrieval system without the written permission of Alterra. Alterra assumes no liability for any losses resulting from the use of the research results or recommendations in this report. -
Chapter 5 Hmdscience.Com EN Online Vir Onmental Science Work Ecosystems How
DO NOT EDIT--Changes must be made through “File info” printcode=a Chapter 5 Section 1 Energy Flow in Ecosystems How Section 2 The Cycling of Matter Section 3 How Ecosystems Change Why It Matters Ecosystems This frog gets the energy it needs to survive by eating other organisms, such as damselflies. Frogs and damselflies are both consumers in an aquatic food chain. Work How does energy continue to be transferred in this food chain? CASESTUDY Learn how pollutants, like the pesticide DDT, are transferred through a food chain in the case study DDT in an Aquatic Food Chain on page 120. Online enVirOnmental Science HMDScience.com Go online to access additional resources, including labs, worksheets, multimedia, and resources in Spanish. Inc. Cosmos Blank/Photo Researchers, ©A. 116 DO NOT EDIT--Changes must be made through “File info” printcode=a Section 1 Energy Flow in Objectives Describe how energy is transferred from the sun Ecosystems to producers and then to consumers. organisms need energy to survive, grow, and reproduce. Different organisms Describe one way in which get energy from different sources, but the ultimate source of energy for almost all consumers depend on producers. organisms on earth is the sun. Identify two types of consumers. Explain how energy transfer in a Life Depends on the Sun food web is more complex than Energy from the sun enters an ecosystem when organisms use sunlight energy transfer in a food chain. to make sugar in a process called photosynthesis. During photosynthesis, plants, algae, and some bacteria capture light energy from the sun and Explain why an energy pyramid use it to convert carbon dioxide and water into sugar and oxygen, as is a representation of trophic shown in Figure 1.1. -
Habitat Evaluation: Guidance for the Review of Environmental Impact Assessment Documents
HABITAT EVALUATION: GUIDANCE FOR THE REVIEW OF ENVIRONMENTAL IMPACT ASSESSMENT DOCUMENTS EPA Contract No. 68-C0-0070 work Assignments B-21, 1-12 January 1993 Submitted to: Jim Serfis U.S. Environmental Protection Agency Office of Federal Activities 401 M Street, SW Washington, DC 20460 Submitted by: Mark Southerland Dynamac Corporation The Dynamac Building 2275 Research Boulevard Rockville, MD 20850 CONTENTS Page INTRODUCTION ... ...... .... ... ................................................. 1 Habitat Conservation .......................................... 2 Habitat Evaluation Methodology ................................... 2 Habitats of Concern ........................................... 3 Definition of Habitat ..................................... 4 General Habitat Types .................................... 5 Values and Services of Habitats ................................... 5 Species Values ......................................... 5 Biological diversity ...................................... 6 Ecosystem Services.. .................................... 7 Activities Impacting Habitats ..................................... 8 Land Conversion ....................................... 9 Land Conversion to Industrial and Residential Uses ............. 9 Land Conversion to Agricultural Uses ...................... 10 Land Conversion to Transportation Uses .................... 10 Timber Harvesting ...................................... 11 Grazing ............................................. 12 Mining ............................................. -
Deforestation and Habitat Destruction
Deforestation and Habitat Destruction Say Thanks to the Authors Click http://www.ck12.org/saythanks (No sign in required) To access a customizable version of this book, as well as other 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-source, collaborative, and web-based compilation model, CK-12 pioneers and promotes the creation and distribution of high-quality, adaptive online textbooks that can be mixed, modified and printed (i.e., the FlexBook® textbooks). Copyright © 2016 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. Complete terms can be found at http://www.ck12.org/about/ terms-of-use.