Ecological Succession on Neotropical Landslides
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Early Evolution of the Angiosperm Clade Asteraceae in the Cretaceous of Antarctica
Early evolution of the angiosperm clade Asteraceae in the Cretaceous of Antarctica Viviana D. Barredaa,1,2, Luis Palazzesia,b,1, Maria C. Telleríac, Eduardo B. Oliverod, J. Ian Rainee, and Félix Forestb aDivisión Paleobotánica, Museo Argentino de Ciencias Naturales “Bernardino Rivadavia,” Consejo Nacional de Investigaciones Cientificas y Técnicas, Buenos Aires C1405DJR, Argentina; bJodrell Laboratory, Royal Botanic Gardens, Kew, Richmond, Surrey TW9 3DS, United Kingdom; cLaboratorio de Sistemática y Biología Evolutiva, Museo de La Plata, La Plata B1900FWA, Argentina; dCentro Austral de Investigaciones Científicas, Consejo Nacional de Investigaciones Cientificas y Técnicas, 9410 Ushuaia, Tierra del Fuego, Argentina; and eDepartment of Palaeontology, GNS Science, Lower Hutt 5040, New Zealand Edited by Michael J. Donoghue, Yale University, New Haven, CT, and approved July 15, 2015 (received for review December 10, 2014) The Asteraceae (sunflowers and daisies) are the most diverse Here we report fossil pollen evidence from exposed Campanian/ family of flowering plants. Despite their prominent role in extant Maastrichtian sediments from the Antarctic Peninsula (Fig. 1, Fig. S1, terrestrial ecosystems, the early evolutionary history of this family and SI Materials and Methods, Fossiliferous Localities)(7)thatradi- remains poorly understood. Here we report the discovery of a cally changes our understanding of the early evolution of Asteraceae. number of fossil pollen grains preserved in dinosaur-bearing deposits from the Late Cretaceous of Antarctica that drastically pushes back Results and Discussion the timing of assumed origin of the family. Reliably dated to ∼76–66 The pollen grains reported here and discovered in the Late Cre- Mya, these specimens are about 20 million years older than previ- taceous of Antarctica are tricolporate, microechinate, with long ously known records for the Asteraceae. -
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. -
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. -
Systematics of Dasyphyllum (Asteraceae)
Instituto de Pesquisas Jardim Botânico do Rio de Janeiro Escola Nacional de Botânica Tropical Programa de Pós-Graduação em Botânica Systematics of Dasyphyllum (Asteraceae) Mariana M. Saavedra Elsie F. Guimarães e Rafaela C. Forzza Barnadesioideae • Synapomorphies: – axillary spines – barnadesioids trichomes • Restricted distribution in South America • 9 genus and 85 species – Dasyphyllum (33 spp.) – Chuquiraga (23 spp.) – Barnadesia (19 spp.) – Arnaldoa (3 spp.) – Doniophyton (2 spp.) – Fulcaldea (2 spp.) – Duseniella, Huarpea e Dasyphyllum vagans Schlechtendalia (1 spp.) Funk et al. 2009 Dasyphyllum Kunth Kunth (1820) – D. argenteum Cabrera (1959) – Dasyphyllum • 36 species (34 new combinations) Infrageneric classification sensu Cabrera • Trees Dasyphyllum subg. Archydasyphyllum • Pinnate leaves • Anthers’ apical appendage • 2 species obtuse or emarginate • D. diacanthoides (Less.) Cabrera • D. excelsum (D.Don) Cabrera) D. diacanthoides Stuessy et al. 1996 Dasyphyllum sensu Cabrera (1959) • Trees or shrubs Dasyphyllum subg. Dasyphyllum • Trinerved leaves • Anthers’ apical appendages bilobed Section Microcephala (=Dasyphyllum) Section Macrocephala • Small and numerous heads • Large and solitaries or few heads • 27 species, 6 varieties • 11 species, 2 varieties D. sprengelianum Stuessy et al. 1996 Stuessy et al. 1996 D. spinescens Morphological phylogeny Urtubey & Stuessy 2001 • 52 of 88 species of the subfamily • 29 spp. Dasyphyllum • 31 morphological characters • 13 characters are informative to Dasyphyllum Infrageneric classification -
Chloroplast Dna Systematics of Lilioid Monocots: Resources, Feasibility, and an Example from the Orchidaceaei
Amer. J. Bot. 76(12): 1720-1730. 1989. CHLOROPLAST DNA SYSTEMATICS OF LILIOID MONOCOTS: RESOURCES, FEASIBILITY, AND AN EXAMPLE FROM THE ORCHIDACEAEI MARK W. CHASE2 AND JEFFREY D. PALMER3 Department of Biology, University of Michigan, Ann Arbor, Michigan 48109-1048 ABSTRACT Although chloroplast DNA (cpDNA) analysis has been widely and successfully applied to systematic and evolutionary problems in a wide variety of dicots, its use in monocots has thus far been limited to the Poaceae. The cpDNAs ofgrasses are significantly altered in arrangement relative to the genomes of most vascular plants, and thus the available clone banks ofgrasses are not particularly useful in studying variation in the cpDNA ofother monocots. In this report, we present mapping studies demonstrating that cpDNAs offour lilioid monocots (Allium cepa, Alliaceae; Asparagus sprengeri, Asparagaceae; Narcissus x hybridus, Amaryllidaceae; and On cidium excavatum, Orchidaceae), which, while varying in size over as much as 18 kilobase pairs, conform to the genome arrangement typical of most vascular plants. A nearly complete (99.2%) clone bank was constructed from restriction fragments of the chloroplast genome of Oncidium excavatum; this bank should be useful in cpDNA analysis among the monocots and is available upon request. As an example of the utility of filter hybridization using this clone bank to detect systematically useful variation, we present a Wagner parsimony analysis of restriction site data from the controversial genus Trichocentrum and several sections of Oncid ium, popularly known as the "mule ear" and "rat tail oncidiums." Because of their vastly different floral morphology, the species of Trichocentrum have never been placed in Oncidium, although several authors have recently suggested a close relationship to this vegetatively modified group. -
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. -
Phylogenetic Uncertainty and Fossil Calibration of Asteraceae Chronograms LETTER Jose L
LETTER Phylogenetic uncertainty and fossil calibration of Asteraceae chronograms LETTER Jose L. Panero1 Barreda et al. (1) claim a Cretaceous fossil pollen type is an opposed to other Barnadesioideae. Encoding “columel- extinct Asteraceae. Concluding this pollen type is “nested late layer visibility under light microscopy” (character 19) within Dasyphyllum (crown representative),” they calibrate results in unintentional character weighting. Exine thick- a Dasyphyllum + Barnadesia crown node (Dasyphyllum ness (character 22) is much smaller in Dasyphyllum crown absent) and estimate an 85.9-Ma Asteraceae crown inerme and Dasyphyllum velutinum than in other Dasy- age that potentially compresses asterid evolution by tens phyllum spp. (3) that would be scored as other Barnade- of millions of years. However, the bootstrap majority con- sioideae and different from the fossil had they been sensus topology reported could not be reproduced from sampled. Characters 19, 21, and 22 clearly contribute the data; instead, the fossil resolved in a trichotomy with to place the fossil with Dasyphyllum. Character 17 as- Calyceraceae and Asteraceae. Thus, unambiguous assign- sumes that concavities distributed asymmetrically ment of these pollen grains to Asteraceae is premature. (sometimes absent) along the intercolpal region in the Paleocene, not Cretaceous, mean ages of Asteraceae fossil are homologous with symmetrically distributed result from calibration placement consistent with the intercolpal concavities in extant taxa and not the result fossil’s phylogenetic position in the reproduced bootstrap of compression forces during fossilization (figure 4 in tree. Calibration at the Asteraceae + Calyceraceae crown ref. 1). This character is scored as “present” in the fossil node (second calibration scenario; figure S5A and table (table S1 in ref. -
Early Successional Habitat
Early Successional Habitat January 2007 Fish and Wildlife Habitat Management Leaflet Number 41 Introduction Change is a characteristic of all natural systems. Directional change in the make-up and appearance of natural communities over time is commonly known as ecological succession. This change begins with a dis- turbance to the existing community, followed by plant colonization or regrowth. Materials (snags, soils, and disturbance-adapted seeds and other organisms) that are left behind after a disruptive event serve as biolog- ical legacies; that is, potential reservoirs of life, facili- tating the recovery of the habitat and biological com- munity. Through complex interactions, the disturbances, cli- mate, and soils of an ecological site are reflected in NRCS a plant community that is unique to that site. In a Early successional habitats are highly dynamic, highly healthy ecosystem, the plant community is in a state productive seral stages with uniquely adapted animal of dynamic (or ever changing) equilibrium exhibiting communities. variability in species composition and successional stages following disturbance. This variability creates valuable wildlife habitat because different wildlife Early successional habitats form soon after a distur- species are adapted to different plant species and suc- bance. Early successional plants are generally her- cessional stages. Over evolutionary time, plants and baceous annuals and perennials that quickly occupy animals have developed traits that allow them to sur- disturbed sites. They reproduce seeds that are distur- vive, exploit, and even depend on disturbances. For bance adapted or can be widely dispersed by wind, example, some plants require fire to produce seeds or water, or animals. Early successional communities flowers, and some fish depend on regular flooding to are characterized by high productivity and provide create and maintain their streambed habitat.