Ecology and Energy Flow 9Th - 12Th Grade
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Dung Beetle Richness, Abundance, and Biomass Meghan Gabrielle Radtke Louisiana State University and Agricultural and Mechanical College, [email protected]
Louisiana State University LSU Digital Commons LSU Doctoral Dissertations Graduate School 2006 Tropical Pyramids: Dung Beetle Richness, Abundance, and Biomass Meghan Gabrielle Radtke Louisiana State University and Agricultural and Mechanical College, [email protected] Follow this and additional works at: https://digitalcommons.lsu.edu/gradschool_dissertations Recommended Citation Radtke, Meghan Gabrielle, "Tropical Pyramids: Dung Beetle Richness, Abundance, and Biomass" (2006). LSU Doctoral Dissertations. 364. https://digitalcommons.lsu.edu/gradschool_dissertations/364 This Dissertation is brought to you for free and open access by the Graduate School at LSU Digital Commons. It has been accepted for inclusion in LSU Doctoral Dissertations by an authorized graduate school editor of LSU Digital Commons. For more information, please [email protected]. TROPICAL PYRAMIDS: DUNG BEETLE RICHNESS, ABUNDANCE, AND BIOMASS A Dissertation Submitted to the Graduate Faculty of the Louisiana State University and Agricultural and Mechanical College in partial fulfillment of the requirements for the degree of Doctor of Philosophy in The Department of Biological Sciences by Meghan Gabrielle Radtke B.S., Arizona State University, 2001 May 2007 ACKNOWLEDGEMENTS I would like to thank my advisor, Dr. G. Bruce Williamson, and my committee members, Dr. Chris Carlton, Dr. Jay Geaghan, Dr. Kyle Harms, and Dr. Dorothy Prowell for their help and guidance in my research project. Dr. Claudio Ruy opened his laboratory to me during my stay in Brazil and collaborated with me on my project. Thanks go to my field assistants, Joshua Dyke, Christena Gazave, Jeremy Gerald, Gabriela Lopez, and Fernando Pinto, and to Alejandro Lopera for assisting me with Ecuadorian specimen identifications. I am grateful to Victoria Mosely-Bayless and the Louisiana State Arthropod Museum for allowing me work space and access to specimens. -
A Study of Differences in Vertical Phosphorus Profiles Within the Sediments of Selected Florida Lakes As Related to Trophic Dynamics
University of Central Florida STARS Retrospective Theses and Dissertations 1976 A Study of Differences in Vertical Phosphorus Profiles Within the Sediments of Selected Florida Lakes as Related to Trophic Dynamics Edgar Allen Stewart III University of Central Florida, [email protected] Part of the Engineering Commons Find similar works at: https://stars.library.ucf.edu/rtd University of Central Florida Libraries http://library.ucf.edu This Masters Thesis (Open Access) is brought to you for free and open access by STARS. It has been accepted for inclusion in Retrospective Theses and Dissertations by an authorized administrator of STARS. For more information, please contact [email protected]. STARS Citation Stewart, Edgar Allen III, "A Study of Differences in Vertical Phosphorus Profiles Within the Sediments of Selected Florida Lakes as Related to Trophic Dynamics" (1976). Retrospective Theses and Dissertations. 258. https://stars.library.ucf.edu/rtd/258 • A STUDY OF DIFFEREilCES IN VERTICAL PHOSPHORUS PRO FILES WliHIN THE SEDIMENTS OF SELECTED FLORIUA LAKES AS [{ELATED TO °fROPfiiC DYNArHCS BY EDGAR ALLE N STEHART III B.S., University of Florida, 1971 THESIS SubmHted o'n partial fulfiliment of the requirements for the degree of Mdster of Science °in the Graduate Studies Program of the Co 11 eye of Engi neer i ng of Florida Technological University , Or l ando, Florida 1976 • A STUDY OF DIFFERENCES IN VERTICAL PHOSPHOROUS PROFILES WITHIN THE SEDIMENTS OF SELECTED FLORIDA LAKES AS RELATED TO TROPHIC DYNAMICS BY E. ALLEIJ STEWART I II \ ABSTRACT Seve"a 1 Flori da 1akes with different docu'llcnted traphi c sta te indi ces were se lected for sediment analysis . -
"Species Richness: Small Scale". In: Encyclopedia of Life Sciences (ELS)
Species Richness: Small Advanced article Scale Article Contents . Introduction Rebecca L Brown, Eastern Washington University, Cheney, Washington, USA . Factors that Affect Species Richness . Factors Affected by Species Richness Lee Anne Jacobs, University of North Carolina, Chapel Hill, North Carolina, USA . Conclusion Robert K Peet, University of North Carolina, Chapel Hill, North Carolina, USA doi: 10.1002/9780470015902.a0020488 Species richness, defined as the number of species per unit area, is perhaps the simplest measure of biodiversity. Understanding the factors that affect and are affected by small- scale species richness is fundamental to community ecology. Introduction diversity indices of Simpson and Shannon incorporate species abundances in addition to species richness and are The ability to measure biodiversity is critically important, intended to reflect the likelihood that two individuals taken given the soaring rates of species extinction and human at random are of the same species. However, they tend to alteration of natural habitats. Perhaps the simplest and de-emphasize uncommon species. most frequently used measure of biological diversity is Species richness measures are typically separated into species richness, the number of species per unit area. A vast measures of a, b and g diversity (Whittaker, 1972). a Di- amount of ecological research has been undertaken using versity (also referred to as local or site diversity) is nearly species richness as a measure to understand what affects, synonymous with small-scale species richness; it is meas- and what is affected by, biodiversity. At the small scale, ured at the local scale and consists of a count of species species richness is generally used as a measure of diversity within a relatively homogeneous area. -
SCI Grade 7 Invasive Species
Invasive Species: A Study of the Disruption of an Ecosystem’s Dynamics Life Science: Ecosystems, Interactions, Energy, and Dynamics, Grade 7 This unit engages students in an exploration of ecosystem dynamics as seen through the study of invasive species. The unit focuses on the effects of resource availability in an ecosystem and changes in biological or physical components of an ecosystem on organism populations. Students explore how invasive species are introduced and what impact they have on local food webs; and how ecosystems react to the introduction of invasive species. This unit is designed for students in grade 7, using research, models, data analysis, and writing about invasive species to understand changes in an ecosystem. This Model Curriculum Unit is designed to illustrate effective curriculum that lead to expectations outlined in the Draft Revised Science and Technology/Engineering Standards (www.doe.mass.edu/STEM/review.html) as well as the MA Curriculum Frameworks for English Language Arts/Literacy and Mathematics. This unit includes lesson plans, a Curriculum Embedded Performance Assessment, and related resources. In using this unit it is important to consider the variability of learners in your class and make adaptations as necessary. This work is licensed by the MA Department of Elementary & Secondary Education under the Creative Commons Attribution-NonCommercial-ShareAlike 3.0 Unported License (CC BY-NC-SA 3.0). Educators may use, adapt, and/or share. Not for commercial use. To view a copy of the license, visit http://creativecommons.org/licenses/by-nc-sa/3.0/ July 2015 Page 1 of 77 This document was prepared by the Massachusetts Department of Elementary and Secondary Education Mitchell D. -
102: Trophic Dynamics
102: Trophic Dynamics CORY C CLEVELAND, ALAN R TOWNSEND AND DIANE M MCKNIGHT Institute of Arctic and Aipine Research, University of Coiorado, Bouider, CO, US The carbon (C) and water cycles are intimately linked in terrestrial ecosystems. Thus, an understanding of the processes regulating transfers of water in terrestrial ecosystems requires an understanding of the carbon cycle, and in particular, the factors constraining carbon movement in the soii-piant-atmo sphere continuum and through trophic levels in ecosystems. The linkages between the C and the water cycles are mediated primarily through biological processes, and are bidirectional in nature. For example, precipitation (and hence ecosystem water avaiiabiiity) strongly regulates plant growth and biogeochemicai cycling in soils. Subsequently, plant growth and soil biogeochemistry strongly influence evaporation and atmospheric water vapor (and hence precipitation). Plant growth and soil processes are also cyciicaiiy linked. Thus, plant and soil interactions can have important implications for water cycling. However, while major climatic variables (including precipitation) may drive biological patterns and processes at large scales, other ecological interactions also regulate both plant and soil processes. An appreciation of these ecological factors is important to understanding the relationship between C and water, and to predicting how global environmental change is likely to affect the interactions between the C and water cycles. INTRODUCTION ecosystems is fnndamental to onr nnderstanding of ecosys tem water balance, both at present and in the fntnre. From an ecological perspective, plant photosynthesis regn- lates the carbon balance and prodnctivity of the biosphere, PRIMARY PRODUCTION controls linxes of C between the biosphere and the atmo Gross Primary Production sphere, and is responsible for virtnally all of the biochemi In 1942, Lindeman ontlined the fnndamental ecological cal prodnction of organic matter. -
Community Diversity
Community Diversity Topics What is biodiversity and why is it important? What are the major drivers of species richness? Habitat heterogeneity Disturbance Species energy theory Metobolic energy theory Dynamic equilibrium hypothesis (interactions among disturbance and energy) Resource ratio theory How does biodiversity influence ecosystem function? Biodiversity and ecosystem function hypothesis Integration of biodiversity theory How might the drivers of species richness and hence levels of species richness differ among biomes? Community Diversity Defined Biodiversity Merriam-Webster - the existence of many different kinds of plants and animals in an environment. Wikipedia - the degree of variation of life forms within a given species, ecosystem, biome, or an entire planet. U.S. Congress Office of Technology Assessment - the variety and variability among living organisms and the ecological complexes in which they occur. Diversity can be defined as the number of different items and their relative frequency. For biological diversity, these items are organized at many levels, ranging from complete ecosystems to the chemical structures that are the molecular basis of heredity. Thus, the term encompasses different ecosystems, species, genes, and their relative abundance." Community Diversity Defined Species richness - Species evenness - Species diversity - Community Diversity Defined Species richness - number of species present in the community (without regard for their abundance). Species evenness - relative abundance of the species that are -
Long-Term Nutrient Enrichment Decouples Predator and Prey Production
Long-term nutrient enrichment decouples predator and prey production John M. Davisa,1,2, Amy D. Rosemonda, Susan L. Eggertb, Wyatt F. Crossa,3, and J. Bruce Wallacec aOdum School of Ecology, University of Georgia, Athens, GA 30602; bUS Department of Agriculture Forest Service, Northern Research Station, Grand Rapids, MN 55744; and cDepartment of Entomology, University of Georgia, Athens, GA 30602 Edited by William Bowden, University of Vermont, and accepted by the Editorial Board November 23, 2009 (received for review July 28, 2009) Increased nutrient mobilization by human activities represents one amplify variability in predator–prey cycles and even extirpate of the greatest threats to global ecosystems, but its effects on predator populations (i.e., “the paradox of enrichment”) (9). ecosystem productivity can differ depending on food web structure. More recent models predict that nutrient enrichment can fur- When this structure facilitates efficient energy transfers to higher ther alter predator–prey interactions by increasing the dominance trophic levels, evidence from previous large-scale enrichments of predator-resistant primary consumers, diverting energy flow to suggests that nutrients can stimulate the production of multiple predator-resistant pathways that are relatively inaccessible to top trophic levels. Here we report results from a 5-year continuous predators (10, 11). Small-scale mesocosm experiments have nutrient enrichment of a forested stream that increased primary shown that such a reduction in trophic efficiency can ultimately consumer production, but not predator production. Because of decrease predator production, even with sustained increases in strong positive correlations between predator and prey production primary consumer productivity (i.e., resulting in a trophic decou- (evidence of highly efficient trophic transfers) under reference pling) (12, 13). -
Burning Reduces Nematode Abundance in Reconstructed Prairies
Burning reduces nematode abundance in reconstructed prairies EVIE KENEPP Biology Department, Grinnell College, PO Box 805, Grinnell, IA 50112, USA Introduction community upon death (Freckman and Baldwin, 1990). Their effect on Nematodes are one of the most plant production is less numerous and diverse groups of conclusive and depends highly on organisms. They have an intricate the interaction between specific relationship with the soil plant and nematode species: some ecosystem (Freckman & Baldwin, plants are resistant to nematode 1990; Ingham, 1994). Nematodes are invasion, while others are microscopic worms that vary in tolerant of high numbers of size, but most are less than 4 mm nematodes feeding in or on their in length (Freckman and Baldwin, roots (Freckman and Baldwin, 1990). There are six 1990). classifications of nematodes, It is important to know the based on their feeding habits: impact of nematodes on prairie endoparasites, ectoparasites, ecosystems so they can be properly microbivores, and fungivores, managed. Smolick (1974) estimated omnivores and predators, which that root-feeding nematodes play a unique role in soil food consumed as much plant material as webs (Freckman and Virginia, 1997; cattle in a Colorado grassland Ingham, 1994). Plant-feeding ecosystem (as cited in Freckman nematodes affect primary plant and Virginia, 1989). Ingham and production by feeding on roots and Detling (1984) found that in seed heads. Other types of grassland ecosystems, nematode nematodes affect nutrient cycling herbivory decreased plant and decomposition by feeding on production from 6-13% (as cited in fungi, bacteria and microfauna. Freckman and Virginia, 1989). A (Freckman & Baldwin, 1990; high population of root-feeding Freckman & Virginia, 1997). -
Arboreal Arthropod Predation on Early Instar Douglas-Fir Tussock Moth Redacted for Privacy
AN ABSTRACT OF THE THESIS OF Becky L. Fichter for the degree of Doctor of Philosophy in Entomologypresented onApril 23, 1984. Title: Arboreal Arthropod Predation on Early Instar Douglas-fir Tussock Moth Redacted for privacy Abstract approved: William P. StOphen Loss of early instar Douglas-fir tussock moth( Orgyia pseudotsugata McDunnough) (DFTM) has been found to constitute 66-92% of intra-generation mortality and to be a key factor in inter-generation population change. This death has been attributed to dispersal and to arthropod predation, two factors previously judged more important to an endemic than an outbreak population. Polyphagous arthropod predators are abundant in the forest canopy but their predaceous habits are difficult to document or quantify. The purpose of the study was to develop and test a serological assay, ELISA or enzyme-linked immunosorbent assay, for use as an indirect test of predation. Development of this assay involved production of an antiserum reactive with DFTM but not reactive with material from any coexisting lepidopteran larvae. Two-dimensional immunoelectrophoresis was used to select a minimally cross-reactive fraction of DFTM hemolymph as the antigen source so that a positive response from a field-collected predator would correlate unambiguously with predation on DFTM. Feeding trials using Podisus maculiventris Say (Hemiptera, Pentatomidae) and representative arboreal spiders established the rate of degredation of DFTM antigens ingested by these predators. An arbitrary threshold for deciding which specimens would be considered positive was established as the 95% confidence interval above the mean of controls. Half of the Podisus retained 0 reactivity for 3 days at a constant 24 C. -
Food Webs, Body Size, and Species Abundance in Ecological Community Description
Food Webs, Body Size, and Species Abundance in Ecological Community Description TOMAS JONSSON, JOEL E. COHEN, AND STEPHEN R. CARPENTER I. Summary ............................................... 2 A. Trivariate Relationships................................ 2 B. Bivariate Relationships ................................ 3 C. Univariate Relationships . ............................ 4 D. EVect of Food Web Perturbation ........................ 4 II. Introduction . ........................................... 4 A. Definitions .......................................... 7 III. Theory: Integrating the Food Web and the Distributions of Body Size and Abundance . ................................... 9 A. Predicting Community Patterns.......................... 10 B. The Distribution of Body Sizes .......................... 13 C. Rank-Abundance and Food Web Geometry . ............. 15 D. Linking the Food Web to the Relationship Between Body Size and Numerical Abundance . ............................ 16 E. Trophic Pyramids and the Relationship Between Consumer and Resource Abundance Across Trophic Levels ............ 18 IV. Data: Tuesday Lake . ................................... 20 A. The Manipulation . ................................... 21 B. The Data ........................................... 22 V. Results: Patterns and Relationships in the Pelagic Community of Tuesday Lake ........................................... 25 A. Trivariate Distributions: Food Web, Body Size, and Abundance 25 B. Bivariate Distributions. ................................ 29 C. -
The Benefits of MARINE PROTECTED AREAS © Commonwealth of Australia 2003 ISBN 0 642 54949 4
TheThe benefitsbenefits ofof MMARINEARINE PROTECTEDPROTECTED AREASAREAS The benefits of MARINE PROTECTED AREAS © Commonwealth of Australia 2003 ISBN 0 642 54949 4 Information contained in this document may be copied for study, research, information or educational purposes, subject to inclusion of acknowledgment of the source. Photography courtesy of the Great Barrier Marine Park Authority. This document has been prepared by the Commonwealth Department of Environment and Heritage from material supplied by Richard Kenchington, Trevor Ward, and Eddie Hegerl. A technical support paper is also included in this resource kit, providing more details on current issues and practice for those who have not yet been involved in the processes of creation and management of marine protected areas. This summary of the benefits of marine protected areas is based on the scientific contributions of numerous authors. We acknowledge these sources, and specific contributions are cited in the accompanying technical support paper. THE BENEFITS OF MARINE PROTECTED AREAS CONTENTS What is a marine protected area? 4 Why do we need marine protected areas? 4 The role of MPAs in protecting marine habitats and biodiversity 5 Conserving biodiversity and ecosystems 6 How do MPAs benefit fisheries? 8 How do MPAs benefit tourism? 13 What are the broader benefits of MPAs? 15 Education, training, heritage and culture 17 MPAs and research 19 3. THE BENEFITS OF MARINE PROTECTED AREAS What is a marine protected area? marine resources for seafood. The global fish catch has been in consistent decline since 1989 and the downward A marine protected area (MPA) is an area of sea especially trend is projected to continue. -
Overview Directions
R E S O U R C E L I B R A R Y A C T I V I T Y : 1 H R Marine Food Webs Students investigate marine food webs and trophic levels, research one marine organism, and fit their organisms together in a class-created food web showing a balanced marine ecosystem. G R A D E S 9 - 12+ S U B J E C T S Biology, Ecology, Earth Science, Oceanography, Geography, Physical Geography C O N T E N T S 9 Images, 3 PDFs, 6 Links OVERVIEW Students investigate marine food webs and trophic levels, research one marine organism, and fit their organisms together in a class-created food web showing a balanced marine ecosystem. For the complete activity with media resources, visit: http://www.nationalgeographic.org/activity/marine-food-webs/ DIRECTIONS 1. Build background about marine trophic pyramids and food webs. Review with students that food chains show only one path of food and energy through an ecosystem. In most ecosystems, organisms can get food and energy from more than one source, and may have more than one predator. Healthy, well-balanced ecosystems are made up of multiple, interacting food chains, called food webs. Ask volunteers to come to the front of the room and draw a pyramid and a web. Explain that the shapes of a pyramid and a web are two different ways of representing predator-prey relationships and the energy flow in an ecosystem. Food chains are often represented as food pyramids so that the different trophic levels and the amount of energy and biomass they contain can be compared.