A Mechanistic Verification of the Competitive Exclusion Principle
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Plant Species Richness and Species Area Relationships in a Florida Sandhill Monica Ruth Downer University of South Florida, [email protected]
University of South Florida Scholar Commons Graduate Theses and Dissertations Graduate School January 2012 Plant Species Richness and Species Area Relationships in a Florida Sandhill Monica Ruth Downer University of South Florida, [email protected] Follow this and additional works at: http://scholarcommons.usf.edu/etd Part of the American Studies Commons, Biology Commons, and the Ecology and Evolutionary Biology Commons Scholar Commons Citation Downer, Monica Ruth, "Plant Species Richness and Species Area Relationships in a Florida Sandhill" (2012). Graduate Theses and Dissertations. http://scholarcommons.usf.edu/etd/4030 This Thesis is brought to you for free and open access by the Graduate School at Scholar Commons. It has been accepted for inclusion in Graduate Theses and Dissertations by an authorized administrator of Scholar Commons. For more information, please contact [email protected]. Plant Species Richness and Species Area Relationships in a Florida Sandhill Community by Monica Ruth Downer A thesis submitted in partial fulfillment Of the requirements for the degree of Master of Science Department of Biology College of Arts and Sciences University of South Florida Major Professor: Gordon A. Fox, Ph.D. Co-Major Professor: Earl D. McCoy, Ph.D. Co-Major Professor: Frederick B. Essig, Ph.D. Date of Approval: March 27, 2012 Keywords: Species area curve, burn regime, rank occurrence, heterogeneity, autocorrelation Copyright © 2012, Monica Ruth Downer ACKNOWLEDGEMENTS I would like to offer special thanks to my major professor, Dr. Gordon A. Fox, for his patience, guidance and many hours devoted to helping me in this endeavor. I would like to thank my committee, Dr. -
Functional Benefits of Predator Species Diversity Depend on Prey Identity
Ecological Entomology (2005) 30, 497–501 Functional benefits of predator species diversity depend on prey identity A. WILBY1 , S. C. VILLAREAL2 ,L.P.LAN3 ,K.L.HEONG2 and 1 M. B. THOMAS 1Department of Agricultural Sciences and NERC Centre for Population Biology, Imperial College London, U.K., 2International Rice Research Institute, Metro Manila, Philippines and 3Institute of Agricultural Sciences of South Vietnam, Ho Chi Minh City, Vietnam Abstract. 1. Determining the functional significance of species diversity in nat- ural enemy assemblages is a key step towards prediction of the likely impact of biodiversity loss on natural pest control processes. While the biological control literature contains examples in which increased natural enemy diversity hinders pest control, other studies have highlighted mechanisms where pest suppression is promoted by increased enemy diversity. 2. This study aimed to test whether increased predator species diversity results in higher rates of predation on two key, but contrasting, insect pest species commonly found in the rice ecosystems of south-east Asia. 3. Glasshouse experiments were undertaken in which four life stages of a planthopper (Nilaparvata lugens) and a moth (Marasmia patnalis) were caged with single or three-species combinations of generalist predators. 4. Generally, predation rates of the three-species assemblages exceeded expec- tation when attacking M. patnalis, but not when attacking N. lugens. In addition, a positive effect of increased predator species richness on overall predation rate was found with M. patnalis but not with N. lugens. 5. The results are consistent with theoretical predictions that morphological and behavioural differentiation among prey life stages promotes functional com- plementarity among predator species. -
Species Richness, Species–Area Curves and Simpson's Paradox
Evolutionary Ecology Research, 2000, 2: 791–802 Species richness, species–area curves and Simpson’s paradox Samuel M. Scheiner,1* Stephen B. Cox,2 Michael Willig,2 Gary G. Mittelbach,3 Craig Osenberg4 and Michael Kaspari5 1Department of Life Sciences (2352), Arizona State University West, P.O. Box 37100, Phoenix, AZ 85069, 2Program in Ecology and Conservation Biology, Department of Biological Sciences and The Museum, Texas Tech University, Lubbock, TX 79409, 3W.K. Kellogg Biological Station, 3700 E. Gull Lake Drive, Michigan State University, Hickory Corners, MI 49060, 4Department of Zoology, University of Florida, Gainesville, FL 32611 and 5Department of Zoology, University of Oklahoma, Norman, OK 73019, USA ABSTRACT A key issue in ecology is how patterns of species diversity differ as a function of scale. The scaling function is the species–area curve. The form of the species–area curve results from patterns of environmental heterogeneity and species dispersal, and may be system-specific. A central concern is how, for a given set of species, the species–area curve varies with respect to a third variable, such as latitude or productivity. Critical is whether the relationship is scale-invariant (i.e. the species–area curves for different levels of the third variable are parallel), rank-invariant (i.e. the curves are non-parallel, but non-crossing within the scales of interest) or neither, in which case the qualitative relationship is scale-dependent. This recognition is critical for the development and testing of theories explaining patterns of species richness because different theories have mechanistic bases at different scales of action. -
Loss of Microsatellite Diversity and Low Effective Population Size in an Overexploited Population of New Zealand Snapper (Pagrus Auratus)
Loss of microsatellite diversity and low effective population size in an overexploited population of New Zealand snapper (Pagrus auratus) Lorenz Hauser*†, Greg J. Adcock*‡, Peter J. Smith§, Julio H. Bernal Ramı´rez*¶, and Gary R. Carvalho* *Molecular Ecology and Fisheries Genetics Laboratory, Department of Biological Sciences, University of Hull, Hull HU6 7RX, United Kingdom; and §National Institute of Water and Atmospheric Research, P.O. Box 14901, Wellington, New Zealand Edited by John C. Avise, University of Georgia, Athens, GA, and approved June 27, 2002 (received for review April 23, 2002) Although the effects of overfishing on species diversity and abun- ered being in danger of losing genetic diversity (8), and so there dance are well documented, threats to the genetic diversity of appears to be little cause for concern from a genetic perspective. marine fish populations have so far been largely neglected. Indeed, On the other hand, the number of fish in a population (census there seems to be little cause for concern, as even ‘‘collapsed’’ population size, N) is often much larger than the genetically stocks usually consist of several million individuals, whereas pop- effective population size (Ne), which determines the genetic ulation genetics theory suggests that only very small populations properties of a population (12). The long-term evolutionary Ne suffer significant loss of genetic diversity. On the other hand, in is often orders of magnitude smaller than current population many marine species the genetically effective population size (Ne), sizes, probably because of historic population bottlenecks, ‘‘se- which determines the genetic properties of a population, may be lective sweeps,’’ or colonization histories (13). -
European Gradients of Resilience in the Face of Climate Extremes
EUROPEAN GRADIENTS OF RESILIENCE IN THE FACE OF CLIMATE EXTREMES POLICY BRIEF Field site in Belgium with rainout shelters deployed in 2013 ©Sigi Berwaers This policy brief is based on the results Extreme weather events and the presence of invasive species can act as of the BiodivERsA-funded project pressures threatening biodiversity, resilience and ecosystem services of semi- ‘SIGNAL’ addressing the interaction of three major research areas, combined natural grasslands and drive them beyond thresholds of system integrity in ecology for the first time: biodiversity (tipping points and regime shifts). On the other hand, biodiversity itself may experiments, climate change research, and invasion research. The project made use buffer ecosystem functioning and services against change. Potential stabilising of coordinated experiments in different mechanisms include species richness, presence of key species such as legumes climates across Europe, thereby increasing and within-species diversity. These potential buffers can be promoted by the scope and relevance of the results. conservation management and policy adjustments. K EY POLICY RECOMMENDATIONS • Local biodiversity should be actively stimulated or preserved across European grasslands in order to increase the stability of ecosystem service provisioning, which is especially relevant as climate extremes are expected to become more frequent and intense. • Adjustment of mowing frequency and cutting height can help maintain or increase biodiversity. • More explicit consideration of within-species diversity is warranted, as this component of biodiversity can contribute to stabilising ecosystem functioning in the face of climate extremes. • Ecosystem responses to climate extremes of similar magnitude can vary significantly between climates and regions, suggesting that targeted policy requires tailor-made impact predictions. -
Lecture 33 May 9 Species Interactions – Competition 2007
Figure 49.14 upper left 7.014 Lecture 33 May 9 Species Interactions – Competition 2007 Consumptive competition occurs when organisms compete for the same resources. These trees are competing for nitrogen and other nutrients. Figure 49.14 upper right Figure 49.14 middle left Preemptive competition occurs when individuals occupy space and prevent access Overgrowth competition occurs when an organism grows over another, blocking to resources by other individuals. The space preempted by these barnacles is access to resources. This large fern has overgrown other individuals and is unavailable to competitors. shading them. 1 Figure 49.14 middle right Figure 49.14 lower left Chemical competition occurs when one species produces toxins that negatively Territorial competition occurs when mobile organisms protect a feeding or affect another. Note how few plants are growing under these Salvia shrubs. breeding territory. These red-winged blackbirds are displaying to each other at a territorial boundary. Figure 49.14 lower left The Fundamental Ecological Niche: “An n-dimensional hyper-volume every point on which a species can survive and reproduce indefinitely in the absence of other species” (Hutchinson) y t i d i m u h e iz tem s pe d Encounter competition occurs when organisms interfere directly with each other’s ra oo tur F access to specific resources. Here, spotted hyenas and vultures fight over a kill. e 2 The Realized Ecological Niche: the niche actually occupied in the presence of other species niche overlap leads to competition y t i d i -
Maximum Sustainable Yield from Interacting Fish Stocks in an Uncertain World: Two Policy Choices and Underlying Trade-Offs Arxiv
Maximum sustainable yield from interacting fish stocks in an uncertain world: two policy choices and underlying trade-offs Adrian Farcas Centre for Environment, Fisheries & Aquaculture Science Pakefield Road, Lowestoft NR33 0HT, United Kingdom [email protected] Axel G. Rossberg∗ Queen Mary University of London, School of Biological and Chemical Sciences, 327 Mile End Rd, London E1, United Kingdom and Centre for Environment, Fisheries & Aquaculture Science Pakefield Road, Lowestoft NR33 0HT, United Kingdom [email protected] 26 May 2016 c Crown copyright Abstract The case of fisheries management illustrates how the inherent structural instability of ecosystems can have deep-running policy implications. We contrast ten types of management plans to achieve maximum sustainable yields (MSY) from multiple stocks and compare their effectiveness based on a management strategy evalua- tion (MSE) that uses complex food webs in its operating model. Plans that target specific stock sizes (BMSY) consistently led to higher yields than plans targeting spe- cific fishing pressures (FMSY). A new self-optimising control rule, introduced here arXiv:1412.0199v6 [q-bio.PE] 31 May 2016 for its robustness to structural instability, led to intermediate yields. Most plans outperformed single-species management plans with pressure targets set without considering multispecies interactions. However, more refined plans to \maximise the yield from each stock separately", in the sense of a Nash equilibrium, produced total yields comparable to plans aiming to maximise total harvested biomass, and were more robust to structural instability. Our analyses highlight trade-offs between yields, amenability to negotiations, pressures on biodiversity, and continuity with current approaches in the European context. -
"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. -
Species Richness and Evolutionary Niche Dynamics: a Spatial Pattern–Oriented Simulation Experiment
vol. 170, no. 4 the american naturalist october 2007 ൴ Species Richness and Evolutionary Niche Dynamics: A Spatial Pattern–Oriented Simulation Experiment Thiago Fernando L. V. B. Rangel,1,* Jose´ Alexandre F. Diniz-Filho,2,† and Robert K. Colwell1,‡ 1. Department of Ecology and Evolutionary Biology, University of Connecticut, Storrs, Connecticut 06269; 2. Departamento de Biologia Geral, Instituto de Cieˆncias As early as the eighteenth and nineteenth centuries, nat- Biolo´gicas, Universidade Federal de Goia´s, CP 131, 74001-970 uralists described and documented what we today call geo- Goiaˆnia, Goiaˆnia, Brasil graphical gradients in taxon diversity (species richness), Submitted November 27, 2006; Accepted May 14, 2007; especially the general global pattern of increase in species Electronically published August 9, 2007 richness toward warm and wet tropical regions (Whittaker et al. 2001; Hawkins et al. 2003b; Willig et al. 2003; Hil- Online enhancements: appendixes. lebrand 2004). Initial hypotheses explaining this pattern were deduced solely by observing and describing nature and were based on nothing more rigorous than intuitive correspondence between climatic and biological patterns abstract: Evolutionary processes underlying spatial patterns in (Hawkins 2001). Surprisingly, even after 200 years of re- species richness remain largely unexplored, and correlative studies search in biogeography and ecology, the most common lack the theoretical basis to explain these patterns in evolutionary framework used in such investigations still relies on sta- terms. In this study, we develop a spatially explicit simulation tistical measurements of the concordance between the spa- model to evaluate, under a pattern-oriented modeling approach, whether evolutionary niche dynamics (the balance between niche tial patterns in species richness and multiple environmen- conservatism and niche evolution processes) can provide a parsi- tal factors. -
How to Quantify Competitive Ability
Received: 7 December 2017 | Accepted: 8 February 2018 DOI: 10.1111/1365-2745.12954 ESSAY REVIEW How to quantify competitive ability Simon P. Hart1 | Robert P. Freckleton2 | Jonathan M. Levine1 1Institute of Integrative Biology, ETH Zürich (Swiss Federal Institute of Technology), Abstract Zürich, Switzerland 1. Understanding the role of competition in structuring communities requires that we 2 Department of Animal and Plant quantify competitive ability in a way that permits us to predict the outcome of com- Sciences, University of Sheffield, Sheffield, UK petition over the long term. Given such a clear goal for a process that has been the focus of ecological research for decades, there is surprisingly little consensus on how Correspondence Simon P. Hart to measure competitive ability, with up to 50 different metrics currently proposed. Email: [email protected] 2. Using competitive population dynamics as a foundation, we define competitive Handling Editor: Hans de Kroon ability—the ability of one species to exclude another—using quantitative theoreti- cal models of population dynamics to isolate the key parameters that are known to predict competitive outcomes. 3. Based on the definition of competitive ability we identify the empirical require- ments and describe straightforward methods for quantifying competitive ability in future empirical studies. In doing so, our analysis also allows us to identify why many existing approaches to studying competition are unsuitable for quantifying competitive ability. 4. Synthesis. Competitive ability is precisely defined starting from models of com- petitive population dynamics. Quantifying competitive ability in a theoretically justified manner is straightforward using experimental designs readily applied to studies of competition in the laboratory and field. -
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. -
Plant Species Diversity, Plant Biomass and Responses of the Soil Community on Abandoned Land Across Europe: Idiosyncracy Or Above-Belowground Time Lags
Plant species diversity, plant biomass and responses of the soil community on abandoned land across Europe: idiosyncracy or above-belowground time lags Hedlund, Katarina; Regina, IS; Van der Putten, WH; Leps, J; Diaz, T; Korthals, GW; Lavorel, S; Brown, VK; Gormsen, Dagmar; Mortimer, SR; Barrueco, CR; Roy, J; Smilauer, P; Smilauerova, M; Van Dijk, C Published in: Oikos DOI: 10.1034/j.1600-0706.2003.12511.x 2003 Link to publication Citation for published version (APA): Hedlund, K., Regina, IS., Van der Putten, WH., Leps, J., Diaz, T., Korthals, GW., Lavorel, S., Brown, VK., Gormsen, D., Mortimer, SR., Barrueco, CR., Roy, J., Smilauer, P., Smilauerova, M., & Van Dijk, C. (2003). Plant species diversity, plant biomass and responses of the soil community on abandoned land across Europe: idiosyncracy or above-belowground time lags. Oikos, 103(1), 45-58. https://doi.org/10.1034/j.1600- 0706.2003.12511.x Total number of authors: 15 General rights Unless other specific re-use rights are stated the following general rights apply: Copyright and moral rights for the publications made accessible in the public portal are retained by the authors and/or other copyright owners and it is a condition of accessing publications that users recognise and abide by the legal requirements associated with these rights. • Users may download and print one copy of any publication from the public portal for the purpose of private study or research. • You may not further distribute the material or use it for any profit-making activity or commercial gain • You may freely distribute the URL identifying the publication in the public portal Read more about Creative commons licenses: https://creativecommons.org/licenses/ Take down policy If you believe that this document breaches copyright please contact us providing details, and we will remove access to the work immediately and investigate your claim.