Population Ecology and the Distribution of Organisms Lecture Presentations by Kathleen Fitzpatrick and Nicole Tunbridge, Simon Fraser University
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Effective Population Size and Genetic Conservation Criteria for Bull Trout
North American Journal of Fisheries Management 21:756±764, 2001 q Copyright by the American Fisheries Society 2001 Effective Population Size and Genetic Conservation Criteria for Bull Trout B. E. RIEMAN* U.S. Department of Agriculture Forest Service, Rocky Mountain Research Station, 316 East Myrtle, Boise, Idaho 83702, USA F. W. A LLENDORF Division of Biological Sciences, University of Montana, Missoula, Montana 59812, USA Abstract.ÐEffective population size (Ne) is an important concept in the management of threatened species like bull trout Salvelinus con¯uentus. General guidelines suggest that effective population sizes of 50 or 500 are essential to minimize inbreeding effects or maintain adaptive genetic variation, respectively. Although Ne strongly depends on census population size, it also depends on demographic and life history characteristics that complicate any estimates. This is an especially dif®cult problem for species like bull trout, which have overlapping generations; biologists may monitor annual population number but lack more detailed information on demographic population structure or life history. We used a generalized, age-structured simulation model to relate Ne to adult numbers under a range of life histories and other conditions characteristic of bull trout populations. Effective population size varied strongly with the effects of the demographic and environmental variation included in our simulations. Our most realistic estimates of Ne were between about 0.5 and 1.0 times the mean number of adults spawning annually. We conclude that cautious long-term management goals for bull trout populations should include an average of at least 1,000 adults spawning each year. Where local populations are too small, managers should seek to conserve a collection of interconnected populations that is at least large enough in total to meet this minimum. -
Routledge Handbook of Ecological and Environmental Restoration the Principles of Restoration Ecology at Population Scales
This article was downloaded by: 10.3.98.104 On: 26 Sep 2021 Access details: subscription number Publisher: Routledge Informa Ltd Registered in England and Wales Registered Number: 1072954 Registered office: 5 Howick Place, London SW1P 1WG, UK Routledge Handbook of Ecological and Environmental Restoration Stuart K. Allison, Stephen D. Murphy The Principles of Restoration Ecology at Population Scales Publication details https://www.routledgehandbooks.com/doi/10.4324/9781315685977.ch3 Stephen D. Murphy, Michael J. McTavish, Heather A. Cray Published online on: 23 May 2017 How to cite :- Stephen D. Murphy, Michael J. McTavish, Heather A. Cray. 23 May 2017, The Principles of Restoration Ecology at Population Scales from: Routledge Handbook of Ecological and Environmental Restoration Routledge Accessed on: 26 Sep 2021 https://www.routledgehandbooks.com/doi/10.4324/9781315685977.ch3 PLEASE SCROLL DOWN FOR DOCUMENT Full terms and conditions of use: https://www.routledgehandbooks.com/legal-notices/terms This Document PDF may be used for research, teaching and private study purposes. Any substantial or systematic reproductions, re-distribution, re-selling, loan or sub-licensing, systematic supply or distribution in any form to anyone is expressly forbidden. The publisher does not give any warranty express or implied or make any representation that the contents will be complete or accurate or up to date. The publisher shall not be liable for an loss, actions, claims, proceedings, demand or costs or damages whatsoever or howsoever caused arising directly or indirectly in connection with or arising out of the use of this material. 3 THE PRINCIPLES OF RESTORATION ECOLOGY AT POPULATION SCALES Stephen D. -
Population Ecology: Theory, Methods, Lenses Dr. Bill Fagan
Population ecology: Theory, methods, lenses Dr. Bill Fagan Population Ecology & Spatial Ecology A) Core principles of population growth B) Spatial problems and methods for modeling them C) Integrodifference equations as a robust platform Population Ecology & Spatial Ecology A) Core principles of population growth B) Spatial problems and methods for modeling them C) Integrodifference equations as a robust platform Socio – Environmental Issues: 1. Fisheries 2. Invasive Species 3. Biological Control 4. Ecological Footprints 5. Critical Patch Size / Reserve Design A) Core principles of population growth Berryman: On principles, laws, and theory in population ecology. Oikos. 2003 1) Exponential population growth as a null baseline. What causes deviations from that ? The Basics of Discrete Time Models Have Form Nt1 f Nt , Nt1, Nt2 ,... where N is the thing you are measuring and t is an index representing blocks of time. Constant time step = 1 unit (year, month, day, second) Time is discrete, #’s need not be In many cases Nt1 f Nt Reduced Form Status next time step depends only on where system is now. history is unimportant Alternatively: N t 1 f N t , N t 1 , N t 2 ... history is important wide applicability 1) Many ecological phenomenon change discretely - insects don’t hatch out all day long, only in morning - rodents are less mobile near full moon - seeds germinate in spring daily censuses 2) Data were collected at discrete times yearly censuses The Simplest Discrete Time Model N t1 N t “Geometric” Growth Equation N Thing we -
Energy Economics in Ecosystems By: J
Energy Economics in Ecosystems By: J. Michael Beman (School of Natural Sciences, University of California at Merced) © 2010 Nature Education Citation: Beman, J. (2010) Energy Economics in Ecosystems. Nature Education Knowledge 3(10):13 What powers life? In most ecosystems, sunlight is absorbed and converted into usable forms of energy via photosynthesis. These usable forms of energy are carbonbased. The laws of physics describe the interactions between energy and mass: the energy in a closed system is conserved, and matter can neither be created nor destroyed. Modern physics has shown that reality is more 2 complex at very large and very small scales (e.g., Einstein’s famous equation, E = mc demonstrated that mass can be converted to energy in the sun or nuclear reactors), but in the context of Earth’s ecosystems, energy is conserved and matter can neither be created nor destroyed. This seemingly simplistic statement has profound consequences when we study how ecosystems function. In particular, the energy present within an ecosystem is collected and shared by organisms in many different ways; this "sharing" takes place through ecological interactions, such as predatorprey dynamics and symbioses. When we move to the ecosystem level, however, we consider interactions among organisms, populations, communities, and their physical and chemical environment. These interactions have an important bearing on the structure of organisms, ecosystems, and, over geologic time, the planet itself. A primary example of this involves the energy currency in ecosystems, which is carbon. The amount and form of carbon present in different ecosystem pools — such as plants, animals, air, soil, and water — is controlled by organisms, and ultimately affects their ecological success. -
Evolutionary Restoration Ecology
ch06 2/9/06 12:45 PM Page 113 189686 / Island Press / Falk Chapter 6 Evolutionary Restoration Ecology Craig A. Stockwell, Michael T. Kinnison, and Andrew P. Hendry Restoration Ecology and Evolutionary Process Restoration activities have increased dramatically in recent years, creating evolutionary chal- lenges and opportunities. Though restoration has favored a strong focus on the role of habi- tat, concerns surrounding the evolutionary ecology of populations are increasing. In this con- text, previous researchers have considered the importance of preserving extant diversity and maintaining future evolutionary potential (Montalvo et al. 1997; Lesica and Allendorf 1999), but they have usually ignored the prospect of ongoing evolution in real time. However, such contemporary evolution (changes occurring over one to a few hundred generations) appears to be relatively common in nature (Stockwell and Weeks 1999; Bone and Farres 2001; Kin- nison and Hendry 2001; Reznick and Ghalambor 2001; Ashley et al. 2003; Stockwell et al. 2003). Moreover, it is often associated with situations that may prevail in restoration projects, namely the presence of introduced populations and other anthropogenic disturbances (Stockwell and Weeks 1999; Bone and Farres 2001; Reznick and Ghalambor 2001) (Table 6.1). Any restoration program may thus entail consideration of evolution in the past, present, and future. Restoration efforts often involve dramatic and rapid shifts in habitat that may even lead to different ecological states (such as altered fire regimes) (Suding et al. 2003). Genetic variants that evolved within historically different evolutionary contexts (the past) may thus be pitted against novel and mismatched current conditions (the present). The degree of this mismatch should then determine the pattern and strength of selection acting on trait variation in such populations (Box 6.1; Figure 6.1). -
Concept of Population Ecology
Mini Review Int J Environ Sci Nat Res Volume 12 Issue 1 - June 2018 Copyright © All rights are reserved by Nida Tabassum Khan DOI: 10.19080/IJESNR.2018.12.555828 Concept of Population Ecology Nida Tabassum Khan* Department of Biotechnology, Faculty of Life Sciences and Informatics, Balochistan University of Information Technology Engineering and Management Sciences, Pakistan Submission: May 29, 2018; Published: June 06, 2018 *Corresponding author: Nida Tabassum Khan, Department of Biotechnology, Balochistan University, Quetta, Pakistan, Tel: ; Email: Abstract Population ecology deals with the study of the structure and subtleties of a population which comprises of a group of interacting organisms of the same specie that occupies a given area. The demographic structure of a population is a key factor which is characterized by the number of is growing, shrinking or remain constant in terms of its size. individual members (population size) present at each developmental stage of their cycle to identify whether the population of a specific specie Keywords: Population size; Population density; Gene pool; Life tables Introduction of random genetic drift therefore variation is easily sustained Population ecology deals with the study of the structure in large populations than in smaller ones [10]. Natural selection and subtleties of a population which comprises of a group of selects the most favorable phenotypes suited for an organism interacting organisms of the same specie that occupies a given survival thereby reducing variation within populations [11]. area [1]. Populations can be characterized as local which is a Population structure determines the arrays of demographic group of less number of individuals occupying a small area or variation such as mode of reproduction, age, reproduction met which is a group of local populations linked by disbanding frequency, offspring counts, gender ratio of newborns etc within/ members [2]. -
Meta-Ecosystems: a Theoretical Framework for a Spatial Ecosystem Ecology
Ecology Letters, (2003) 6: 673–679 doi: 10.1046/j.1461-0248.2003.00483.x IDEAS AND PERSPECTIVES Meta-ecosystems: a theoretical framework for a spatial ecosystem ecology Abstract Michel Loreau1*, Nicolas This contribution proposes the meta-ecosystem concept as a natural extension of the Mouquet2,4 and Robert D. Holt3 metapopulation and metacommunity concepts. A meta-ecosystem is defined as a set of 1Laboratoire d’Ecologie, UMR ecosystems connected by spatial flows of energy, materials and organisms across 7625, Ecole Normale Supe´rieure, ecosystem boundaries. This concept provides a powerful theoretical tool to understand 46 rue d’Ulm, F–75230 Paris the emergent properties that arise from spatial coupling of local ecosystems, such as Cedex 05, France global source–sink constraints, diversity–productivity patterns, stabilization of ecosystem 2Department of Biological processes and indirect interactions at landscape or regional scales. The meta-ecosystem Science and School of perspective thereby has the potential to integrate the perspectives of community and Computational Science and Information Technology, Florida landscape ecology, to provide novel fundamental insights into the dynamics and State University, Tallahassee, FL functioning of ecosystems from local to global scales, and to increase our ability to 32306-1100, USA predict the consequences of land-use changes on biodiversity and the provision of 3Department of Zoology, ecosystem services to human societies. University of Florida, 111 Bartram Hall, Gainesville, FL Keywords 32611-8525, -
Population Biology & Life Tables
EXERCISE 3 Population Biology: Life Tables & Theoretical Populations The purpose of this lab is to introduce the basic principles of population biology and to allow you to manipulate and explore a few of the most common equations using some simple Mathcad© wooksheets. A good introduction of this subject can be found in a general biology text book such as Campbell (1996), while a more complete discussion of pop- ulation biology can be found in an ecology text (e.g., Begon et al. 1990) or in one of the references listed at the end of this exercise. Exercise Objectives: After you have completed this lab, you should be able to: 1. Give deÞnitions of the terms in bold type. 2. Estimate population size from capture-recapture data. 3. Compare the following sets of terms: semelparous vs. iteroparous life cycles, cohort vs. static life tables, Type I vs. II vs. III survivorship curves, density dependent vs. density independent population growth, discrete vs. continuous breeding seasons, divergent vs. dampening oscillation cycles, and time lag vs. generation time in population models. 4. Calculate lx, dx, qx, R0, Tc, and ex; and estimate r from life table data. 5. Choose the appropriate theoretical model for predicting growth of a given population. 6. Calculate population size at a particular time (Nt+1) when given its size one time unit previous (Nt) and the corre- sponding variables (e.g., r, K, T, and/or L) of the appropriate model. 7. Understand how r, K, T, and L affect population growth. Population Size A population is a localized group of individuals of the same species. -
Biogeography: an Ecosystems Approach (Geography 338)
WELCOME TO GEOGRAPHY/BOTANY 338: ENVIRONMENTAL BIOGEOGRAPHY Fall 2018 Schedule: Monday & Wednesday 2:30-3:45 pm, Humanities 1641 Credits: 3 Instructor: Professor Ken Keefover-Ring Email: [email protected] Office: Science Hall 115C Office Hours: Tuesday 3:00-4:00 pm & Wednesday 12:00-1:00 pm or by appointment Note: This course fulfills the Biological Science breadth requirement. COURSE DESCRIPTION: This course takes an ecosystems approach to understand how physical -- climate, geologic history, soils -- and biological -- physiology, evolution, extinction, dispersal, competition, predation -- factors interact to affect the past, present and future distribution of terrestrial biomes and all levels of biodiversity: ecosystems, species and genes. A particular focus will be placed on the role of disturbance and to recent human-driven climatic and land-cover changes and biological invasions on differences in historical and current distributions of global biodiversity. COURSE GOALS: • To learn patterns and mechanisms of local to global gene, species, ecosystem and biome distributions • To learn how past, current and future environmental change affect biogeography • To learn how humans affect geographic patterns of biodiversity • To learn how to apply concepts from biogeography to current environmental problems • To learn how to read and interpret the primary literature, that is, scientific articles in peer- reviewed journals. COURSE POLICY: I expect you to attend all lectures and come prepared to participate in discussion. I will take attendance. Please let me know if you need to miss three or more lectures. Please respect your fellow students, professor, and guest speakers and turn off the ringers on your cell phones and refrain from texting during class time. -
Equilibrium Theory of Island Biogeography: a Review
Equilibrium Theory of Island Biogeography: A Review Angela D. Yu Simon A. Lei Abstract—The topography, climatic pattern, location, and origin of relationship, dispersal mechanisms and their response to islands generate unique patterns of species distribution. The equi- isolation, and species turnover. Additionally, conservation librium theory of island biogeography creates a general framework of oceanic and continental (habitat) islands is examined in in which the study of taxon distribution and broad island trends relation to minimum viable populations and areas, may be conducted. Critical components of the equilibrium theory metapopulation dynamics, and continental reserve design. include the species-area relationship, island-mainland relation- Finally, adverse anthropogenic impacts on island ecosys- ship, dispersal mechanisms, and species turnover. Because of the tems are investigated, including overexploitation of re- theoretical similarities between islands and fragmented mainland sources, habitat destruction, and introduction of exotic spe- landscapes, reserve conservation efforts have attempted to apply cies and diseases (biological invasions). Throughout this the theory of island biogeography to improve continental reserve article, theories of many researchers are re-introduced and designs, and to provide insight into metapopulation dynamics and utilized in an analytical manner. The objective of this article the SLOSS debate. However, due to extensive negative anthropo- is to review previously published data, and to reveal if any genic activities, overexploitation of resources, habitat destruction, classical and emergent theories may be brought into the as well as introduction of exotic species and associated foreign study of island biogeography and its relevance to mainland diseases (biological invasions), island conservation has recently ecosystem patterns. become a pressing issue itself. -
Community-Based Population Recovery of Overexploited Amazonian Wildlife
G Model PECON-41; No. of Pages 5 ARTICLE IN PRESS Perspectives in Ecology and Conservation xxx (2017) xxx–xxx ´ Supported by Boticario Group Foundation for Nature Protection www.perspectecolconserv.com Policy Forums Community-based population recovery of overexploited Amazonian wildlife a,∗ b c d e João Vitor Campos-Silva , Carlos A. Peres , André P. Antunes , João Valsecchi , Juarez Pezzuti a Institute of Biological and Health Sciences, Federal University of Alagoas, Av. Lourival Melo Mota, s/n, Tabuleiro do Martins, Maceió 57072-900, AL, Brazil b Centre for Ecology, Evolution and Conservation, School of Environmental Sciences, University of East Anglia, Norwich Research Park, Norwich NR47TJ, UK c Wildlife Conservation Society Brasil, Federal University of Amazonas, Av. Rodrigo Otavio, 3000, Manaus 69077-000, Amazonas, Brazil d Mamiraua Sustainable Development Institute (IDSM), Estrada da Bexiga 2584, Fonte Boa, Tefé, AM, Brazil e Centre for Advanced Amazon Studies, Federal University of Para, R. Augusto Correa 01, CEP 66075-110, Belém, PA, Brazil a b s t r a c t a r t i c l e i n f o Article history: The Amazon Basin experienced a pervasive process of resource overexploitation during the 20th-century, Received 3 June 2017 which induced severe population declines of many iconic vertebrate species. In addition to biodiversity Accepted 18 August 2017 loss and the ecological consequences of defaunation, food security of local communities was relentlessly threatened because wild meat had a historically pivotal role in protein acquisition by local dwellers. Keywords: Here we discuss the urgent need to regulate subsistence hunting by Amazonian semi-subsistence local Hunting regulation communities, which are far removed from the market and information economy. -
Plant Species Traits Are the Predominant Control on Litter Decomposition Rates Within Biomes Worldwide
Ecology Letters, (2008) 11: 1065–1071 doi: 10.1111/j.1461-0248.2008.01219.x LETTER Plant species traits are the predominant control on litter decomposition rates within biomes worldwide Abstract William K. Cornwell,1* Johannes Worldwide decomposition rates depend both on climate and the legacy of plant functional H. C. Cornelissen,1 Kathryn traits as litter quality. To quantify the degree to which functional differentiation among Amatangelo,2 Ellen Dorrepaal,1 species affects their litter decomposition rates, we brought together leaf trait and litter mass 3 4 Valerie T. Eviner, Oscar Godoy, loss data for 818 species from 66 decomposition experiments on six continents. We show Sarah E. Hobbie,5 Bart Hoorens,1 6,7 that: (i) the magnitude of species-driven differences is much larger than previously thought Hiroko Kurokawa, Natalia and greater than climate-driven variation; (ii) the decomposability of a speciesÕ litter is Pe´ rez-Harguindeguy,8 Helen M. consistently correlated with that speciesÕ ecological strategy within different ecosystems Quested,9 Louis S. Santiago,10 David A. Wardle,11,12 Ian J. globally, representing a new connection between whole plant carbon strategy and Wright,13 Rien Aerts,1 Steven D. biogeochemical cycling. This connection between plant strategies and decomposability is Allison,14 Peter van Bodegom,1 crucial for both understanding vegetation–soil feedbacks, and for improving forecasts of Victor Brovkin,15 Alex Chatain,16 the global carbon cycle. Terry V. Callaghan,17,18 Sandra Dı´az,7 Eric Garnier,19 Diego E. Keywords Gurvich,8 Elena Kazakou,19 Julia Carbon cycling, decomposition, leaf economic spectrum, leaf traits, meta-analysis.