The Genetic Allee Effect
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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. -
Genetic and Demographic Dynamics of Small Populations of Silene Latifolia
Heredity (2003) 90, 181–186 & 2003 Nature Publishing Group All rights reserved 0018-067X/03 $25.00 www.nature.com/hdy Genetic and demographic dynamics of small populations of Silene latifolia CM Richards, SN Emery and DE McCauley Department of Biological Sciences, Vanderbilt University, PO Box 1812, Station B, Nashville, TN 37235, USA Small local populations of Silene alba, a short-lived herbac- populations doubled in size between samples, while others eous plant, were sampled in 1994 and again in 1999. shrank by more than 75%. Similarly, expected heterozygosity Sampling included estimates of population size and genetic and allele number increased by more than two-fold in diversity, as measured at six polymorphic allozyme loci. individual populations and decreased by more than three- When averaged across populations, there was very little fold in others. When population-specific change in number change between samples (about three generations) in and change in measures of genetic diversity were considered population size, measures of within-population genetic together, significant positive correlations were found be- diversity such as number of alleles or expected hetero- tween the demographic and genetic variables. It is specu- zygosity, or in the apportionment of genetic diversity within lated that some populations were released from the and among populations as measured by Fst. However, demographic consequences of inbreeding depression by individual populations changed considerably, both in terms gene flow. of numbers of individuals and genetic composition. Some Heredity (2003) 90, 181–186. doi:10.1038/sj.hdy.6800214 Keywords: genetic diversity; demography; inbreeding depression; gene flow Introduction 1986; Lynch et al, 1995), the interaction of genetics and demography could also influence population persistence How genetics and demography interact to influence in common species, because it is generally accepted that population viability has been a long-standing question in even many abundant species are not uniformly distrib- conservation biology. -
Introduction to Theoretical Ecology
Introduction to Theoretical Ecology Natal, 2011 Objectives After this week: The student understands the concept of a biological system in equilibrium and knows that equilibria can be stable or unstable. The student understands the basics of how coupled differential equations can be analyzed graphically, including phase plane analysis and nullclines. The student can analyze the stability of the equilibria of a one-dimensional differential equation model graphically. The student has a basic understanding of what a bifurcation point is. The student can relate alternative stable states to a 1D bifurcation plot (e.g. catastrophe fold). Study material / for further study: This text Scheffer, M. 2009. Critical Transitions in Nature and Society, Princeton University Press, Princeton and Oxford. Scheffer, M. 1998. Ecology of Shallow Lakes. 1 edition. Chapman and Hall, London. Edelstein-Keshet, L. 1988. Mathematical models in biology. 1 edition. McGraw-Hill, Inc., New York. Tentative programme (maybe too tight for the exercises) Monday 9:00-10:30 Introduction Modelling + introduction Forrester diagram + 1D models (stability graphs) 10:30-13:00 GRIND Practical CO2 chamber - Ethiopian Wolf Tuesday 9:00-10:00 Introduction bifurcation (Allee effect) and Phase plane analysis (Lotka-Volterra competition) 10:00-13:00 GRIND Practical Lotka-Volterra competition + Sahara Wednesday 9:00-13:00 GRIND Practical – Sahara (continued) and Algae-zooplankton Thursday 9:00-13:00 GRIND practical – Algae zooplankton spatial heterogeneity Friday 9:00-12:00 GRIND practical- Algae zooplankton fish 12:00-13:00 Practical summary/explanation of results - Wrap up 1 An introduction to models What is a model? The word 'model' is used widely in every-day language. -
Population Genetic Consequences of the Allee Effect and The
Genetics: Early Online, published on July 9, 2014 as 10.1534/genetics.114.167569 Population genetic consequences of the Allee effect and the 2 role of offspring-number variation Meike J. Wittmann, Wilfried Gabriel, Dirk Metzler 4 Ludwig-Maximilians-Universit¨at M¨unchen, Department Biology II 82152 Planegg-Martinsried, Germany 6 Running title: Allee effect and genetic diversity Keywords: family size, founder effect, genetic diversity, introduced species, stochastic modeling 8 Corresponding author: Meike J. Wittmann Present address: Stanford University 10 Department of Biology 385 Serra Mall, Stanford, CA 94305-5020, USA 12 [email protected] 1 Copyright 2014. Abstract 14 A strong demographic Allee effect in which the expected population growth rate is nega- tive below a certain critical population size can cause high extinction probabilities in small 16 introduced populations. But many species are repeatedly introduced to the same location and eventually one population may overcome the Allee effect by chance. With the help of 18 stochastic models, we investigate how much genetic diversity such successful populations har- bor on average and how this depends on offspring-number variation, an important source of 20 stochastic variability in population size. We find that with increasing variability, the Allee effect increasingly promotes genetic diversity in successful populations. Successful Allee-effect 22 populations with highly variable population dynamics escape rapidly from the region of small population sizes and do not linger around the critical population size. Therefore, they are 24 exposed to relatively little genetic drift. It is also conceivable, however, that an Allee effect itself leads to an increase in offspring-number variation. -
AC28 Inf. 30 (English and Spanish Only / Únicamente En Inglés Y Español / Seulement En Anglais Et Espagnol)
AC28 Inf. 30 (English and Spanish only / únicamente en inglés y español / seulement en anglais et espagnol) CONVENTION ON INTERNATIONAL TRADE IN ENDANGERED SPECIES OF WILD FAUNA AND FLORA ___________________ Twenty-eighth meeting of the Animals Committee Tel Aviv (Israel), 30 August-3 September 2015 REPORT OF THE SECOND MEETING OF THE CFMC/OSPESCA/WECAFC/CRFM WORKING GROUP ON QUEEN CONCH The attached information document has been submitted by the Secretariat on behalf of the FAO Western Central Atlantic Fishery Commission in relation to agenda item 19.* * The geographical designations employed in this document do not imply the expression of any opinion whatsoever on the part of the CITES Secretariat (or the United Nations Environment Programme) concerning the legal status of any country, territory, or area, or concerning the delimitation of its frontiers or boundaries. The responsibility for the contents of the document rests exclusively with its author. AC28 Inf. 30 – p. 1 SLC/FIPS/SLM R1097 FAO Fisheries and Aquaculture Report ISSN 2070-6987 WESTERN CENTRAL ATLANTIC FISHERY COMMISSION Report of the SECOND MEETING OF THE CFMC/OSPESCA/WECAFC/CRFM WORKING GROUP ON QUEEN CONCH Panama City, Panama, 18–20 November 2014 DRAFT Prepared for the 28th meeting of the Animals Committee (A final version in English, French and Spanish is expected to be published by October 2015) 1 PREPARATION OF THIS DOCUMENT This is the report of the second meeting of the Caribbean Fisheries Management Council (CFMC), Organization for the Fisheries and Aquaculture Sector of the Central American Isthmus (OSPESCA), Western Central Atlantic Fishery Commission (WECAFC) and the Caribbean Regional Fisheries Mechanism (CRFM) Working Group on Queen Conch, held in Panama City, Panama, from 18 to 20 November 2014. -
4 Genetics of Small Populations: the Case of the Laysan Finch
Case Studies in Ecology and Evolution DRAFT 4 Genetics of Small Populations: the case of the Laysan Finch In 1903, rabbits were introduced to a tiny island in the Hawaiian archipelago called Laysan Island. That island is only 187 ha in size, in the middle of the Pacific Ocean about 1000 km northeast of Hawaii. Despite the benign intentions for having rabbits on the island, the released rabbits quickly multiplied and devoured most of the vegetation. Oceanic islands are often home to unique or endemic species that have evolved in isolation. Laysan was no exception. Well-known examples of island endemics include the finches on the Galapagos Islands and the dodo that was only known from the islands of Mauritius. On Laysan there were several species of birds and plants that were known only from that single island. The introduced rabbits on the island destroyed the food supply for various species of land birds. Several endemic species of plants and animals were driven extinct, including the Laysan rail, the Laysan honeycreeper, the millerbird, and plants like the Laysan fan palm. Only 4 of 26 species of plants remained on the island in 1923, 20 years after the rabbits first arrived. Populations of other species declined to very small levels. One of the two surviving endemic land birds was a small finch called the Laysan finch, Telespiza cantans. After the rabbits were finally exterminated in 1923, the population of finches recovered on Laysan Island. Over the last four decades the average population size of on Laysan Island has been about 11,000 birds. -
Amphibian Cascades Frog SOC X X Mountain Meadows, Bogs, Ponds Or
Taxa Species Species SMU/ESU/D Federal State BM CP CR EC KM NR WC WV NS Special needs Limiting factors Data gaps Conservation actions Key reference or plan, if available Common Scientific PS/Group Listing listing Name Name Status status Amphibian Cascades SOC X X Mountain meadows, bogs, ponds or potholes Montane species vulnerable to genetic Habitat requirements and how they may vary by Maintain connectivity of habitat. Monitor effects of fish http://www.fs.fed.us/psw/publications/documents/ frog above 2,400 feet elevation. Requires access isolation. Experiencing substantial elevation within the species' range. Habitat stocking and water quality on populations. Carefully manage psw_gtr244/psw_gtr244.pdf to permanent water. Lays eggs in shallow reductions in southern parts of range characteristics that could enhance migration livestock grazing in occupied wet meadows. Use prescribed sunny edges of ponds, or on low vegetation (e.g., CA). Potentially sensitive to and gene flow. Feeding habits. Effects of burning or hand-felling of trees periodically to set plant near ponds where warm sunlight speeds egg waterborne pathogens. pathogens airborne environmental pollution. succession. If reintroductions are warranted, use individuals development. Larvae may “school” in large Feasibility studies on reintroduction at historic from nearby populations and consult results of feasibility masses. sites. studies. Conservation actions in Oregon are particularly valuable given reductions in other parts of range. Amphibian Cascade X X Cold, fast-flowing, clear, permanent headwater Larvae take several years to reach sexual Basic inventory, abundance and population Maintain stream buffers to maintain cool water Howell, B.L. and N. M. Maggiulli. 2011. -
ANDREW M. KRAMER Curriculum Vitae Address
Kramer 1 ANDREW M. KRAMER Curriculum Vitae Address: Department of Integrative Biology University of South Florida 4202 E. Fowler Ave SCA 110 Tampa, FL 33620 (813) 974-2825 email: [email protected] website: http://kramera3.github.io EDUCATION • Ph.D. in Fisheries and Wildlife / Ecology, Evolutionary Biology and Behavior (dual degree), 2007, Michigan State University. Advisor: Orlando Sarnelle • Bachelor of Science, 2000, Saint Louis University, Honors degree, Biology (summa cum laude) ACADEMIC APPOINTMENTS • Assistant Professor, Department of Integrative Biology, University of South Florida, Jan. 2018 – present. • Assistant Research Scientist, Odum School of Ecology, University of Georgia, Aug. 2013 – Dec. 2017. Member of the Graduate Faculty. • Postdoctoral researcher, Odum School of Ecology, University of Georgia, Sept. 2009 – April 2013. Mentor: Dr. John Drake • Instructor, Department of Biology, Gainesville State College, Georgia, Summer 2009. • Postdoctoral researcher, Odum School of Ecology, University of Georgia, Oct. 2007-March 2009. Mentor: Dr. John Drake GRANTS AND AWARDS • Under consideration – National Science Foundation, National Artificial Intelligence Research Institute, “AI Institute: Institute for Advancing Integrative Biology (AIBI)”, 2021-2026. co-PI Kramer, PI: Sudeep Sarkar. ($19,599,253 with $1,959,925 to Kramer). • Under consideration – National Science Foundation, Information Integration and Informatics, “Collaborative Research: Data-Driven modeling of COVID-19 with continuous time Dynamic Mode Decompositions and other approaches”, 2021-2024. co-PI: Kramer, A., PI: J. Rosenfeld. ($859,145 with $340,000 to Kramer). • Under consideration – National Science Foundation, Macrosystems Biology and Neon-enabled Science, “Collaborative Research: MRA: The Paradox of Mosquito Macrosystems: Homogenizing communities and diverging populations in urbanizing landscapes”, 2021-2024. co-PI: Kramer, A., PI: Shannon LaDeau (Cary Institute of Ecosystem Studies). -
Understanding the Ecology of Extinction: Are We Close to the Critical Threshold?
Ann. Zool. Fennici 40: 71–80 ISSN 0003-455X Helsinki 30 April 2003 © Finnish Zoological and Botanical Publishing Board 2003 Understanding the ecology of extinction: are we close to the critical threshold? Tim G. Benton Institute of Biological Sciences, University of Stirling, FK9 4LA, UK (e-mail: [email protected]) Received 25 Nov. 2002, revised version received 20 Jan. 2003, accepted 21 Jan. 2003 Benton, T. G. 2003: Understanding the ecology of extinction: are we close to the critical threshold? — Ann. Zool. Fennici 40: 71–80. How much do we understand about the ecology of extinction? A review of recent lit- erature, and a recent conference in Helsinki gives a snapshot of the “state of the art”*. This “snapshot” is important as it highlights what we currently know, the tools avail- able for studying the process of extinction, its ecological correlates, and the theory concerning extinction thresholds. It also highlights that insight into the ecology of extinction can come from areas as diverse as the study of culture, the fossil record and epidemiology. Furthermore, it indicates where the gaps in knowledge and understand- ing exist. Of particular note is the need either to generate experimental data, or to make use of existing empirical data — perhaps through meta-analyses, to test general theory and guide its future development. Introduction IUCNʼs 2002 Red List, a total of 11 167 species are currently known to be threatened (http:// Few would argue that managing natural popu- www.redlist.org/info/tables/table1.html), though lations and their habitats is one of the greatest this is a gross underestimate of the true value, as, challenges for humans in the 21st century. -
The Impact of Fragmented Habitat's Size and Shape on Populations
Math. Model. Nat. Phenom. Vol. 11, No. 4, 2016, pp. 5–15 DOI: 10.1051/mmnp/201611402 The Impact of Fragmented Habitat’s Size and Shape on Populations with Allee Effect W. G. Alharbi, S. V. Petrovskii ∗ Department of Mathematics, University of Leicester, University Road, Leicester LE1 7RH, UK Abstract. This study aims to explore the ways in which population dynamics are affected by the shape and size of fragmented habitats. Habitat fragmentation has become a key concern in ecology over the past 20 years as it is thought to increase the threat of extinction for a number of plant and animal species; particularly those close to the fragment edge. In this study, we consider this issue using mathematical modelling and computer simulations in several domains of various shape and with different strength of the Allee effect. A two-dimensional reaction-diffusion equation (taking the Allee effect into account) is used as a model. Extensive simulations are performed in order to determine how the boundaries impact the population persistence. Our results indicate the following: (i) for domains of simple shape (e.g. rectangle), the effect of the critical patch size (amplified by the Allee effect) is similar to what is observed in 1D space, in particular, the likelihood of population survival is determined by the interplay between the domain size and thee strength of the Allee effect; (ii) in domains of complicated shape, for the population to survive, the domain area needs to be larger than the area of the corresponding rectangle. Hence, it can be concluded that domain size and shape both have crucial effect on population survival. -
Bottom-Up and Top-Down Control of Dispersal Across Major Organismal Groups: a Coordinated Distributed Experiment
bioRxiv preprint doi: https://doi.org/10.1101/213256; this version posted November 2, 2017. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC 4.0 International license. Bottom-up and top-down control of dispersal across major organismal groups: a coordinated distributed experiment Emanuel A. Fronhofer1;2;∗, Delphine Legrand4, Florian Altermatt1;2, Armelle Ansart3, Simon Blanchet4;5, Dries Bonte6, Alexis Chaine4;7, Maxime Dahirel3;6, Frederik De Laender8, Jonathan De Raedt8;9, Lucie di Gesu5, Staffan Jacob10, Oliver Kaltz11, Estelle Laurent10, Chelsea J. Little1;2, Luc Madec3, Florent Manzi11, Stefano Masier6, Felix Pellerin5, Frank Pennekamp2, Nicolas Schtickzelle10, Lieven Therry4, Alexandre Vong4, Laurane Winandy5 and Julien Cote5 1 Eawag: Swiss Federal Institute of Aquatic Science and Technology, Department of Aquatic Ecology, Uberlandstrasse¨ 133, CH-8600 D¨ubendorf, Switzerland 2 Department of Evolutionary Biology and Environmental Studies, University of Zurich, Winterthur- erstrasse 190, CH-8057 Z¨urich, Switzerland 3 Universit´eRennes 1, Centre National de la Recherche Scientifique (CNRS), UMR6553 EcoBio, F- 35042 Rennes cedex, France 4 Centre National de la Recherche Scientifique (CNRS), Universit´ePaul Sabatier, UMR5321 Station d'Ecologie Th´eoriqueet Exp´erimentale (UMR5321), 2 route du CNRS, F-09200 Moulis, France. 5 Centre National de la Recherche Scientifique (CNRS), -
A Theoretical and Experimental Study of Allee Effects
W&M ScholarWorks Dissertations, Theses, and Masters Projects Theses, Dissertations, & Master Projects 2003 A theoretical and experimental study of Allee effects Joanna Gascoigne College of William and Mary - Virginia Institute of Marine Science Follow this and additional works at: https://scholarworks.wm.edu/etd Part of the Ecology and Evolutionary Biology Commons, Fresh Water Studies Commons, and the Oceanography Commons Recommended Citation Gascoigne, Joanna, "A theoretical and experimental study of Allee effects" (2003). Dissertations, Theses, and Masters Projects. Paper 1539616659. https://dx.doi.org/doi:10.25773/v5-qwvk-b742 This Dissertation is brought to you for free and open access by the Theses, Dissertations, & Master Projects at W&M ScholarWorks. It has been accepted for inclusion in Dissertations, Theses, and Masters Projects by an authorized administrator of W&M ScholarWorks. For more information, please contact [email protected]. A THEORETICAL AND EXPERIMENTAL STUDY OF ALLEE EFFECTS A Dissertation Presented to The Faculty of the School of Marine Science The College of William and Mary in Virginia In Partial Fulfillment of the Requirements for the Degree of Doctor of Philosophy by Joanna Gascoigne 2003 Reproduced with permission of the copyright owner. Further reproduction prohibited without permission. APPROVAL SHEET This dissertation is submitted in partial fulfillment of the requirements for the degree of Doctor of Philosophy Joanna/Gascoigne Approved August 2003 Romuald N. Lipcius"Ph.D. Committee Chairman/Advisor L Rogar Mann, Ph.D. Mark R. Patterson, Ph.D. 1 Shandelle M. Henson, Ph.D Andrews University Berrien Springs, MI Callum Roberts, Ph.D. University of York, UK Craig Dahlgren, Ph.D.