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Effective Population Sizes and Adaptive Genetic Variation in a Captive Bird Population
bioRxiv preprint doi: https://doi.org/10.1101/307728; this version posted June 19, 2018. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity.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-ND 4.0 International license. Effective population sizes and adaptive genetic variation in a captive bird population 1,2∔ 1 1 3 Giridhar Athrey , Nikolas Faust , Anne-Sophie Charlotte Hieke , I. Lehr Brisbin 1 Department of Poultry Science, Texas A&M University, 2472 TAMU, College Station, TX, 77843. 2 Faculty of Ecology and Evolutionary Biology, Texas A&M University, 2472 TAMU, College Station, TX, 77843. 3 University of Georgia/Savannah River Ecology Lab, Drawer E, Aiken, SC, 29802. ∔Corresponding author: Giridhar Athrey, Department of Poultry Science, Texas A&M University, 2472 TAMU, College Station, TX, 77843. Email: [email protected] 1 bioRxiv preprint doi: https://doi.org/10.1101/307728; this version posted June 19, 2018. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity.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-ND 4.0 International license. Abstract Captive populations are considered a key component of ex situ conservation programs. Research on multiple taxa have shown the differential success of maintaining demographic versus genetic stability and viability in captive populations. In typical captive populations, usually founded by few or related individuals, genetic diversity can be lost and inbreeding can accumulate rapidly, calling into question their ultimate utility for release into the wild. -
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. -
Conservation and Management of Forest
Journal of Tropical Forest Science 11(1):286-302 (1999) CONSERVATIO MANAGEMEND NAN FORESF TO T GENETIC RESOURCES Christel Palmberg-Lerche Forest Resources Development Service, Forest Resources Division, FAO, Rome, Italy Received June 1998___________________________________________________ PALMBERG-LERCHE, C. 1999. Conservation and management of forest genetic resources papee .Th r reviews available strategie conservatione th r sfo , management, enhancemen sustainabld an t e utilisatio foresf no t genetic resources linkagee th d ,an s of genetic conservation with the management of forests, tree improvement and breeding. International co-operation, co-ordination of efforts and possible future strategies of action are briefly mentioned. The paper concludes that efforts to conserv enhancd ean e forest genetic resource present-dar sfo futurd yan e uses must e "tripod basee th b n f do managemeno " protectef o t d areas managemene th , f o t productive forests, and the management of breeding populations. It stresses that the key to success will lie in the development of programmes which harmonise conservatio sustainabld nan e utilisatio foresf no t genetic resources withi mosaina f co lan optionse dus , includin gstrona g elemen activf to e gene management. Key words: Forest biological diversit y- fores t genetic resource - sconservatio f no forest genetic resources - tree improvement - forest seed procurement - sustainable forest management PALMBERG-LERCHE, C. 1999. Pemuliharaan dan pengurusan sumber-sumber genetik hutan. Artike mengulai lin s mengenai strategi yan baga gad i pemuliharaan, pengurusan, peningkatan dan penggunaan secara berkekalan sumber-sumber genetik hutan, serta kaitan pemuliharaan genetik dengan pengurusan hutan, pembaikan pokok dan pembiakbaikan pokok. Kerjasama antarabangsa, penyelarasan usaha dan strategi tindakan pada masa hadapan juga dinyatakan secara ringkas. -
Species Knowledge Review: Shrill Carder Bee Bombus Sylvarum in England and Wales
Species Knowledge Review: Shrill carder bee Bombus sylvarum in England and Wales Editors: Sam Page, Richard Comont, Sinead Lynch, and Vicky Wilkins. Bombus sylvarum, Nashenden Down nature reserve, Rochester (Kent Wildlife Trust) (Photo credit: Dave Watson) Executive summary This report aims to pull together current knowledge of the Shrill carder bee Bombus sylvarum in the UK. It is a working document, with a view to this information being reviewed and added when needed (current version updated Oct 2019). Special thanks to the group of experts who have reviewed and commented on earlier versions of this report. Much of the current knowledge on Bombus sylvarum builds on extensive work carried out by the Bumblebee Working Group and Hymettus in the 1990s and early 2000s. Since then, there have been a few key studies such as genetic research by Ellis et al (2006), Stuart Connop’s PhD thesis (2007), and a series of CCW surveys and reports carried out across the Welsh populations between 2000 and 2013. Distribution and abundance Records indicate that the Shrill carder bee Bombus sylvarum was historically widespread across southern England and Welsh lowland and coastal regions, with more localised records in central and northern England. The second half of the 20th Century saw a major range retraction for the species, with a mixed picture post-2000. Metapopulations of B. sylvarum are now limited to five key areas across the UK: In England these are the Thames Estuary and Somerset; in South Wales these are the Gwent Levels, Kenfig–Port Talbot, and south Pembrokeshire. The Thames Estuary and Gwent Levels populations appear to be the largest and most abundant, whereas the Somerset population exists at a very low population density, the Kenfig population is small and restricted. -
Diversity and Population Genetic Structure of the Wax Palm Ceroxylon
bioRxiv preprint doi: https://doi.org/10.1101/443960; this version posted October 15, 2018. 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 4.0 International license. 1 Diversity and population genetic structure of the wax palm 2 Ceroxylon quindiuense in the Colombian Coffee Region 3 Natalia González-Rivillas1-2, Adriana Bohórquez3, Janeth Patricia Gutierrez3, Víctor Hugo García- 4 Merchán1-2 5 6 1Grupo de Investigación en Evolución, Ecología y Conservación (EECO), Programa de Biología, 7 Universidad del Quindío, Carrera 15 Calle 12 Norte, Armenia, Quindío, Colombia. 8 2 Grupo de Investigación y Asesoría en Estadística, Universidad del Quindío. 9 3 International Center for Tropical Agriculture (CIAT), Km 17, recta Cali-Palmira, Colombia. 10 11 [email protected] (NGR), [email protected] (AB), [email protected] (JPG) & 12 [email protected] (VHGM). 13 14 The authors mentioned contributed equally to this work. 15 16 Abstract 17 The wax palm from Quindío (Ceroxylon quindiuense) is an icon of the cultural identity of the coffee growing 18 eco-region and of all Colombia. Processes of urbanization, expansion of the agricultural and livestock area, among 19 others, have increased its level of threat. Protecting this palm from extinction is important at an ecological level, given 20 its function as a key species in Andean ecosystems. This work evaluated the diversity and population genetic structure 21 of the wax palm from Quindío in five populations of the Colombian coffee region eco-region (Andean zone) by using 22 ten microsatellite molecular markers. -
Genetic Resources: the Key to Adaptation of Forests to Climate
GENETIC RESOURCES THE KEY TO ADAPTATION OF FORESTS TO CLIMATE CHANGE SCIENCE-TO-POLICY EVENT BRUSSELS, 13 DECEMBER 2019 - RADISSON RED HOTEL, RUE D'IDALIE 35 The aim of this event is to present and discuss the relevance and implications of recent research findings and guidelines for policy and practice. The main focus is the role of forest biodiversity, in particular tree species and genetic diversity for the adaptation of forests to climate change. BACKGROUND Global environmental and land-use changes have considerable and long-lasting impact on forests in Europe, modifying the functioning of forest ecosystems and species interactions, thereby affecting the provision of ecosystem services. Trees are long-lived organisms and thus individual trees and tree populations need to withstand significant and rapid environmental changes over their life span and across generations. The capacity of European forests to adapt to such changes, and to continue to provide essential ecosystem services to the society, depends largely on their diversity at species and intraspecific level. Several ongoing transnational research and implementation initiatives examine the state and resilience of forests under unprecedented global changes. Their findings provide substantial information for existing EU regulatory frameworks and enable to derive new policy recommendations. AGENDA 8.45 - 9.30 - Registration and welcome coffee 9.30 - 10.30 - Presentations of recent findings from the four EU research projects on the conservation and sustainable use of forests and -
Favourable Reference Values Expert Group on Reporting Under the Nature Directives 21 March 2017
Favourable Reference Values Expert group on Reporting under the Nature Directives 21 March 2017 This note includes all the text concerning favourable reference values that is included in the Draft Article 17 Guidelines (version of 8 March). It is presented as a stand-alone paper to give an overview of the proposals and facilitate the discussion at the expert group. 10 March 2017 Draft section on Favourable Reference Values – Article 17 reporting guidelines Section on Favourable Reference Values1 For the Article 17 reporting guidelines Introduction (for both species and habitats) What are favourable reference values? The concept of favourable reference values (FRVs) is derived from definitions in the Directive, particularly the definition of favourable conservation status that relates to the ‘long-term distribution and abundance’ of the populations of species (Article 1i), and for habitats to the ‘long-term natural distribution, structure and functions as well as the long-term survival of its typical species’ in their natural range (Article 1e). This requires that the species is maintaining itself on a long-term basis as a viable component of its natural habitats. Similarly, for habitat types, the Directive requires that the specific structure and functions necessary for its long-term maintenance exist and will continue to exist and that its typical species are in favourable status, i.e. are maintaining themselves on a long- term basis. If Member States do not maintain or restore such a situation, the objective of the Directive is not met. Favourable reference values – ‘range’ for species and habitat types, ‘population’ for species, and ‘area’ for habitat types – are critical in the evaluation of Conservation Status. -
Annual Report
1998Annual Report International Plant Genetic Resources Institute Improving conservation strategies and technologies Understanding the extent and distribution of diversity; supporting collecting of genetic resources; improving ex situ and in situ conservation and developing integrated approaches Increasing the use of plant genetic resources Improving methods of using ex situ conserved germplasm; supporting conservation through use; supporting increased use of diversity in production Managing and communicating information Improving germplasm documentation; supporting SINGER and the Musa germplasm information system; providing technical information; increasing public awareness Addressing socioeconomic and policy issues Determining links between diversity and socioeconomic factors; meeting gender concerns and increasing participation; valuing genetic resources; supporting improved policy-making Conserving and using specific crops Supporting work on Musa (through the INIBAP programme), coconut and cocoa; improving conserva- tion of neglected and underused species; conserving wild relatives of crops Conserving and using forest genetic resources Conserving intraspecific diversity through sustainable use; supporting network development; improv- ing ex situ conservation techniques Working with networks Supporting established regional, crop and thematic networks and helping to develop new ones to strengthen international collaboration Strengthening national systems Supporting improved germplasm management strategies and technologies; providing -
Resource Notes No
RESOURCE NOTES NO. 35 DATE 08/01/00 maintain sufficient genetic diversity DEFINITION: Metapopulation refers Summary within these populations. to two or more local breeding popula- tions which are linked to one another by Recommendations- DISCUSSION: Reproductive capac- dispersal activities of individual animals. ity is, to a large degree, dictated by These populations may have unique BLM Wild Horse the genetic fitness of a population. demographic features (birth and death Generally speaking, the higher the rates) but ultimately may share some and Burro level of genetic diversity, within the genetic material if interbreeding is herd, the greater its long-term repro- occurring between individuals. This Wild Horse and Burro Program Population ductive capacity. Inbreeding, random sharing of genetic material may act to matings (genetic drift), and/or envi- enhance genetic diversity within par- Viability Forum, ronmental catastrophes can all lead to ticipating herds, and as such, these the loss of genetic diversity within the populations should be evaluated as April 21, 1999 population. In most herds, though, one larger metapopulation. by Linda Coates-Markle, genetic resources will tend to be lost Montana/Dakotas Wild Horse slowly over periods of many generations DISCUSSION: A complete popula- (~10 years/generation), and there is tion census of each herd management and Burro Specialist, little imminent risk of inbreeding or area is unrealistic, especially for the larg- Bureau of Land Management, population extinction. Potential nega- er populations (>200 total census Montana State Office tive consequences of reduced diversity, size). However, population size can however, may include reduced foal pro- and should be estimated using reliable duction and survival, as well as reduced scientific techniques. -
RSPB CENTRE for CONSERVATION SCIENCE RSPB CENTRE for CONSERVATION SCIENCE Where Science Comes to Life
RSPB CENTRE FOR CONSERVATION SCIENCE RSPB CENTRE FOR CONSERVATION SCIENCE Where science comes to life Contents Knowing 2 Introducing the RSPB Centre for Conservation Science and an explanation of how and why the RSPB does science. A decade of science at the RSPB 9 A selection of ten case studies of great science from the RSPB over the last decade: 01 Species monitoring and the State of Nature 02 Farmland biodiversity and wildlife-friendly farming schemes 03 Conservation science in the uplands 04 Pinewood ecology and management 05 Predation and lowland breeding wading birds 06 Persecution of raptors 07 Seabird tracking 08 Saving the critically endangered sociable lapwing 09 Saving South Asia's vultures from extinction 10 RSPB science supports global site-based conservation Spotlight on our experts 51 Meet some of the team and find out what it is like to be a conservation scientist at the RSPB. Funding and partnerships 63 List of funders, partners and PhD students whom we have worked with over the last decade. Chris Gomersall (rspb-images.com) Conservation rooted in know ledge Introduction from Dr David W. Gibbons Welcome to the RSPB Centre for Conservation The Centre does not have a single, physical Head of RSPB Centre for Conservation Science Science. This new initiative, launched in location. Our scientists will continue to work from February 2014, will showcase, promote and a range of RSPB’s addresses, be that at our UK build the RSPB’s scientific programme, helping HQ in Sandy, at RSPB Scotland’s HQ in Edinburgh, us to discover solutions to 21st century or at a range of other addresses in the UK and conservation problems. -
FOREST BIODIVERSITY Earth’S Living Treasure
OLOGIC OR BI AL DI Y F VER DA SI L TY A 2 N 2 IO M T a A y N 2 R 0 E 1 T 1 N I FOREST BIODIVERSITY Earth’s Living Treasure INTERNATIONAL DAY FOR BIOLOGICAL DIVERSITY 22 May 2011 FOREST BIODIVERSITY Earth’s Living Treasure Published by the Secretariat of the Convention on Biological Diversity. ISBN: 92-9225-298-4 Copyright © 2010, Secretariat of the Convention on Biological Diversity. The designations employed and the presentation of material in this publication do not imply the expression of any opinion whatsoever on the part of the Secretariat of the Convention on Biological Diversity concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The views reported in this publication do not necessarily represent those of the Convention on Biological Diversity. This publication may be reproduced for educational or non-profit purposes without special permission from the copyright holders, provided acknowledgement of the source is made. The Secretariat of the Convention would appreciate receiving a copy of any publications that use this document as a source. Citation: Secretariat of the Convention on Biological Diversity (2010). Forest Biodiversity—Earth’s Living Treasure. Montreal, 48 pages. For further information, please contact: Secretariat of the Convention on Biological Diversity World Trade Centre 413 St. Jacques Street, Suite 800 Montreal, Quebec, Canada H2Y 1N9 Phone: 1 (514) 288 2220 Fax: 1 (514) 288 6588 E-mail: [email protected] Website: www.cbd.int Design & typesetting: Em Dash Design Cover illustration: Cover illustration: Untitled, 2010. -
Effective Population Sizes and Adaptive Genetic Variation in a Captive Bird Population
Effective population sizes and adaptive genetic variation in a captive bird population Giridhar Athrey1,2, Nikolas Faust1, Anne-Sophie Charlotte Hieke1 and I. Lehr Brisbin3 1 Department of Poultry Science, Texas A&M University, College Station, TX, United States of America 2 Faculty of Ecology and Evolutionary Biology, Texas A&M University, College Station, TX, United States of America 3 Savannah River Ecology Lab, Aiken, SC, United States of America ABSTRACT Captive populations are considered a key component of ex situ conservation programs. Research on multiple taxa has shown the differential success of maintaining demo- graphic versus genetic stability and viability in captive populations. In typical captive populations, usually founded by few or related individuals, genetic diversity can be lost and inbreeding can accumulate rapidly, calling into question their ultimate utility for release into the wild. Furthermore, domestication selection for survival in captive conditions is another concern. Therefore, it is crucial to understand the dynamics of population sizes, particularly the effective population size, and genetic diversity at non- neutral and adaptive loci in captive populations. In this study, we assessed effective population sizes and genetic variation at both neutral microsatellite markers, as well as SNP variants from the MHC-B locus of a captive Red Junglefowl population. This population represents a rare instance of a population with a well-documented history in captivity, following a realistic scenario of chain-of-custody, unlike many captive lab populations. Our analyses, which included 27 individuals comprising the entirety of one captive population show very low neutral and adaptive genetic variation, as well as low effective sizes, which correspond with the known demographic history.