14 Genetics of Small Populations: the Case of the Laysan Finch
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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. -
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). -
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. -
Apapane (Himatione Sanguinea)
The Birds of North America, No. 296, 1997 STEVEN G. FANCY AND C. JOHN RALPH 'Apapane Himatione sanguinea he 'Apapane is the most abundant species of Hawaiian honeycreeper and is perhaps best known for its wide- ranging flights in search of localized blooms of ō'hi'a (Metrosideros polymorpha) flowers, its primary food source. 'Apapane are common in mesic and wet forests above 1,000 m elevation on the islands of Hawai'i, Maui, and Kaua'i; locally common at higher elevations on O'ahu; and rare or absent on Lāna'i and Moloka'i. density may exceed 3,000 birds/km2 The 'Apapane and the 'I'iwi (Vestiaria at times of 'ōhi'a flowering, among coccinea) are the only two species of Hawaiian the highest for a noncolonial honeycreeper in which the same subspecies species. Birds in breeding condition occurs on more than one island, although may be found in any month of the historically this is also true of the now very rare year, but peak breeding occurs 'Ō'ū (Psittirostra psittacea). The highest densities February through June. Pairs of 'Apapane are found in forests dominated by remain together during the breeding 'ōhi'a and above the distribution of mosquitoes, season and defend a small area which transmit avian malaria and avian pox to around the nest, but most 'Apapane native birds. The widespread movements of the 'Apapane in response to the seasonal and patchy distribution of ' ōhi'a The flowering have important implications for disease Birds of transmission, since the North 'Apapane is a primary carrier of avian malaria and America avian pox in Hawai'i. -
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. -
COULD R SELECTION ACCOUNT for the AFRICAN PERSONALITY and LIFE CYCLE?
Person. individ.Diff. Vol. 15, No. 6, pp. 665-675, 1993 0191-8869/93 S6.OOf0.00 Printedin Great Britain.All rightsreserved Copyright0 1993Pergamon Press Ltd COULD r SELECTION ACCOUNT FOR THE AFRICAN PERSONALITY AND LIFE CYCLE? EDWARD M. MILLER Department of Economics and Finance, University of New Orleans, New Orleans, LA 70148, U.S.A. (Received I7 November 1992; received for publication 27 April 1993) Summary-Rushton has shown that Negroids exhibit many characteristics that biologists argue result from r selection. However, the area of their origin, the African Savanna, while a highly variable environment, would not select for r characteristics. Savanna humans have not adopted the dispersal and colonization strategy to which r characteristics are suited. While r characteristics may be selected for when adult mortality is highly variable, biologists argue that where juvenile mortality is variable, K character- istics are selected for. Human variable birth rates are mathematically similar to variable juvenile birth rates. Food shortage caused by African drought induce competition, just as food shortages caused by high population. Both should select for K characteristics, which by definition contribute to success at competition. Occasional long term droughts are likely to select for long lives, late menopause, high paternal investment, high anxiety, and intelligence. These appear to be the opposite to Rushton’s r characteristics, and opposite to the traits he attributes to Negroids. Rushton (1985, 1987, 1988) has argued that Negroids (i.e. Negroes) were r selected. This idea has produced considerable scientific (Flynn, 1989; Leslie, 1990; Lynn, 1989; Roberts & Gabor, 1990; Silverman, 1990) and popular controversy (Gross, 1990; Pearson, 1991, Chapter 5), which Rushton (1989a, 1990, 1991) has responded to. -
Nomenclature of the Laysan Honeycreeper Himatione [Sanguinea] Fraithii
Peter Pyle 116 Bull. B.O.C. 2011 131(2) Nomenclature of the Laysan Honeycreeper Himatione [sanguinea] fraithii by Peter Pyle Received 21 May 2010 The Apapane Himatione sanguinea is the most abundant extant species of Hawaiian finch (Fringillidae, Drepanidinae) (Pratt 2005, Pyle & Pyle 2009). It occurs throughout high islands of the south-east Hawaiian Islands, where it shows little to no inter-island variation. On Laysan Island, Northwestern Hawaiian Islands, a resident Himatione was first encountered on 3 April 1828 by the naturalist C. Isenbeck (von Kittlitz 1834) and named much later from specimens collected by H. Palmer and G. Munro in June 1891 (Rothschild 1892). While Palmer and Munro were on Laysan they were assisted by George D. Freeth, manager of a guano-mining operation there and an amateur naturalist. In acknowledgement, Rothschild named the new bird Himatione fraithii, based evidently on a miscommunication from Palmer or Munro or an erroneous assumption concerning the spelling of Freeth’s name, which is not mentioned in the description. This taxon, widely known as the Laysan Honeyeater and, later, the Laysan Honeycreeper, became extinct in 1923 (Ely & Clapp 1975, A. Wetmore in Olson 1996). Walter Rothschild was a well-known British zoologist with an avid interest in the birdlife of islands (Rothschild 1983, Olson 2008). He had sent Palmer and other collectors to procure specimens from the Hawaiian Islands in 1890–93 for his private museum in Tring, England. Based upon this collection he published Avifauna of Laysan and the neighbouring islands, with a complete history to date of the birds of the Hawaiian possession in three parts, Part I in August 1893, Part II in November 1893 and Part III in December 1900 (Rothschild 1893– 1900; see Olson 2003). -
The Basics of Population Dynamics Greg Yarrow, Professor of Wildlife Ecology, Extension Wildlife Specialist
The Basics of Population Dynamics Greg Yarrow, Professor of Wildlife Ecology, Extension Wildlife Specialist Fact Sheet 29 Forestry and Natural Resources Revised May 2009 All forms of wildlife, regardless of the species, will respond to changes in density dependence. These concepts are important for landowners habitat, hunting or trapping, and weather conditions with fluctuations and natural resource managers to understand when making decisions in animal numbers. Most landowners have probably experienced affecting wildlife on private land. changes in wildlife abundance from year to year without really knowing why there are fewer individuals in some years than others. How Many Offspring Can Wildlife Have? In many cases, changes in abundance are normal and to be expected. Most people realize that some wildlife species can produce more The purpose of the information presented here is to help landowners offspring than others. Bobwhite quail are genetically programmed to lay understand why animal numbers may vary or change. While a number an average of 14 eggs per clutch. Each species has a maximum genetic of important concepts will be discussed, one underlying theme should reproductive potential or biotic potential. always be remembered. Regardless of whether property is managed or not in any given year, there is always some change in the habitat, Biotic potential describes a population’s ability to grow over time however small. Wildlife must adjust to this change and, therefore, no through reproduction. Most bat species are likely to produce one population is ever the same from one year to the next. offspring per year. In contrast, a female cottontail rabbit will have a litter size of approximately 5. -
THE FORAGING ECOLOGY, HABITAT USE, and POPULATION DYNAMICS of the LAYSAN TEAL (Anas Laysanensis)
THE FORAGING ECOLOGY, HABITAT USE, AND POPULATION DYNAMICS OF THE LAYSAN TEAL (Anas laysanensis) by Michelle H. Reynolds A dissertation submitted in partial fulfillment of the requirements for the degree of Doctor of Philosophy in Biology Virginia Polytechnic Institute and State University Approved by Jeffery R. Walters, Committee chair Curtis Adkisson, Committee member E. F. Benfield, Committee member James Fraser, Committee member William Steiner, Committee member Defense date October 31, 2002 Blacksburg, VA Keywords: Anas laysanensis, foraging ecology, habitat use, population estimate, survival, island waterfowl, Laysan Island THE FORAGING ECOLOGY, HABITAT USE, AND POPULATION DYNAMICS OF THE LAYSAN TEAL (Anas laysanensis) Michelle H. Reynolds ABSTRACT The Laysan teal, an endangered species, is restricted to a single population on Laysan Island, a remote atoll of the Hawaiian archipelago. Little is known of the Laysan teal’s ecology, therefore, I examined food habits, habitat use, and population dynamics. These aspects of its ecology are fundamental to the species management and conservation. I described diel and nocturnal habitat use, home range, and foraging with radio telemetry in 1998-2000. Most individuals showed strong site fidelity during the tracking period, but habitat selection varied between individuals. Mean home range size was 9.78 ha (SE 2.6) using the fixed kernel estimator (95% kernel; 15 birds with >25 locations). Foraging was strongly influenced by time of day: birds spent only 4% of their time foraging in the day, but spent 45% of their time foraging at night. Time activity budgets from the island’s four habitat zones indicated that the coastal zone was rarely used for foraging. -
Billing Code 4333–15 DEPARTMENT of THE
This document is scheduled to be published in the Federal Register on 11/28/2018 and available online at https://federalregister.gov/d/2018-25634, and on govinfo.gov Billing Code 4333–15 DEPARTMENT OF THE INTERIOR Fish and Wildlife Service 50 CFR Part 10 [Docket No. FWS–HQ–MB–2018–0047; FXMB 12320900000//189//FF09M29000] RIN 1018–BC67 General Provisions; Revised List of Migratory Birds AGENCY: Fish and Wildlife Service, Interior. ACTION: Proposed rule. SUMMARY: We, the U.S. Fish and Wildlife Service (Service), propose to revise the List of Migratory Birds protected by the Migratory Bird Treaty Act (MBTA) by both adding and removing species. Reasons for the changes to the list include adding species based on new taxonomy and new evidence of natural occurrence in the United States or U.S. territories, removing species no longer known to occur within the United States or U.S. territories, and changing names to conform to accepted use. The net increase of 59 species (66 added and 7 removed) would bring the total number of species protected by the MBTA to 1,085. We regulate the taking, possession, transportation, sale, purchase, barter, exportation, and importation of migratory birds. An accurate and up-to-date list of species protected by the MBTA is essential for public notification and regulatory purposes. DATES: We will accept comments received or postmarked on or before [INSERT DATE 60 DAYS AFTER DATE OF PUBLICATION IN THE FEDERAL REGISTER]. Comments submitted electronically using the Federal eRulemaking Portal (see ADDRESSES, below) must be received by 11:59 p.m. -
Endangered Millerbird Population on Hawai'i's Laysan Island Doubles To
NEWS RELEASE CONTACT FOR IMMEDIATE RELEASE USFWS: Ken Foote 808-792-9535 or 808-282-9442 . June 24, 2013 American Bird Conservancy (ABC): Bob Johns 202-234-7181 or Chris Farmer 808-987-1779 Endangered Millerbird Population on Hawai‘i's Laysan Island Doubles to More Than 100 Historic Translocation Efforts Securing Future for Species (Honolulu, Hawaii, June 24, 2013) The latest count of endangered Millerbirds on Hawai‘i's Laysan Island found that the bird’s population has doubled – to over 100 – from the original total of 50 translocated birds released by the U.S. Fish and Wildlife Service (FWS), American Bird Conservancy (ABC), and others in 2011 and 2012. The translocation program was initiated several years ago, when all of the world’s remaining Millerbirds -- between 400 and 600 at that time -- were limited to the island of Nihoa in the remote Northwestern Hawaiian Islands. By moving some of the birds to a second island, Laysan, approximately 650 miles northwest of Nihoa, the Millerbird team hoped to reduce the high risk of extinction from catastrophes such as severe storms, droughts, fires, and accidental introduction of alien species such as rats, mosquitos, and/or diseases such as avian pox and malaria. Establishing a second population reduces this risk by increasing the population size and distribution. The translocation of the Nihoa Millerbird to Laysan also serves another purpose. It re-establishes the link in the ecosystem that was lost about 100 years ago when the closely-related Laysan Millerbird went extinct. In the highly successful first phase of the translocation effort, 24 Millerbirds were moved 650 miles from Nihoa to Laysan in September 2011.