Assisted Colonisation As a Climate Change Adaptation Tool
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Two Colonisation Stages Generate Two Different Patterns of Genetic Diversity Within Native and Invasive Ranges of Ulex Europaeus
Heredity (2013) 111, 355–363 & 2013 Macmillan Publishers Limited All rights reserved 0018-067X/13 www.nature.com/hdy ORIGINAL ARTICLE Two colonisation stages generate two different patterns of genetic diversity within native and invasive ranges of Ulex europaeus B Hornoy1,3, A Atlan1, V Roussel1,4, YM Buckley2 and M Tarayre1 Genetic diversity and the way a species is introduced influence the capacity of populations of invasive species to persist in, and adapt to, their new environment. The diversity of introduced populations affects their evolutionary potential, which is particularly important for species that have invaded a wide range of habitats and climates, such as European gorse, Ulex europaeus. This species originated in the Iberian peninsula and colonised Europe in the Neolithic; over the course of the past two centuries it was introduced to, and has become invasive in, other continents. We characterised neutral genetic diversity and its structure in the native range and in invaded regions. By coupling these results with historical data, we have identified the way in which gorse populations were introduced and the consequences of introduction history on genetic diversity. Our study is based on the genotyping of individuals from 18 populations at six microsatellite loci. As U. europaeus is an allohexaploid species, we used recently developed tools that take into account genotypic ambiguity. Our results show that genetic diversity in gorse is very high and mainly contained within populations. We confirm that colonisation occurred in two stages. During the first stage, gorse spread out naturally from Spain towards northern Europe, losing some genetic diversity. During the second stage, gorse was introduced by humans into different regions of the world, from northern Europe. -
Critically Endangered - Wikipedia
Critically endangered - Wikipedia Not logged in Talk Contributions Create account Log in Article Talk Read Edit View history Critically endangered From Wikipedia, the free encyclopedia Main page Contents This article is about the conservation designation itself. For lists of critically endangered species, see Lists of IUCN Red List Critically Endangered Featured content species. Current events A critically endangered (CR) species is one which has been categorized by the International Union for Random article Conservation status Conservation of Nature (IUCN) as facing an extremely high risk of extinction in the wild.[1] Donate to Wikipedia by IUCN Red List category Wikipedia store As of 2014, there are 2464 animal and 2104 plant species with this assessment, compared with 1998 levels of 854 and 909, respectively.[2] Interaction Help As the IUCN Red List does not consider a species extinct until extensive, targeted surveys have been About Wikipedia conducted, species which are possibly extinct are still listed as critically endangered. IUCN maintains a list[3] Community portal of "possibly extinct" CR(PE) and "possibly extinct in the wild" CR(PEW) species, modelled on categories used Recent changes by BirdLife International to categorize these taxa. Contact page Contents Tools Extinct 1 International Union for Conservation of Nature definition What links here Extinct (EX) (list) 2 See also Related changes Extinct in the Wild (EW) (list) 3 Notes Upload file Threatened Special pages 4 References Critically Endangered (CR) (list) Permanent -
US Fish & Wildlife Service Seabird Conservation Plan—Pacific Region
U.S. Fish & Wildlife Service Seabird Conservation Plan Conservation Seabird Pacific Region U.S. Fish & Wildlife Service Seabird Conservation Plan—Pacific Region 120 0’0"E 140 0’0"E 160 0’0"E 180 0’0" 160 0’0"W 140 0’0"W 120 0’0"W 100 0’0"W RUSSIA CANADA 0’0"N 0’0"N 50 50 WA CHINA US Fish and Wildlife Service Pacific Region OR ID AN NV JAP CA H A 0’0"N I W 0’0"N 30 S A 30 N L I ort I Main Hawaiian Islands Commonwealth of the hwe A stern A (see inset below) Northern Mariana Islands Haw N aiian Isla D N nds S P a c i f i c Wake Atoll S ND ANA O c e a n LA RI IS Johnston Atoll MA Guam L I 0’0"N 0’0"N N 10 10 Kingman Reef E Palmyra Atoll I S 160 0’0"W 158 0’0"W 156 0’0"W L Howland Island Equator A M a i n H a w a i i a n I s l a n d s Baker Island Jarvis N P H O E N I X D IN D Island Kauai S 0’0"N ONE 0’0"N I S L A N D S 22 SI 22 A PAPUA NEW Niihau Oahu GUINEA Molokai Maui 0’0"S Lanai 0’0"S 10 AMERICAN P a c i f i c 10 Kahoolawe SAMOA O c e a n Hawaii 0’0"N 0’0"N 20 FIJI 20 AUSTRALIA 0 200 Miles 0 2,000 ES - OTS/FR Miles September 2003 160 0’0"W 158 0’0"W 156 0’0"W (800) 244-WILD http://www.fws.gov Information U.S. -
Re-Thinking Impacts of Island Colonisation
Kerry-Anne Mairs (2007) Islands and human impact... University of Edinburgh, Unpublished PhD Thesis. 398 pp. Chapter 3: Island contexts Chapter 3 Island contexts Introduction Perhaps the thing that most distinguishes islands, at least oceanic islands… is their extreme vulnerability or susceptibility to disturbance (Fosberg 1963: 559). This chapter examines the wider context of island research as introduced in the framework in Figure 1.5 with regards to the notion that islands represent a model system, from which globally occurring processes can be understood. The chapter aims to provide a brief overview of islands and what characterises them, both as islands, and as locations from which to explore human-environment interactions. Recent examples of human-environment research in some Pacific islands, where wide ranging archaeological and comparative-led research has been carried out, are also reviewed. From this research, hypotheses regarding human impacts on environments can be developed with regards to the Faroe Islands. Island contexts as models for human impact and global change The smaller, more manageable spatial scale and insularity of island environments and societies, has made islands (particularly remote islands) popular field locations for research in a variety of disciplines, including biology, ecology, biogeography, ethnography and more recently, environmental archaeology. Islands have been referred to as outdoor laboratories (Kirch 1997a, Fitzhugh and Hunt 1997), where human-environment research can be approached from a comparative -
Gunnison Sage Grouse Biological Opinion
United States Department of Agriculture December 22, 2014 Endangered Species Act (ESA) Section 7 Programmatic Consultation for the Gunnison Sage-Grouse Attached is the regionally developed Biological Opinion for the Gunnison sage-grouse (Centrocercus minimus) in the States of Colorado and Utah. This Opinion takes effect concurrent with the effective date of the grouse’s listing as a threatened species on December 22nd, 2014. This Opinion replaces the 2010 SGI Conference Report for the Gunnison sage-grouse. Continue to use the 2010 SGI Conference Report for the Greater sage-grouse. Section 1.2 describes the Conversion of the Conference Report to a Biological Opinion. Document expires on 07/30/2040. Citation: DOI, 2014. The U.S. Fish and Wildlife Service’s Biological Opinion for the Natural Resources Conservation Services’ USDA Farm Bill programs, including the Sage Grouse Initiative, and associated procedures, conservation practices, and conservation measures for the Gunnison sage-grouse (Centrocercus minimus). Denver, Colorado. Contact Chanda Pettie, State Biologist, at 720-544-2804 or [email protected] for information regarding the content of this notice. FOTG, Section II NRCS, CO SEC, T&E December 2014 BIOLOGICAL OPINION 1.0 INTRODUCTION In accordance with section 7 of the Endangered Species Act of 1973 as amended (16 U.S.C. 1531 et seq. [ESA],), and the Interagency Cooperation Regulations (50 CFR 402), this document transmits the United States Fish and Wildlife Service's (Service) Biological Opinion (Opinion) for the Natural Resources Conservation Services’ (NRCS) USDA Farm Bill programs, including the Sage Grouse Initiative (SGI), and associated procedures, conservation practices, and conservation measures for the Gunnison sage-grouse (Centrocercus minimus). -
The Great White Egret in Europe: Population Increase and Range Expansion Since 1980 Łukasz Ławicki
The Great White Egret in Europe: population increase and range expansion since 1980 Łukasz Ławicki Abstract The European breeding and non-breeding populations of the Great White Egret Ardea alba have increased dramatically since 1980. During this period the breeding range has expanded to the north and west, and the species has nested for the first time in 13 countries, including Sweden and England. Since 2000 there has also been a substantial increase in the wintering populations in western and central Europe, where it formerly wintered in small numbers or only occasionally, with flocks of several hundred individuals reported from some countries. Changes in the availability of foraging habitat and food, the cessation of persecution and related human-induced mortality, improved legal protection, and climate change have probably all played a part in the patterns described here. The feathers of the male are much sought after as decorations, which in the East are a sign of great dignity and highly prized; formerly they were used in Europe as ornamentation by knights and the fair sex. (Taczanowski 1882) he Great White Egret Ardea alba is a Historical status and distribution cosmopolitan species, found on all It seems likely that Great White Egrets were Tcontinents except Antarctica in a common in central Europe in the past. In variety of wetland habitats where food (espe - Poland, for example, they were commonly cially fish) is available: marshes, river flood - hunted using Saker Falcons Falco cherrug plains, the margins of lakes, ponds and (Stajszczyk 2011). Historically, a core area of reservoirs, coasts, estuaries and mangrove the population was probably present-day thickets (Voisin 1991; Kushlan & Hancock Ukraine and Hungary. -
IUCN Red List of Threatened Species™ to Identify the Level of Threat to Plants
Ex-Situ Conservation at Scott Arboretum Public gardens and arboreta are more than just pretty places. They serve as an insurance policy for the future through their well managed ex situ collections. Ex situ conservation focuses on safeguarding species by keeping them in places such as seed banks or living collections. In situ means "on site", so in situ conservation is the conservation of species diversity within normal and natural habitats and ecosystems. The Scott Arboretum is a member of Botanical Gardens Conservation International (BGCI), which works with botanic gardens around the world and other conservation partners to secure plant diversity for the benefit of people and the planet. The aim of BGCI is to ensure that threatened species are secure in botanic garden collections as an insurance policy against loss in the wild. Their work encompasses supporting botanic garden development where this is needed and addressing capacity building needs. They support ex situ conservation for priority species, with a focus on linking ex situ conservation with species conservation in natural habitats and they work with botanic gardens on the development and implementation of habitat restoration and education projects. BGCI uses the IUCN Red List of Threatened Species™ to identify the level of threat to plants. In-depth analyses of the data contained in the IUCN, the International Union for Conservation of Nature, Red List are published periodically (usually at least once every four years). The results from the analysis of the data contained in the 2008 update of the IUCN Red List are published in The 2008 Review of the IUCN Red List of Threatened Species; see www.iucn.org/redlist for further details. -
Local Extinction and Colonisation in Native and Exotic Fish in Relation to Changes in Land
Local extinction and colonisation in native and exotic fish in relation to changes in land use Dorothée Kopp, Jordi Figuerola, Arthur Compin, Frédéric Santoul, Régis Céréghino To cite this version: Dorothée Kopp, Jordi Figuerola, Arthur Compin, Frédéric Santoul, Régis Céréghino. Local extinction and colonisation in native and exotic fish in relation to changes in land use. Marine and Freshwater Research, CSIRO Publishing, 2011, vol. 63, pp. 175-179. 10.1071/MF11142. hal-00913592 HAL Id: hal-00913592 https://hal.archives-ouvertes.fr/hal-00913592 Submitted on 4 Dec 2013 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Open Archive TOULOUSE Archive Ouverte (OATAO) OATAO is an open access repository that collects the work of Toulouse researchers and makes it freely available over the web where possible. This is an author-deposited version published in : http://oatao.univ-toulouse.fr/ Eprints ID : 10194 To link to this article : DOI:10.1071/MF11142 URL : http://dx.doi.org/10.1071/MF11142 To cite this version : Kopp, Dorothée and Figuerola, Jordi and Compin, Arthur and Santoul, Frédéric and Céréghino, Régis. Local extinction and colonisation in native and exotic fish in relation to changes in land use. -
Species at Risk Act
Consultation on Amending the List of Species under the Species at Risk Act Terrestrial Species November 2011 Information contained in this publication or product may be reproduced, in part or in whole, and by any means, for personal or public non-commercial purposes, without charge or further permission, unless otherwise specified. You are asked to: Exercise due diligence in ensuring the accuracy of the materials reproduced; Indicate both the complete title of the materials reproduced, as well as the author organization; and Indicate that the reproduction is a copy of an official work that is published by the Government of Canada and that the reproduction has not been produced in affiliation with or with the endorsement of the Government of Canada. Commercial reproduction and distribution is prohibited except with written permission from the Government of Canada’s copyright administrator, Public Works and Government Services of Canada (PWGSC). For more information, please contact PWGSC at 613-996-6886 or at [email protected]. Cover photo credits: Olive Clubtail © Jim Johnson Peacock Vinyl Lichen © Timothy B. Wheeler Cerulean Warbler © Carl Savignac Title page photo credits: Background photo: Dune Tachinid Fly habitat © Sydney Cannings Foreground, large photo: Dwarf Lake Iris © Jessie M. Harris Small photos, left to right: Butler’s Gartersnake © Daniel W.A. Noble Hungerford’s Crawling Water Beetle © Steve Marshall Barn Swallow © Gordon Court Spring Salamander © David Green Available also on the Internet. ISSN: 1710-3029 Cat. no.: EN1-36/2011E-PDF © Her Majesty the Queen in Right of Canada, represented by the Minister of the Environment, 2011 Consultation on Amending the List of Species under the Species at Risk Act Terrestrial Species November 2011 Please submit your comments by February 8, 2012, for terrestrial species undergoing normal consultations and by November 8, 2012, for terrestrial species undergoing extended consultations. -
Acacia in THIS ISSUE Dacacia the Name Acacia Comes This Issue of Seed Notes from the Greek Acacia, Ace Will Cover the Genus Or Acis Meaning a Point Or Acacia
No. 9 Acacia IN THIS ISSUE DAcacia The name Acacia comes This issue of Seed Notes from the Greek acacia, ace will cover the genus or acis meaning a point or Acacia. thorn, or from acazo, to D Description sharpen, although this name applies more to African than D Geographic Australian species (Australian distribution and Acacia have no thorns or habitat larger prickles, unlike those D Reproductive biology that are native to Africa). D Seed collection Many species of Acacia, or wattles as they are commonly D Phyllodes and flowers of Acacia aprica. Photo – Andrew Crawford Seed quality called in Australia, are valuable assessment for a range of uses, in D Seed germination particular as garden plants. Description In Australia, Acacia (family is modified to form a leaf- D Recommended reading They are also used for amenity plantings, windbreaks, shade DMimosaceae) are woody like structure or phyllode. trees, groundcovers, erosion plants that range from These phyllodes may be flat and salinity control. The timber prostrate under-shrubs to or terete. Some species do of some Acacia is very hard tall trees. Acacia flowers are not have phyllodes and the and is ideal for fence posts small, regular and usually flattened stems or cladodes (e.g. A. saligna or jam). Other bisexual. They occur in spikes act as leaves. Foliage can Acacia species are used to or in globular heads and vary from blueish to dark make furniture and ornaments. range in colour from cream green to silvery grey. Most The seed of some wattles is to intense yellow. The leaves species of Acacia have glands a good food source for birds, of Acacia may be bipinnate on the axis of the phyllodes, other animals and humans (the primary leaflets being although in Australian as ‘bush tucker’. -
OUTLINE for THIS WEEK Lec 11 – 13 METAPOPULATIONS Concept --> Simple Model Spatially Realistic Metapopulation Models De
OUTLINE FOR THIS WEEK Lec 11 – 13 METAPOPULATIONS concept --> simple model Spatially realistic metapopulation models Design and Implementation Pluses/minuses The importance of the MATRIX CORRIDORS (as a conservation tool) THE BASICS Levins 1970 - first used term metapopulation “a population of populations” a group of local populations that are linked by immigration and emigration Approach Model population persistence NOT population size Local populations are reduced to two values 0 local extinction, 1 local persistence Metapopulation operates at a larger spatial scale examines proportion of patches that are occupied The classical metapopulation All patches are the same No spatial structure Large number of patches time Change is due to Extinction and Colonization Metapopulations are buffered by rescue effects or recolonisation after local extinction Modelling the classical metapopulation Extinctions = extinction rate x prop’n patches occupied = e.p Colonization = colonization rate x prop’n unoccupied patches = cp. (1-p) E C 0 1 p 0 p 1 At EQUILIBRIUM Extinction = Colonization ep = cp (1-p) Q. What influences P*= 1- e/c Extinction Graphically Colonization C or E 0 p 1 Classical metapulations and habitat loss Loss of a patch Reduced patch size --> a reduced colonization rate !increased! extinction !reduced! colonization 0 1 Pnew Porig 0 1 P Pnew orig The classical metapopulation model is UNREALISTIC all patches are the same size all patches are equally connected BUT patches in nature vary in size and isolation Spatially realistic metapopulation -
Evidence for Colonisation of Anthropogenic Habitats by the Réunion Day Gecko Phelsuma Borbonica (Mertens, 1966) (Réunion Island, France): Conservation Implications
Herpetology Notes, volume 10: 563-571 (2017) (published online on 18 October 2017) Evidence for colonisation of anthropogenic habitats by the Réunion day gecko Phelsuma borbonica (Mertens, 1966) (Réunion Island, France): conservation implications Stéphane Augros1,*, Lisa Faipoux2, Manon Bodin2, Arnaud Le Goff1, Mickaël Sanchez3 and Johanna Clémencet2 Abstract. Réunion Island landscapes are today characterised by a complex mosaic of ecosystems in varying degrees of alteration. Changes in natural areas result in hybrid ecosystems, retaining some original characteristics (e.g. native species) as well as novel elements (e.g. introduced species). Previous studies demonstrate that substantially modified areas could represent valuable habitats for some species of Phelsuma. Here, we examine a population of the Réunion day gecko, Phelsuma borbonica, in habitats characterised by different degrees of human influence to improve the understanding of the distribution of this species outside its native area. Distribution, edge effect, artificial structure attractiveness and degree of habitats alteration were quantified with four distinct protocols. We found that availability of egg laying sites, and edge effect should be considered as potential drivers to explain the species observed distribution within highly disturbed areas dominated by introduced plant species and scattered with artificial structures. Consequently, anthropogenic habitats must be seen in certain cases as areas of importance for the endangered P. borbonica. Because hybridecosystems