On the Ecology of Invasive Species, Extinction, Ecological
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SDG Indicator Metadata (Harmonized Metadata Template - Format Version 1.0)
Last updated: 4 January 2021 SDG indicator metadata (Harmonized metadata template - format version 1.0) 0. Indicator information 0.a. Goal Goal 15: Protect, restore and promote sustainable use of terrestrial ecosystems, sustainably manage forests, combat desertification, and halt and reverse land degradation and halt biodiversity loss 0.b. Target Target 15.5: Take urgent and significant action to reduce the degradation of natural habitats, halt the loss of biodiversity and, by 2020, protect and prevent the extinction of threatened species 0.c. Indicator Indicator 15.5.1: Red List Index 0.d. Series 0.e. Metadata update 4 January 2021 0.f. Related indicators Disaggregations of the Red List Index are also of particular relevance as indicators towards the following SDG targets (Brooks et al. 2015): SDG 2.4 Red List Index (species used for food and medicine); SDG 2.5 Red List Index (wild relatives and local breeds); SDG 12.2 Red List Index (impacts of utilisation) (Butchart 2008); SDG 12.4 Red List Index (impacts of pollution); SDG 13.1 Red List Index (impacts of climate change); SDG 14.1 Red List Index (impacts of pollution on marine species); SDG 14.2 Red List Index (marine species); SDG 14.3 Red List Index (reef-building coral species) (Carpenter et al. 2008); SDG 14.4 Red List Index (impacts of utilisation on marine species); SDG 15.1 Red List Index (terrestrial & freshwater species); SDG 15.2 Red List Index (forest-specialist species); SDG 15.4 Red List Index (mountain species); SDG 15.7 Red List Index (impacts of utilisation) (Butchart 2008); and SDG 15.8 Red List Index (impacts of invasive alien species) (Butchart 2008, McGeoch et al. -
Final Report of the Statewide Ecological Extinction Task Force
FINAL REPORT OF THE STATEWIDE ECOLOGICAL EXTINCTION TASK FORCE ESTABLISHED UNDER THE PROVISIONS OF SENATE CONCURRENT RESOLUTION NO. 20 OF THE 149TH GENERAL ASSEMBLY RESPECTFULLY SUBMITTED TO THE GOVERNOR, PRESIDENT PRO TEMPORE OF THE SENATE, AND SPEAKER OF THE HOUSE DECEMBER 1ST, 2017 TABLE OF CONTENTS MEMBERS OF THE TASK FORCE ............................................................................... 1 PREFACE.................................................................................................................. 2 INTRODUCTION ........................................................................................................ 3 EXECUTIVE SUMMARY BACKGROUND OF THE TASK FORCE .............................................................. 6 OVERVIEW OF MEETINGS .............................................................................. 7 TASK FORCE FINDINGS ............................................................................................ 10 TASK FORCE RECOMMENDATIONS .......................................................................... 11 APPENDICES A. SENATE CONCURRENT RESOLUTION 20 ................................................... 16 B. COMPOSITION OF TASK FORCE AND MEMBER BIOGRAPHIES ................... 19 C. MINUTES FROM TASK FORCE MEETINGS ................................................. 32 D. INTERN REPORT ....................................................................................... 105 E. LINKS TO SUPPLEMENTAL MATERIALS CONTRIBUTED BY TASK FORCE MEMBERS ............................................. -
Distribution and Current Status of Rodents in the Galapagos
April 1994 NOTICIAS DE GALÁPAGOS 2I DISTRIBUTION AND CURRENT STATUS OF RODENTS IN THE GALÁPAGOS By: Gillian Key and Edgar Muñoz Heredia. INTRODUCTION (GPNS) and the Charles Darwin Resea¡ch Station (CDRS) in their continuing efforts to protecr the The uniqueness and scientific importance of the unique wildlife of the islands. Galápagos Islands has longbeenrecognized, although the c¡eation of the National Park in 1959 came after ENDEMIC RODENTS several centuries of sporadic use and colonization by man. Undoubtedly, the lack of water in the islands Seven species of endemicricerats a¡eknown from has been thei¡ savior by limiting the extent and dura- the Archipelago, of which the seventh was only rel- tion of many early attempts to colonize. Even so the atively recently discove¡ed from owl pellets on impact of man has been severe in the Archipelago, Fernandina island (Ilutterer & Hirsch 1979), Brosset and the biggest problems for conservation today are ( 1 963 ) and Niethammer ( 1 9 64) have summarized the the introduced species of plants and animals. These available information on the six species known at introduced species are frequently pests to the human that time, including last sightings and probable dates inhabitants as well as to the native flora and fauna, to ofextinction. Galápagosricerats belongto twoclosely the former by damaging crops and goods, and to the related generaof oryzomys rodents and were distrib- latter by competition, predation and transmission of uted among the six islands (Table 1). disease. Patton and Hafner (1983) concluded that rats of The feral mammals in particular constitute a ma- the genus Nesoryzomys arrived in the Archipelago jorproblem, principally due to their size and numbers. -
Rewilding Watersheds: Using Nature's Algorithms to Fix Our Broken Rivers
Marine and Freshwater Research © CSIRO 2021 https://doi.org/10.1071/MF20335_AC Supplementary material Rewilding watersheds: using nature’s algorithms to fix our broken rivers Natalie K. RideoutA,G,1, Bernhard WegscheiderB,1, Matilda KattilakoskiA, Katie M. McGeeC,D, Wendy A. MonkE, and Donald J. BairdF ACanadian Rivers Institute, Department of Biology, University of New Brunswick, 10 Bailey Drive, Fredericton, NB, E3B 5A3, Canada. BCanadian Rivers Institute, Faculty of Forestry and Environmental Management, University of New Brunswick, 2 Bailey Drive, Fredericton, NB, E3B 5A3, Canada. CEnvironment and Climate Change Canada, Canada Centre for Inland Waters, 867 Lakeshore Road, Burlington, ON, L7R 4A6, Canada. DCentre for Biodiversity Genomics and Department of Integrative Biology, University of Guelph, 50 Stone Road E., Guelph, ON, N1G 2W1, Canada. EEnvironment and Climate Change Canada @ Canadian Rivers Institute, Faculty of Forestry and Environmental Management, University of New Brunswick, 2 Bailey Drive, Fredericton, NB, E3B 5A3, Canada. FEnvironment and Climate Change Canada @ Canadian Rivers Institute, Department of Biology, University of New Brunswick, 10 Bailey Drive, Fredericton, NB, E3B 5A3, Canada. GCorresponding author. Email: [email protected] 1These authors contributed equally to the work. Page 1 of 49 Table S1. References linking ecosystem functions with rewilding goals, providing supporting evidence for Fig. 1 Restore natural flow Mitigate climate Restore riparian Re-introduce Improve water quality Reduce habitat and sediment regime warming vegetation extirpated species fragmentation 1 Metabolism Aristi et al. 2014 Song et al. 2008 Wassenaar et al. 2010 Huang et al. 2018 Jankowski and Schindler 2019 2 Decomposition Delong 2010 Perry et al. 2011 Delong 2010 Wenisch et al. -
Ecosystem Impact of the Decline of Large Whales in the North Pacific
SIXTEEN Ecosystem Impact of the Decline of Large Whales in the North Pacific DONALD A. CROLL, RAPHAEL KUDELA, AND BERNIE R. TERSHY Biodiversity loss can significantly alter ecosystem processes over a 150-year period (Springer et al. 2003). Although large (Chapin et al. 2000), and ecological extinction can have whales are significant consumers of pelagic prey, such as similar effects (Jackson et al. 2001). For marine vertebrates, schooling fish and euphausiids (krill), the trophic impacts of overharvesting is the main driver of ecological extinction, their removal is not clear (Trites et al. 1999). Indeed, it is and the expansion of fishing fleets into the open ocean has possible that the biomass of prey consumed by large whales precipitated rapid declines in pelagic apex predators such as prior to exploitation exceeded that currently taken by com- whales (Baker and Clapham 2002), sharks (Baum et al. 2003), mercial fisheries (Baker and Clapham 2002), but estimates of tuna, and billfishes (Cox et al. 2002; Christensen et al. 2003), prey consumption by large whales before and after the period leading to a trend in global fisheries toward exploitation of of intense human exploitation are lacking. Given the large lower trophic levels (Pauly et al. 1998a). Globally, many fish biomass of pre-exploitation whale populations (see, e.g., stocks are overexploited (Steneck 1998), and the resulting Whitehead 1995; Roman and Palumbi 2003), their high ecological extinctions have been implicated in the collapse mammalian metabolic rate, and their relatively high trophic of numerous nearshore coastal ecosystems (Jackson et al. position (Trites 2001), it is likely that the removal of large 2001). -
Improvements to the Red List Index Stuart H
Improvements to the Red List Index Stuart H. M. Butchart1*, H. Resit Akc¸akaya2, Janice Chanson3, Jonathan E. M. Baillie4, Ben Collen4, Suhel Quader5,8, Will R. Turner6, Rajan Amin4, Simon N. Stuart3, Craig Hilton-Taylor7 1 BirdLife International, Cambridge, United Kingdom, 2 Applied Biomathematics, Setauket, New York, United States of America, 3 Conservation International/Center for Applied Biodiversity Science-World Conservation Union (IUCN)/Species Survival Commission Biodiversity Assessment Unit, IUCN Species Programme, Center for Applied Biodiversity Science, Conservation International, Washington, D. C., United States of America, 4 Institute of Zoology, Zoological Society of London, London, United Kingdom, 5 Department of Zoology, University of Cambridge, Cambridge, United Kingdom, 6 Center for Applied Biodiversity Science, Conservation International, Washington, D. C., United States of America, 7 World Conservation Union (IUCN) Species Programme, Cambridge, United Kingdom, 8 Royal Society for the Protection of Birds, Sandy, United Kingdom The Red List Index uses information from the IUCN Red List to track trends in the projected overall extinction risk of sets of species. It has been widely recognised as an important component of the suite of indicators needed to measure progress towards the international target of significantly reducing the rate of biodiversity loss by 2010. However, further application of the RLI (to non-avian taxa in particular) has revealed some shortcomings in the original formula and approach: It performs inappropriately when a value of zero is reached; RLI values are affected by the frequency of assessments; and newly evaluated species may introduce bias. Here we propose a revision to the formula, and recommend how it should be applied in order to overcome these shortcomings. -
Broad-Headed Snake (Hoplocephalus Bungaroides)', Proceedings of the Royal Zoological Society of New South Wales (1946-7), Pp
Husbandry Guidelines Broad-Headed Snake Hoplocephalus bungaroides Compiler – Charles Morris Western Sydney Institute of TAFE, Richmond Captive Animals Certificate III RUV3020R Lecturers: Graeme Phipps, Jacki Salkeld & Brad Walker 2009 1 Occupational Health and Safety WARNING This Snake is DANGEROUSLY VENOMOUS CAPABLE OF INFLICTING A POTENTIALLY FATAL BITE ALWAYS HAVE A COMPRESSION BANDAGE WITHIN REACH SNAKE BITE TREATMENT: Do NOT wash the wound. Do NOT cut the wound, apply substances to the wound or use a tourniquet. Do NOT remove jeans or shirt as any movement will assist the venom to enter the blood stream. KEEP THE VICTIM STILL. 1. Apply a broad pressure bandage over the bite site as soon as possible. 2. Keep the limb still. The bandage should be as tight as you would bind a sprained ankle. 3. Extend the bandage down to the fingers or toes then up the leg as high as possible. (For a bite on the hand or forearm bind up to the elbow). 4. Apply a splint if possible, to immobilise the limb. 5. Bind it firmly to as much of the limb as possible. (Use a sling for an arm injury). Bring transport to the victim where possible or carry them to transportation. Transport the victim to the nearest hospital. Please Print this page off and put it up on the wall in your snake room. 2 There is some serious occupational health risks involved in keeping venomous snakes. All risk can be eliminated if kept clean and in the correct lockable enclosures with only the risk of handling left in play. -
The Oyster : Contributions to Habitat, Biodiversity, & Ecological Resiliency
The Oyster : Contributions to Habitat, Biodiversity, & Ecological Resiliency Factors Affecting Oyster Distribution & Abundance Physical = salinity, temperature Salinity & Temperature •S - dynamic change ~daily basis; T - changes seasonally •Affects community organization - high S & T= predators, disease By Steve Morey, FAMU ‘Oysters suffered significant disease- related mortality under high-salinity, drought conditions, particularly in the summer.’ Dermo Perkinsus marinus Petes et al. 2012. Impacts of upstream drought and water withdrawals on the health & survival of downstream estuarine oyster populations. Ecology & Evolution 2(7):1712-1724 Factors Affecting Oyster Distribution & Abundance Physical = River flow Seasonal River Flow •Major influence on physical & biological relationships •Delivers low salinity H2O, turbidity, high nutrient & detritus concentrations •River flow, when high, can extend far offshore influencing shelf-edge productivity Factors Affecting Oyster Distribution & Abundance Competition for space & food at different life stages • Can be intraspecific -oysters competing with oysters- or interspecific - other species competing with oysters) Oysters • Can affect settlement patterns, and so alter community structure • Can reduce oyster density, growth, or physical condition Oysters eat phytoplankton & other organisms within a small size range, competing with other Barnacles filter feeders Mussels & Tunicates Factors Affecting Oyster Distribution & Abundance Species interactions – predation & disease •Habitat complexity -
Population Genetics of the Native Rodents of the Galápagos Islands, Ecuador
Population Genetics of the Native Rodents of the Galápagos Islands, Ecuador A dissertation submitted in partial fulfillment of the requirements for the degree of Doctor of Philosophy at George Mason University By Sarah Johnson Master of Science Stephen F. Austin State University, 2005 Bachelor of Science Texas A&M University, 2003 Director: Dr. Cody W. Edwards, Assistant Professor Department of Environmental Science and Public Policy Summer Semester 2009 George Mason University Fairfax, VA Copyright 2009 Sarah Johnson All Rights Reserved ii ACKNOWLEDGMENTS I would like to thank my parents (Michael and Kay Johnson) and my sisters (Kris and Faith) for their unwavering support throughout my academic career. This dissertation is lovingly dedicated to my parents. I would like to thank my Aggie Family (Brad and Kristin Atchison, Reece and Erin Flood, Samir Moussa, Doug Fuentes, and the rest of the IV Horsemen). They have always lovingly provided a shoulder to lean on and kind ear willing to listen. I would like to thank my fellow graduate students at GMU (Jeff Streicher, Mike Jarcho, Kat Bryant, Tammy Henry, Geoff Cook, Ryan Peters, Kristin Wolf, Trishna Dutta, Sandeep Sharma, and Jolanda Luksenburg) for their help in the field, lab, classroom, and all aspects of student life. I am eternally indebted to Dr. Pat Gillevet and Masi Sikaroodi for their invaluable assistance in the lab, and to Dr. Jesús Maldonado for his assistance in writing the dissertation. They are infinite sources of help and support for which I am forever grateful. The project would not have been possible without Dr. Cody W. Edwards and Dr. -
Interactive Effects of Shifting Body Size and Feeding Adaptation Drive
bioRxiv preprint doi: https://doi.org/10.1101/101675; this version posted January 20, 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-ND 4.0 International license. 1 Interactive effects of shifting body size and feeding 2 adaptation drive interaction strengths of protist 3 predators under warming 4 Temperature adaptation of feeding 5 K.E.Fussmann 1,2, B. Rosenbaum 2, 3, U.Brose 2, 3, B.C.Rall 2, 3 6 1 J.F. Blumenbach Institute of Zoology and Anthropology, University of Göttingen, Berliner 7 Str. 28, 37073 Göttingen, Germany 8 2 German Centre for Integrative Biodiversity Research (iDiv), Halle-Jena-Leipzig, Deutscher 9 Platz 5e, 04103 Leipzig, Germany 10 3 Institute of Ecology, Friedrich Schiller University Jena, Dornburger-Str. 159, 07743 Jena, 11 Germany 12 Corresponding author: Katarina E. Fussmann 13 telephone: +49 341 9733195 14 email: [email protected] 15 Keywords: climate change, functional response, body size, temperature adaptation, activation 16 energies, microcosm experiments, predator-prey, interaction strength, Bayesian statistics 17 Paper type: Primary Research 1 bioRxiv preprint doi: https://doi.org/10.1101/101675; this version posted January 20, 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-ND 4.0 International license. 18 Abstract 19 Global change is heating up ecosystems fuelling biodiversity loss and species extinctions. -
A Robust Goal Is Needed for Species in the Post-2020 Global Biodiversity Framework
Preprints (www.preprints.org) | NOT PEER-REVIEWED | Posted: 16 April 2020 Title: A robust goal is needed for species in the Post-2020 Global Biodiversity Framework Running title: A post-2020 goal for species conservation Authors: Brooke A. Williams*1,2, James E.M. Watson1,2,3, Stuart H.M. Butchart4,5, Michelle Ward1,2, Nathalie Butt2, Friederike C. Bolam6, Simon N. Stuart7, Thomas M. Brooks8,9,10, Louise Mair6, Philip J. K. McGowan6, Craig Hilton-Taylor11, David Mallon12, Ian Harrison8,13, Jeremy S. Simmonds1,2. Affiliations: 1School of Earth and Environmental Sciences, University of Queensland, St Lucia 4072, Australia 2Centre for Biodiversity and Conservation Science, School of Biological Sciences, University of Queensland, St Lucia 4072, Queensland, Australia. 3Wildlife Conservation Society, Global Conservation Program, Bronx, NY 20460, USA. 4BirdLife International, The David Attenborough Building, Pembroke Street, Cambridge CB2 3QZ, UK 5Department of Zoology, Cambridge University, Downing Street, Cambridge CB2 3EJ, UK 6School of Natural and Environmental Sciences, Newcastle University, Newcastle upon Tyne, NE1 7RU, UK 7Synchronicity Earth, 27-29 Cursitor Street, London, EC4A 1LT, UK 8IUCN, 28 rue Mauverney, CH-1196, Gland, Switzerland 9World Agroforestry Center (ICRAF), University of the Philippines Los Baños, Laguna, 4031, Philippines 10Institute for Marine and Antarctic Studies, University of Tasmania, Hobart, TAS 7001, Australia 11IUCN, The David Attenborough Building, Pembroke Street, Cambridge CB2 3QZ, UK 12Division of Biology and Conservation Ecology, Manchester Metropolitan University, Chester St, Manchester, M1 5GD, U.K 13Conservation International, Arlington, VA 22202, USA Emails: Brooke A. Williams: [email protected]; James E.M. Watson: [email protected]; Stuart H.M. -
Dr. Michael L. Rosenzweig the Man the Scientist the Legend
BIOL 7083 Community Ecologist Presentation Dr. Michael L. Rosenzweig The Man The Scientist The Legend Michael Rosenzweigs Biographical Information Born in 1941 Jewish Parents wanted him to be a physician Ph.D. University of Pennsylvania, 1966 Advisor: Robert H. MacArthur, Ph.D. Married for over 40 years to Carole Ruth Citron Together they have three children, and several grandchildren Biographical Information Known to be an innovator Founded the Department of Ecology & Evolutionary Biology at the University of Arizona in 1975, and was its first head In 1987 he founded the scientific journal Evolutionary Ecology In 1998, when prices for journals began to rise, he founded a competitor, Evolutionary Ecology Research Honor and Awards Ecological Society of America Eminent Ecologist Award for 2008 Faculty of Sci, Univ Arizona, Career Teaching Award, 2001 Ninth Lukacs Symp: Twentieth Century Distinguished Service Award, 1999 International Ecological Soc: Distinguished Statistical Ecologist, 1998 Udall Center for Studies in Public Policy, Univ Arizona: Fellow, 1997±8 Mountain Research Center, Montana State Univ: Distinguished Lecturer, 1997 Univ Umeå, Sweden: Distinguished Visiting Scholar, 1997 Univ Miami: Distinguished Visiting Professor, 1996±7 Univ British Columbia: Dennis Chitty Lecturer, 1995±6 Iowa State Univ: 30th Paul L. Errington Memorial Lecturer, 1994 Michigan State Univ, Kellogg Biological Station: Eminent Ecologist, 1992 Honor and Awards Ben-Gurion Univ of the Negev, Israel: Jacob Blaustein Scholar, 1992