Selecting for Tolerance Against Pathogens and Herbivores to Enhance Success of Reintroduction and Translocation

Total Page:16

File Type:pdf, Size:1020Kb

Selecting for Tolerance Against Pathogens and Herbivores to Enhance Success of Reintroduction and Translocation Essay Selecting for Tolerance against Pathogens and Herbivores to Enhance Success of Reintroduction and Translocation MATTHEW D. VENESKY,∗† JOSEPH R. MENDELSON III,‡§ BRITTANY F. SEARS,∗ PETER STILING,∗ AND JASON R. ROHR∗ ∗Department of Integrative Biology, The University of South Florida, 4202 East Fowler Avenue, SCA 110, Tampa, FL 33620, U.S.A. ‡Zoo Atlanta, 800 Cherokee Avenue SE, Atlanta, GA 30315, U.S.A. §Georgia Institute of Technology, School of Biology, 301 Ferst Drive, Atlanta, GA 30332, U.S.A. Abstract: Some species have insufficient defenses against climate change, emerging infectious diseases, and non-native species because they have not been exposed to these factors over their evolutionary history, and this can decrease their likelihood of persistence. Captive breeding programs are sometimes used to reintroduce individuals back into the wild; however, successful captive breeding and reintroduction can be difficult because species or populations often cannot coexist with non-native pathogens and herbivores without artificial selection. In captive breeding programs, breeders can select for host defenses that prevent or reduce pathogen or herbivore burden (i.e., resistance) or traits that limit the effects of parasitism or herbivory on host fitness (i.e., tolerance). We propose that selection for host tolerance may enhance the success of reintroduction or translocation because tolerant hosts generally have neutral effects on introduced pathogens and herbivores. The release of resistant hosts would have detrimental effects on their natural enemies, promoting rapid evolution to circumvent the host resistance that may reduce the long-term probability of persistence of the reintroduced or translocated species. We examined 2 case studies, one on the pathogenic amphibian chytrid fungus ( Batrachochytrium dendrobatidis [Bd]) and the other on the herbivorous cactus moth ( Cactoblastis cactorum) in the United States, where it is not native. In each case study, we provide recommendations for how captive breeders and managers could go about selecting for host tolerance. Selecting for tolerance may offer a promising tool to rescue hosts species from invasive natural enemies as well as new natural enemies associated with climate change-induced range shifts. Keywords: artificial selection, Batrachochytrium dendrobatidis, Cactoblastis cactorum, cactus moth, captive breeding, chytridiomycosis, non-native species, tolerance Seleccion´ de Tolerancia a Patogenos´ y Herb´ıvoros para Incrementar el Exito´ de la Reintroduccion´ y la Translocacion´ Resumen: Algunas especies no tienen suficientes defensas contra el cambio climatico,´ enfermedades in- fecciosas emergentes y especies no nativas porque no han sido expuestas a estos factores a lo largo de su historia evolutiva, y esto puede disminuir su probabilidad de persistencia. El ´exito de la reproduccion´ en cautiverio y de la reintroduccion´ puede ser dif´ıcil porque las especies o poblaciones a menudo no pueden coexistir con patogenos´ y herb´ıvoros no nativos sin seleccion´ artificial. En programas de reproduccion´ en cau- tiverio, los criadores pueden seleccionar defensas que prevengan infecciones o herbivor´ıa o que reducen la carga de patogenos´ o herb´ıvoros atacando directamente al patogeno´ o herb´ıvoro (i.e., resistencia) o atributos que limitan los efectos del parasitismo o la herbivor´ıa sobre la adaptabilidad del hu´esped (i.e., tolerancia). †email [email protected] Paper submitted August 16, 2011; revised manuscript accepted January 13, 2012. 586 Conservation Biology, Volume 26, No. 4, 586–592 C 2012 Society for Conservation Biology DOI: 10.1111/j.1523-1739.2012.01854.x Venesky et al. 587 Proponemos que la seleccion´ de tolerancia del hu´esped puede incrementar el ´exito de los programas de reintro- duccion´ o translocacion.´ Nuestra hipotesis´ es que los hu´espedes tolerantes generalmente tienen efectos neutros sobre patogenos´ y herb´ıvoros introducidos. En contraste, planteamos la hipotesis´ que los hu´espedes resistentes tienen efectos perjudiciales sobre los patogenos´ y herb´ıvoros porque promueven la evolucion´ rapida´ para sortear la resistencia del hu´esped, lo cual puede reducir la probabilidad de persistencia a largo plazo de la especie reintroducida o translocada. Examinamos dos casos de estudio, uno en el hongo quitridio patogeno´ de anfibios ( Batrachochytrium dendrobatidis [Bd]) y el otro en la polilla herb´ıvora ( Cactoblastis cactorum) en los Estados Unidos, donde es no nativa. Con anfibios, la tolerancia a Bd puede provenir de respuestas inmunologicas´ o de atributos fisiologicos´ que mantienen la funcion´ osmorguladora. En cactos, la tolerancia alaherbivor´ıa puede ser mediada por incremento en la produccion´ de brotes o por redistribucion´ de energ´ıa de las ra´ıces a la reproduccion.´ El conocimiento de la importancia relativa de la tolerancia de hu´espedes versus la resistencia podr´ıa tener implicaciones para taxa de plantas y animales amenazados. Palabras Clave: Batrachochytrium dendrobatidis, Cactoblastis cactorum, especie no nativa, polilla del cacto, quitridiomicosis, reproduccion´ en cautiverio, seleccion´ artificial, tolerancia Introduction a constant exposure to the pathogen or herbivore. Tol- erance reduces the fitness consequences of a particular Some species have insufficient defenses against intro- pathogen load or level of herbivory and thus, unlike re- duced pathogens and predators because they have not sistance, it is hypothesized to have either a neutral or been exposed to these organisms over evolutionary time. positive effect on the pathogen or herbivore (Miller et As species continue to shift their distributions naturally in al. 2006). Tolerance is typically measured as the slope response to climate change or as their distributions are of the relation between host fitness (or a proxy measure changed artificially through translocation, they will be of fitness) and pathogen or herbivore abundance (Fig. 1) more likely to be exposed to non-native pathogens and (Raberg et al. 2007; Raberg et al. 2009). Hence, reintro- predators to which they lack evolved defenses (Hoegh- duction and translocation programs can artificially select Guldberg et al. 2008). for individuals that are resistant or tolerant to a pathogen When species are unable to survive in their natural or herbivore or reintroduce or translocate the species habitat because of an introduced pathogen or herbivore, without selection. conservation efforts, such as captive breeding, are of- Given that resistance has a direct adverse effect on ten used to reduce the threat of extinction (Ebenhard pathogens and herbivores, but tolerance does not, re- 1995). The eventual introduction of captive-bred individ- sistance and tolerance can impose different selection uals to their natural habitat (Griffiths & Pavajeau 2008) pressures on pathogens and herbivores (Roy & Kirchner or their translocation to another area thought to be suffi- cient habitat (Hoegh-Guldberg et al. 2008) is an inherent element of captive breeding programs. Artificial selection in captive breeding programs is often an important tool because natural selection may not occur fast enough to protect hosts from rapid exposure to novel pathogens or herbivores. An unresolved question, however, is how to imple- ment a successful reintroduction or translocation pro- gram for species that cannot presently coexist with introduced pathogens or herbivores. In the disease and plant biology literature, strategies for coexisting with pathogens (here, pathogens include micro- and macroparasites) and herbivores are dichotomized into resistance and tolerance (e.g., Strauss & Agrawal 1999; Nunez-Farfan et al. 2007; Raberg et al. 2007). Resistance refers to defenses that reduce pathogen or herbivore bur- Figure 1. Comparison of the tolerance responses of den by either preventing infection or herbivory or di- individuals of 2 species or genotypes when exposed to rectly attacking the pathogen or herbivore (e.g., immune a pathogen or herbivore (slope of lines is tolerance). responses to pathogens, herbivore-deterring toxins); con- Fitness and pathogen or herbivore intensity increase sequently, resistance has a direct adverse effect on the on each axis from the origin. Individuals of the pathogen or herbivore. Resistance is typically measured species represented by the closed circles are less as the inverse of pathogen abundance or herbivory given tolerant than those represented by the open circles. Conservation Biology Volume 26, No. 4, 2012 588 Tolerance against Pathogens and Herbivores 2000) that may affect the success of reintroductions and cosis, so conservation strategies focus on management of translocations. For instance, to breed resistant individu- host populations. Captive breeding was explicitly rec- als, one selects for traits that provide countermeasures ommended in the International Union for Conservation (i.e., an action to oppose, neutralize, or retaliate against of Nature (IUCN) global amphibian action plan as a prior- some other action) to pathogens or herbivores. Given ity conservation initiative in response to the spatial and that pathogens and most herbivores (e.g., insects) have temporal spread of Bd epidemics (Gascon et al. 2007). shorter generation times than their hosts, host evolu- As a result of efforts by the IUCN Amphibian Ark tion would likely lag behind the countermeasures of the network and other conservation initiatives, hundreds of pathogens or herbivores. This evolutionary lag could re- threatened amphibian
Recommended publications
  • Lepidoptera:Pyralidae) in Florida
    Mississippi State University Scholars Junction Theses and Dissertations Theses and Dissertations 1-1-2009 The Ecology of Cactoblastis Cactorum (Berg) (Lepidoptera:pyralidae) in Florida Kristen Erica Sauby Follow this and additional works at: https://scholarsjunction.msstate.edu/td Recommended Citation Sauby, Kristen Erica, "The Ecology of Cactoblastis Cactorum (Berg) (Lepidoptera:pyralidae) in Florida" (2009). Theses and Dissertations. 4323. https://scholarsjunction.msstate.edu/td/4323 This Graduate Thesis - Open Access is brought to you for free and open access by the Theses and Dissertations at Scholars Junction. It has been accepted for inclusion in Theses and Dissertations by an authorized administrator of Scholars Junction. For more information, please contact [email protected]. THE ECOLOGY OF CACTOBLASTIS CACTORUM (BERG) (LEPIDOPTERA: PYRALIDAE) IN FLORIDA By Kristen Erica Sauby A Thesis Submitted to the Faculty of Mississippi State University in Partial Fulfillment of the Requirements for the Degree of Master of Science in Biological Sciences in the Department of Biological Sciences Mississippi State, Mississippi August 2009 Copyright by Kristen Erica Sauby 2009 THE ECOLOGY OF CACTOBLASTIS CACTORUM (BERG) (LEPIDOPTERA: PYRALIDAE) IN FLORIDA By Kristen Erica Sauby Approved: Christopher P. Brooks Richard L. Brown Assistant Professor of Biological Sciences Professor of Entomology (Director of Thesis) (Committee Member) Gary N. Ervin Gary N. Ervin Associate Professor of Biological Sciences Graduate Coordinator of the
    [Show full text]
  • Research Notes
    Research Notes GEOGRAPHICAL DISTRIBUTION AND HOST PLANTS OF THE CACTUS MOTH, CACTOBLASTIS CACTORUM (BERG) IN PUERTO RICO AND THE UNITED STATES VIRGIN ISLANDS The cactus moth, Caddblastis cadorum (Berg)1, was described from Argentina in 1885 in the genus Zophodia. Ragonot2 transferred the species to the genus Caddblastis in his 1901 monograph. C. cadorum occurs endemically in the more northern provinces of Argen­ tina: Entre Ríos, Corrientes, Santa Fe, the northern part of Córdoba, Santiago del Estero, Tucumán, Salta, Juyuy and the Chaco. In Uruguay, it has been recorded along the Uruguay and Plata Rivers from Piriápolis in the south, northward to Salta. The distribution extends from Corrientes in northeastern Argentina northward through Paraguay, where the insect has been observed at Villa de la Concepción and in the vicinity of Asunción, into the Brazilian province of Matto Grosso, where the larva has been recorded at Corumba on the Paraguay River. Heinrich3'4 discussed this species taxonomically in his 1939 and 1956 revisions of the moths belonging to the Phycitinae (Lepidoptera). The most complete account on the biological control of this species was given by Dodd6 in 1940, while Mann6 in 1969 furnished an excellent account of the distribution, host plants and biology of C. cadorum. Simmonds and Bennett7 in 1966 discussed the introduction and host plants of the moth into the Leeward Islands of the West Indies (Nevis, Montserrat, Antigua, St. Kitts). The eggs of Caddblastis cadorum are laid in chains or egg sticks generally at the end of a cactus spine (fig. 1, A). It is well known that larvae (fig.
    [Show full text]
  • Local Dispersal Pathways During the Invasion of the Cactus Moth
    www.nature.com/scientificreports OPEN Local dispersal pathways during the invasion of the cactus moth, Cactoblastis cactorum, within North America and the Caribbean Guadalupe Andraca-Gómez1, Eric Lombaert2, Mariano Ordano3, Rubén Pérez-Ishiwara1, Karina Boege1, César A. Domínguez1 & Juan Fornoni1 ✉ Cactoblastis cactorum, a species of moth native to Argentina, feeds on several prickly pear cactus species (Opuntia) and has been successfully used as a biological control of invading Opuntia species in Australia, South Africa and native ruderal Opuntia species in some Caribbean islands. Since its introduction to the Caribbean its spread was uncontrolled, invading successfully Florida, Texas and Louisiana. Despite this long history of invasion, we are still far from understanding the factors determining the patterns of invasion of Cactoblastis in North America. Here, we explored three non-mutually exclusive explanations: a) a stepping stone model of colonization, b) long distance colonization due to hurricanes, and/or c) hitchhiking through previously reported commercial routes. Genetic diversity, genetic structure and the patterns of migration among populations were obtained by analyzing 10 nuclear microsatellite loci. Results revealed the presence of genetic structure among populations of C. cactorum in the invaded region and suggest that both marine commercial trade between the Caribbean islands and continental USA, as well as recurrent transport by hurricanes, explain the observed patterns of colonization. Provided that sanitary regulations avoiding human- mediated dispersal are enforced, hurricanes probably represent the most important agent of dispersal and future invasion to continental areas. During the last decades, biological invasion studies have strongly benefted from the use of neutral molecu- lar markers to disentangle routes of invasion1–3.
    [Show full text]
  • Tracking the Cactus Moth, Cactoblastis Cactorum Berg., As It Flies and Eats Its Way Westward in the U.S
    Spring 2004 News of the Lepidopterists’ Society Alert: Tracking the Cactus Moth, Cactoblastis cactorum Berg., as it flies and eats its way westward in the U.S. M. Alma Solis1, Stephen D. Hight2, and Doria R. Gordon3 1Systematic Entomology Laboratory, Agricultural Research Service, U. S. Department of Agriculture, c/o Smithsonian Institution, P.O. Box 37012, National Museum Natural History, E-517, MRC 168, Washington, DC 20013-7012, [email protected]; 2USDA, ARS, CMAVE at Florida A&M University, Center for Biological Control, Tallahassee, FL 32317, [email protected]; 3The Nature Conservancy, Department of Botany, University of Florida, P.O. Box 118526, Gainesville, FL 32611, [email protected] In 1989, Terry Dickel, a member of the Florida have followed the northward Survey, and the USDA, ARS (Agri- Lepidopterists’ Society, was collecting movement of the cactus moth. By 2002, culture Research Service) to discuss the moths on a sheet at night on Big Pine the cactus moth had eaten its way from westward movement of the cactus moth Key, Florida. He collected a very large the Florida Keys to Folly Island, South beyond Floridian borders. This moth is phycitine he had never seen before in Carolina, on the Atlantic eastern coast predicted to move into the western his extensive surveys of the Florida and to St. George Island, Florida, on states and south to Mexico once it Keys. He contacted Dale Habeck at the the Gulf coast (Hight, et al. 2002). reaches Texas. University of Florida at Gainesville who The late-instar bright orange-red, The cactus moth is currently feeding on recognized that it was the first U.S.
    [Show full text]
  • A Misplaced Sense of Risk: Variation in U.S
    United States Department of Agriculture A MISPLACED SENSE OF RISK: VARIATION IN U.S. STANDARDS FOR MANAGEMENT OF RISKS POSED BY NEW SPECIES INTRODUCED FOR DIFFERENT PURPOSES Roy G. Van Driesche, Robert M. Nowierski, and Richard C. Reardon LEVEL OF REGULATION FISH & FUR-BEARING ANIMALS PETS HORTICULTURE ANIMALS VECTORING DISEASE BIOCONTROL AGENTS nutria LEAST REGULATED Burmese python MOST DANGEROUS kudzu smothering trees kudzu native frog killed by chytrid fungus fire belly toad thistle-feeding weevil trees being killed by nutria MOST REGULATED python eating deer LEAST DANGEROUS thistle seedhead destroyed by weevil HORTICULTURE ANIMALS VECTORING DISEASE FISH & FUR-BEARING ANIMALS PETS BIOCONTROL AGENTS LEVEL OF RISK Forest Health Assessment FHAAST-2019-02 and Applied Sciences Team July 2020 The Forest Health Technology Enterprise Team (FHTET) was created in 1995 by the Deputy Chief for State and Private Forestry, USDA, Forest Service, to develop and deliver technologies to protect and improve the health of American forests. FHTET became Forest Health Assessment and Applied Sciences Team (FHAAST) in 2016. This booklet was published by FHAAST as part of the technology transfer series. https://www.fs.fed.us/foresthealth/applied-sciences/index.shtml Cover Photos: (a) nutria (Philippe Amelant, Wikipedia.org); (b) Burmese python (Roy Wood, National Park Service, Bugwood.org); (c) kudzu (Marco Schmidt, iNaturalist.org); (d) fire belly toad (Kim, Hyun-tae, iNaturalist.org); (e) thistle- feeding weevil (Eric Coombs, Oregon Department of Agriculture, Bugwood.org); (f) kudzu blanketing trees (Kerry Britton, USDA Forest Service, Bugwood.org); (g) native frog killed by chytrid fungus (Brian Gratwicke, iNaturalist. a b c d e org); (h) trees being killed by nutria (Gerald J.
    [Show full text]
  • Area-Wide Control of Insect Pests: Integrating the Sterile Insect and Related Nuclear and Other Techniques
    051346-CN131-Book.qxd 2005-04-19 13:34 Page 1 FAO/IAEA International Conference on Area-Wide Control of Insect Pests: Integrating the Sterile Insect and Related Nuclear and Other Techniques 9 - 13 May 2005 Vienna International Centre Vienna, Austria BOOK OF EXTENDED SYNOPSES FAO Food and Agriculture Organization of the United Nations IAEA-CN-131 051346-CN131-Book.qxd 2005-04-19 13:34 Page 2 The material in this book has been supplied by the authors and has not been edited. The views expressed remain the responsibility of the named authors and do not necessarily reflect those of the government(s) of the designating Member State(s). The IAEA cannot be held responsible for any material reproduced in this book. TABLE OF CONTENTS OPENING SESSION: SETTING THE SCENE..................................................................................1 Area-wide Pest Management: Environmental and Economic Issues .......................................................3 D. Pimentel Regional Management Strategy of Cotton Bollworm in China ...............................................................4 K. Wu SESSION 1: LESSONS LEARNED FROM OPERATIONAL PROGRAMMES...........................7 Boll Weevil Eradication in the United States...........................................................................................9 O. El-Lissy and W. Grefenstette Integrated Systems for Control of Pink Bollworm in Cotton.................................................................10 T. J. Henneberry SESSION 2: LESSONS LEARNED FROM OPERATIONAL PROGRAMMES.........................13
    [Show full text]
  • Cactoblastis Cactorum
    Control Tactics Developed Against the Argentine Cactus Moth, Cactoblastis cactorum Stephen Hight – ARS Tallahassee, FL Jim Carpenter – ARS Tifton, GA and many collaborators Cactoblastis cactorum Life Cycle Adult Oviposition Pupate under/in Eggsticks old (60-100 eggs) pads or veg on soil Early instar larvae Internal feeding Gregarious larvae Cactoblastis cactorum is endemic to Argentina, Paraguay, and Uruguay Cactoblastis cactorum • Opuntia species from N. America became serious non-native weed 1920’s Australia: Cactus moth, was introduced from Argentina to control Opuntia spp. C. cactorum as Biological Control Agent Successful control achieved in Australia after a few years and is still effective 70 years later BEFORE AFTER Cactoblastis cactorum detections in the Southeastern United States SC MS AL GA Charleston LA 2009 2008 Mobile 2007 Pensacola 2005 Tallahassee New Orleans 2004 FL 2003 2011 Northern 2002 expansion in 2001 Farthest Western Florida Tampa Outbreak: Delta area N Peninsula 2000 south of New Orleans 1993 1989 0 50 100 200 mi Miami Oct. 1989 First Continental US Detection – Bahia Honda Key, FL Rangeland Grazing -- cattle and wildlife Nursery Plants and Landscaping Fruit and Pad Production Importance to Subsistence Farmers Historical and Cultural Importance Biodiversity Desert Habitat Approach: 1. Develop survey and trapping techniques to monitor expanding geographical range 2. Identify sex pheromone for trapping lure 3. Develop mass rearing strategies 4. Develop the SIT (Sterile Insect Technique) 5. Implement the SIT on area-wide basis Trap Type Trap Height Trap Color Best Trap white (unpainted) wing trap with sticky bottom and placed at a height of 2m MATING BEHAVIOR Female Calling - time initiate calling - success of calling action - duration of calling Male Response to Calling Behavior - time to respond to female calling - mating success - duration of mating calling mating inactive 60 50 40 30 20 Number of Females 10 0 Time – a.m.
    [Show full text]
  • INVASIVE ALIEN SPECIES: a Toolkit of Best Prevention and Management Practices
    ToolkitUL.qkx 8/10/01 3:35 PM Page 1 INVASIVE ALIEN SPECIES: A Toolkit of Best Prevention and Management Practices Edited by Rüdiger Wittenberg and Matthew J.W. Cock CABI Publishing on behalf of the Global Invasive Species Programme ToolkitUL.qkx 8/10/01 3:35 PM Page ii The designation of geographical entities in this publication, and the presentation of the material, do not imply the expression of any opinion whatsoever, on the part of CABI, SCOPE, IUCN or GISP, concerning the legal status of any country, territory or area, or of its authorities, or concerning the delimitation of its frontiers or boundaries. Published by: CAB International, Wallingford, Oxon, UK, The views expressed in this publication do not necessarily reflect those of CAB International. Copyright: © 2001 CAB International on behalf of the Global Invasive Species Programme. Reproduction of this publication for educational or other non-commercial purposes is authorised without prior permission from the copyright holder provided the source is fully acknowledged. Reproduction for resale or other commercial purpose is prohibited without the prior written permission from the copyright holder. Citation: Wittenberg, R., Cock, M.J.W. (eds.) 2001. Invasive Alien Species: A Toolkit of Best Prevention and Management Practices. CAB International, Wallingford, Oxon, UK, xvii - 228. ISBN: 0 85199 569 1 Catalogue records of this book are available from the British Library, London, UK, and from the Library of Congress, Washington DC, USA Design: The Visual Group, 345 California Avenue,
    [Show full text]
  • United States Department of State Bureau of Oceans and International
    United States Department of State Bureau of Oceans and International Environmental and Scientific Affairs Washington, D.C. 20520 4 September 2015 Dr. Braulio Ferreira de Souza Dias Executive Secretary Convention on Biological Diversity World Trade Centre 393 Saint-Jacques Street, Suite 300 Montréal, Québec, Canada H2Y 1N9 Dear Dr. Dias: In response to CBD Notification 2015-052 – Submission of Information on Invasive Alien Species Management, the United States has the pleasure of providing the attached resources on invasive alien species management. Thank you for your consideration. Sincerely, Jean Preston Acting Director Office of Conservation and Water On behalf of Barbara M. De Rosa-Joynt Chief for Biodiversity U.S. National Focal Point for the Convention on Biological Diversity Attachments: Submission of Invasive Alien Species Management Information United States COVER NOTE FOR SUBMISSION OF INVASIVE ALIEN SPECIES MANAGEMENT INFORMATION Use one sheet per each type of information submitted NAME OF COUNTRY or ORGANIZATION United States of America CONTACT PERSON ON TECHNICAL CONTENTS OF THE INFORMATION Name of the contact Mr. Stanley W. Burgiel person Name of her/his National Invasive Species Council organization Postal address of the c/o U.S. Department of the Interior organization 1849 C Street NW MS-3529 Washington DC 20240 USA Phone number +1 (202) 208 4163 E-mail address [email protected] TYPE OF INFORMATION SUBMITTED – Tick one information source in the right column Peer reviewed journal publication X Other publication,
    [Show full text]
  • Biological Control Options for Invasive Weeds of New Zealand Protected Areas
    Biological control options for invasive weeds of New Zealand protected areas SCIENCE FOR CONSERVATION 199 Victoria Ann Froude Published by Department of Conservation P.O. Box 10-420 Wellington, New Zealand Science for Conservation is a scientific monograph series presenting research funded by New Zealand Department of Conservation (DOC). Manuscripts are internally and externally peer-reviewed; resulting publications are considered part of the formal international scientific literature. Titles are listed in the DOC Science Publishing catalogue on the departmental website http:// www.doc.govt.nz and printed copies can be purchased from [email protected] © Copyright June 2002, New Zealand Department of Conservation ISSN 1173–2946 ISBN 0–478–22266–1 This report was prepared for publication by DOC Science Publishing, Science & Research Unit; editing by Geoff Gregory and layout by Ruth Munro. Publication was approved by the Manager, Science & Research Unit, Science Technology and Information Services, Department of Conservation, Wellington. CONTENTS Abstract 5 1. Introduction 6 2. Background 6 2.1 Overview of weeds in New Zealand natural areas 6 2.2 What is biological control? 6 3. Review objectives 7 4. Methodology 8 4.1 Review of international biological control outcomes 8 4.2 Assessment and management of weed threats 8 4.3 Identification of international and New Zealand biological control work for problem weed species 8 4.4 Selecting weed species for biological control investigations 9 4.5 Preliminary biological control assessments
    [Show full text]
  • Chapter 9: the Status of Nonindigenous Species in the South Florida Environment
    2006 South Florida Environmental Report Chapter 9 Chapter 9: The Status of Nonindigenous Species in the South Florida Environment Amy Ferriter1, Bob Doren2, Carole Goodyear3, Dan Thayer, Jim Burch4, Lou Toth, Mike Bodle, Jon Lane5, Don Schmitz6, Paul Pratt 8, Skip Snow4 and Ken Langeland7 SUMMARY Successful restoration of the South Florida ecosystem, which includes the last vestiges of a once vast Everglades hinges on being able to reverse the environmental degradation that has occurred from human activities over the last 100+ years and prevent degradation from future human activities. While it is clear through the efforts of the Comprehensive Everglades Restoration Plan (CERP) and Restoration Coordination and Verification (RECOVER) programs that numerous factors (e.g., water quantity and quality, and abundance of flora and fauna) are a factor in the restoration effort, the potential impact of invasive species has only recently become a high priority for CERP planning. In support of the collective activities of the many agencies involved in Everglades restoration and CERP, this chapter reviews the broad issues involving nonindigenous species in South Florida and their relationship to restoration, management, planning, organization, and funding. This chapter also provides an overview of nonindigenous species using a comprehensive, all-taxa format for understanding and presenting an inclusive picture of the magnitude of the invasive species threats that exists in South Florida. While detailed information on many of the included nonindigenous species is still unknown, this is the first document to provide a complete listing with species annotations for those species either known, or considered to be, serious threats to Everglades restoration.
    [Show full text]
  • Chapter 4. Analysis of Fauna in the Receiving Area for the Purpose of Identifying Native Species That Exotic Natural Enemies May Potentially Attack
    ASSESSING HOST RANGES OF PARASITOIDS AND PREDATORS _________________________________ CHAPTER 4. ANALYSIS OF FAUNA IN THE RECEIVING AREA FOR THE PURPOSE OF IDENTIFYING NATIVE SPECIES THAT EXOTIC NATURAL ENEMIES MAY POTENTIALLY ATTACK M. S. Hoddle University of California, Riverside, CA 92521 U.S.A. [email protected] GOAL The deliberate introduction and establishment of exotic natural enemies in a new geographic region to control a target pest as part of a classical biological control program entails some level of risk. One aspect of risk pertains to the potential adverse effect released natural enemies could have on desirable native and exotic fauna that are resident in the proposed region of introduc- tion. To mitigate risk associated with classical biological control programs, the threat to the resident fauna needs to be assessed before new species are introduced. Major assumptions with such risk assessments are that the resident fauna is well studied from the phylogenetic, taxo- nomic, ecological, and biological view points and that the autecology of the natural enemy is known. Assuming a sound knowledge base exists, literature surveys, museum records, and biodiversity census data can be very useful in developing a list of potential organisms that could be at risk in the introduced range of the natural enemy. Further, information on the ecological requirements for successful development and population growth, and phenology of natural enemies in their home range can be used to further assess risk to non-targets in the introduced range by determining the level of overlap of key biological aspects between natural enemies and non-targets. In many instances robust data sets will not be available for analysis, and the pest, its associ- ated natural enemies, and the fauna potentially at risk may be entities new to science, further complicating such risk assessments.
    [Show full text]