Xylosandrus Compactus Global Invasive Species Database (GISD)
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Seed Ecology Iii
SEED ECOLOGY III The Third International Society for Seed Science Meeting on Seeds and the Environment “Seeds and Change” Conference Proceedings June 20 to June 24, 2010 Salt Lake City, Utah, USA Editors: R. Pendleton, S. Meyer, B. Schultz Proceedings of the Seed Ecology III Conference Preface Extended abstracts included in this proceedings will be made available online. Enquiries and requests for hardcopies of this volume should be sent to: Dr. Rosemary Pendleton USFS Rocky Mountain Research Station Albuquerque Forestry Sciences Laboratory 333 Broadway SE Suite 115 Albuquerque, New Mexico, USA 87102-3497 The extended abstracts in this proceedings were edited for clarity. Seed Ecology III logo designed by Bitsy Schultz. i June 2010, Salt Lake City, Utah Proceedings of the Seed Ecology III Conference Table of Contents Germination Ecology of Dry Sandy Grassland Species along a pH-Gradient Simulated by Different Aluminium Concentrations.....................................................................................................................1 M Abedi, M Bartelheimer, Ralph Krall and Peter Poschlod Induction and Release of Secondary Dormancy under Field Conditions in Bromus tectorum.......................2 PS Allen, SE Meyer, and K Foote Seedling Production for Purposes of Biodiversity Restoration in the Brazilian Cerrado Region Can Be Greatly Enhanced by Seed Pretreatments Derived from Seed Technology......................................................4 S Anese, GCM Soares, ACB Matos, DAB Pinto, EAA da Silva, and HWM Hilhorst -
(Rattus Spp. and Mus Musculus) in The
CHAPTER SIX: CONCLUSIONS Aaron B. Shiels Department of Botany University of Hawaii at Manoa 3190 Maile Way Honolulu, HI. 96822 173 Along with humans, introduced rats (Rattus rattus, R. norvegicus, and R. exulans) and mice (Mus musculus) are among the most invasive and widely distributed mammals on the planet; they occur on more than 80% of the world‘s islands groups (Atkinson 1985; Towns 2009). By incorporating modern technology, such as aerial broadcast of rodenticides, the number of islands where invasive rodents can be successfully removed has recently increased (Howald et al. 2007). However, successful rat and mouse eradication on relatively large (> 5000 ha) or human-inhabited islands such as the main Hawaiian Islands rarely occurs (Howald et al. 2007) despite large sums of money and research efforts annually to combat invasive rodent problems (see Chapter 1 section ―Rat history in Hawaii‖; Tobin et al. 1990). Therefore, it is highly unlikely that invasive rats and mice will be eradicated from relatively large, human-occupied islands such as Oahu in the near or distant future (Howald et al. 2007); and accepting this may be a first step towards increasing the likelihood of native species conservation in archipelagos like Hawaii where introduced rodents have established. Determining which invasive rodent species are present at a given site is important because the risks that some rodent species pose to particular (prey) species and/or habitats differ from those posed by other rodent species. Two sympatric species cannot occupy the same niche indefinitely, in a stable environment (Gause 1934), which may partly explain why some rodent species may not occur where others are present (Harper 2006). -
Pu'u Wa'awa'a Biological Assessment
PU‘U WA‘AWA‘A BIOLOGICAL ASSESSMENT PU‘U WA‘AWA‘A, NORTH KONA, HAWAII Prepared by: Jon G. Giffin Forestry & Wildlife Manager August 2003 STATE OF HAWAII DEPARTMENT OF LAND AND NATURAL RESOURCES DIVISION OF FORESTRY AND WILDLIFE TABLE OF CONTENTS TITLE PAGE ................................................................................................................................. i TABLE OF CONTENTS ............................................................................................................. ii GENERAL SETTING...................................................................................................................1 Introduction..........................................................................................................................1 Land Use Practices...............................................................................................................1 Geology..................................................................................................................................3 Lava Flows............................................................................................................................5 Lava Tubes ...........................................................................................................................5 Cinder Cones ........................................................................................................................7 Soils .......................................................................................................................................9 -
Recovery Plan for Tyoj5llllt . I-Bland Plants
Recovery Plan for tYOJ5llllt. i-bland Plants RECOVERY PLAN FOR MULTI-ISLAND PLANTS Published by U.S. Fish and Wildlife Service Portland, Oregon Approved: Date: / / As the Nation’s principal conservation agency, the Department of the Interior has responsibility for most ofour nationally owned public lands and natural resources. This includes fostering the wisest use ofour land and water resources, protecting our fish and wildlife, preserving the environmental and cultural values ofour national parks and historical places, and providing for the enjoyment of life through outdoor recreation. The Department assesses our energy and mineral resources and works to assure that their development is in the best interests ofall our people. The Department also has a major responsibility for American Indian reservation communities and for people who live in island Territories under U.S. administration. DISCLAIMER PAGE Recovery plans delineate reasonable actions that are believed to be required to recover and/or protect listed species. Plans are published by the U.S. Fish and Wildlife Service, sometimes prepared with the assistance ofrecovery teams, contractors, State agencies, and others. Objectives will be attained and any necessary funds made available subject to budgetary and other constraints affecting the parties involved, as well as the need to address other priorities. Costs indicated for task implementation and/or time for achievement ofrecovery are only estimates and are subject to change. Recovery plans do not necessarily represent the views nor the official positions or approval ofany individuals or agencies involved in the plan formulation, otherthan the U.S. Fish and Wildlife Service. They represent the official position ofthe U.S. -
Effect of Trap Color on Captures of Bark- and Wood-Boring Beetles
insects Article Effect of Trap Color on Captures of Bark- and Wood-Boring Beetles (Coleoptera; Buprestidae and Scolytinae) and Associated Predators Giacomo Cavaletto 1,*, Massimo Faccoli 1, Lorenzo Marini 1 , Johannes Spaethe 2 , Gianluca Magnani 3 and Davide Rassati 1,* 1 Department of Agronomy, Food, Natural Resources, Animals and Environment (DAFNAE), University of Padova, Viale dell’Università, 16–35020 Legnaro, Italy; [email protected] (M.F.); [email protected] (L.M.) 2 Department of Behavioral Physiology & Sociobiology, Biozentrum, University of Würzburg, Am Hubland, 97074 Würzburg, Germany; [email protected] 3 Via Gianfanti 6, 47521 Cesena, Italy; [email protected] * Correspondence: [email protected] (G.C.); [email protected] (D.R.); Tel.: +39-049-8272875 (G.C.); +39-049-8272803 (D.R.) Received: 9 October 2020; Accepted: 28 October 2020; Published: 30 October 2020 Simple Summary: Several wood-associated insects are inadvertently introduced every year within wood-packaging materials used in international trade. These insects can cause impressive economic and ecological damage in the invaded environment. Thus, several countries use traps baited with pheromones and plant volatiles at ports of entry and surrounding natural areas to intercept incoming exotic species soon after their arrival and thereby reduce the likelihood of their establishment. In this study, we investigated the performance of eight trap colors in attracting jewel beetles and bark and ambrosia beetles to test if the trap colors currently used in survey programs worldwide are the most efficient for trapping these potential forest pests. In addition, we tested whether trap colors can be exploited to minimize inadvertent removal of their natural enemies. -
List 01 Hawaiian Names 01 Plants
V\.{). 3 v BOTANICAL BULLETIN NO.2 JUNE. 1913 TERRITORY OF HAWAII BOARD OF AGRICULTURE AND FORESTRY List 01 Hawaiian Names 01 Plants BY JOSEPH F. ROCK Consulting Botanist, Board of Agriculture and Forestry HONOLULU: HAWAIIAN GAZETTE CO., LTD. 1913 ALPHABETICAL LIST OF HAWAIIAN NAMES OF PLANTS. The following list of Hawaiian plant-names has been compiled from various sources. Hillebrand in his valuable Flora of the Hawaiian Islands has given many Hawaiian names, especially of the more common species; these are incorporated in this list with a few corrections. Nearly all Hawaiian plant-names found in this list and not in Hillebrand's Flora were secured from Mr. Francis Gay of the Island of Kauai, an old resident in this Terri tory and well acquainted with its plants from a layman's stand point. It was the writer's privilege to camp with Mr. Gay in the mountains of Kauai collecting botanical material; for almost every species he could give the native name, which he had se cured in the early days from old and reliable natives. Mr. Gay had made spatter prints of many of the native plants in a large record book with their names and uses, as well as their symbolic meaning when occurring in mele (songs) or olioli (chants), at tached to them. For all this information the writer is indebted mainly to Mr. Francis Gay and also to Mr. Augustus F. Knudsen of the same Island. The writer also secured Hawaiian names from old na tives and Kahunas (priests) in the various islands of the group. -
United States of America
anran Forestry Department Food and Agriculture Organization of the United Nations GLOBAL FOREST RESOURCES ASSESSMENT COUNTRY REPORTS NITED TATES OF MERICA U S A FRA2005/040 Rome, 2005 FRA 2005 – Country Report 040 UNITED STATES OF AMERICA The Forest Resources Assessment Programme Sustainably managed forests have multiple environmental and socio-economic functions important at the global, national and local scales, and play a vital part in sustainable development. Reliable and up- to-date information on the state of forest resources - not only on area and area change, but also on such variables as growing stock, wood and non-wood products, carbon, protected areas, use of forests for recreation and other services, biological diversity and forests’ contribution to national economies - is crucial to support decision-making for policies and programmes in forestry and sustainable development at all levels. FAO, at the request of its member countries, regularly monitors the world’s forests and their management and uses through the Forest Resources Assessment Programme. This country report forms part of the Global Forest Resources Assessment 2005 (FRA 2005), which is the most comprehensive assessment to date. More than 800 people have been involved, including 172 national correspondents and their colleagues, an Advisory Group, international experts, FAO staff, consultants and volunteers. Information has been collated from 229 countries and territories for three points in time: 1990, 2000 and 2005. The reporting framework for FRA 2005 is based on the thematic elements of sustainable forest management acknowledged in intergovernmental forest-related fora and includes more than 40 variables related to the extent, condition, uses and values of forest resources. -
Sato Hawii 0085O 10652.Pdf
RESTORATION OF HAWAIIAN TROPICAL DRY FORESTS: A BIOCULTURAL APPROACH A THESIS SUBMITTED TO THE GRADUATE DIVISION OF THE UNIVERSITY OF HAWAI‘I AT MĀNOA IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF MASTER OF SCIENCE IN BOTANY (CONSERVATION BIOLOGY) MAY 2020 By Aimee Y. Sato Thesis Committee: Tamara Ticktin, Chairperson Christian P. Giardina Rakan A. Zahawi Kewords: Tropical Dry Forest, Biocultural, Conservation, Restoration, Natural Regeneration, Social-Ecological 1 ACKNOWLEDGEMENTS I thank my graduate committee for steering and guiding me through my thesis work. Dr. Tamara Ticktin, my thesis advisor who has been the greatest kumu (teacher) that I could have asked for in my research. I also thank my two committee members, Dr. Rakan A. Zahawi and Dr. Christian P. Giardina, who both brought their expansive levels of expertise to help develop this thesis. Thank you so much to the hoaʻāina (caretakers/restoration managers) of my two project sites. I thank the hoaʻāina of Kaʻūpūlehu, ‘Aunty’ Yvonne Carter, ‘Uncle’ Keoki Carter, Wilds Brawner, Kekaulike Tomich, Lehua Alapai, Kuʻulei Keakealani, and ‘Aunty’ Hannah Kihalani Springer. Thank you to the hoaʻāina of Auwahi, Art Medeiros, Erica von-Allmen, Ainoa and Kalaʻau Kaiaokamalie, Amy Campbell, Andy Bieber, Robert Pitts, and Kailie Aina. I would also like to acknowledge Kamehameha Schools and the Ulupalakua Ranch for allowing me to conduct this research on their lands. Thank you to the dry forest restoration managers and researchers that participated in the overview survey of Hawaiian dry forests. On Oʻahu Island: Lorena ‘Tap’ Wada, James Harmon and Kapua Kawelo. On Hawaiʻi Island: Elliott Parsons, Rebecca Most, Lena Schnell, Kalā Asing, Jen Lawson, and Susan Cordell. -
Xylosandrus Compactus (Coleoptera: Scolytidae - Black Twig Borer) Is a Highly Polyphagous Pest of Woody Plants Which Has Recently Been Reported from Italy and France
EPPO, 2020 Mini data sheet on Xylosandrus compactus Added to the EPPO Alert List in 2017 – Deleted in 2020 Reasons for deletion: Xylosandrus compactus and its associated fungi have been included in EPPO Alert List for more than 3 years and during this period no particular international action was requested by the EPPO member countries. In 2020, the Working Party on Phytosanitary Regulations agreed that it could be deleted, considering that sufficient alert has been given. Why: Xylosandrus compactus (Coleoptera: Scolytidae - black twig borer) is a highly polyphagous pest of woody plants which has recently been reported from Italy and France. It probably originates from Asia and has been introduced to other parts of the world, most probably with trade of plants and wood. In parts of Italy (Lazio), serious damage has recently been observed on Mediterranean maquis plants in a natural environment. As this pest might also present a risk to many woody plants in nurseries, plantations, orchards, parks and gardens, scientists who had observed this outbreak in Lazio recommended that X. compactus should be added to the EPPO Alert List. Where: X. compactus is widely distributed in Africa, Asia and South America. It has been introduced in the Pacific Islands, New Zealand, Southeastern USA, and more recently in Europe in Italy and Southern France. X. compactus is thought to originate from East Asia. EPPO region: Italy (first found in 2011 - Campania, Lazio, Liguria, Sicilia and Toscana), France (first found in 2016 - Provence-Alpes-Côte-d’Azur region), Greece (first found in 2019), Spain (Baleares only). Africa: Benin, Cameroon, Central African Republic, Comoros, Congo, Congo (Democratic Republic of), Cote d'Ivoire, Equatorial Guinea, Gabon, Ghana, Guinea, Guinea-Bissau, Kenya, Liberia, Madagascar, Mauritania, Mauritius, Nigeria, Reunion, Senegal, Seychelles, Sierra Leone, South Africa, Tanzania, Togo, Uganda, Zimbabwe. -
5-Year Review Summary and Evaluation
Spermolepis hawaiiensis (no common name) 5-Year Review Summary and Evaluation U.S. Fish and Wildlife Service Pacific Islands Fish and Wildlife Office Honolulu, Hawaii 5-YEAR REVIEW Species reviewed: Spermolepis hawaiiensis (no common name) TABLE OF CONTEN TS 1.0 GENERAL IN FORMATION .......................................................................................... 1 1.1 Reviewers ....................................................................................................................... 1 1.2 Methodology used to complete the review:................................................................. 1 1.3 Background: .................................................................................................................. 1 2.0 REVIEW ANALYSIS....................................................................................................... 3 2.1 Application of the 1996 Distinct Population Segment (DPS) policy ......................... 3 2.2 Recovery Crite ria .......................................................................................................... 4 2.3 Updated Information and Current Species Status .................................................... 5 2.4 Synthesis......................................................................................................................... 8 3.0 RESULTS ........................................................................................................................ 15 3.3 Recommended Classification: ................................................................................... -
Auwahi: Ethnobotany of a Hawaiian Dryland Forest
AUWAHI: ETHNOBOTANY OF A HAWAIIAN DRYLAND FOREST. A. C. Medeiros1, C.F. Davenport2, and C.G. Chimera1 1. U.S. Geological Survey, Biological Resources Division, Haleakala Field Station, P.O. Box 369, Makawao, HI 96768 2. Social Sciences Department, Maui Community College, 310 Ka’ahumanu Ave., Kahului, HI 96732 ABSTRACT Auwahi district on East Maui extends from sea level to about 6800 feet (1790 meters) elevation at the southwest rift of leeward Haleakal¯a volcano. In botanical references, Auwahi currently refers to a centrally located, fairly large (5400 acres) stand of diverse dry forest at 3000-5000 feet (915- 1525 meters) elevation surrounded by less diverse forest and more open-statured shrubland on lava. Auwahi contains high native tree diversity with 50 dryland species, many with extremely hard, durable, and heavy wood. To early Hawaiians, forests like Auwahi must have seemed an invaluable source of unique natural materials, especially the wide variety of woods for tool making for agriculture and fishing, canoe building, kapa making, and weapons. Of the 50 species of native trees at Auwahi, 19 species (38%) are known to have been used for medicine, 13 species (26%) for tool-making, 13 species (26%) for canoe building 13 species (26%) for house building, 8 species (16%) for tools for making kapa, 8 species (16%) for weapons 8 species (16%) for fishing, 8 species (16%) for dyes, and 7 species (14 %) for religious purposes. Other miscellaneous uses include edible fruits or seeds, bird lime, cordage, a fish narcotizing agent, firewood, a source of "fireworks", recreation, scenting agents, poi boards, and h¯olua sled construction. -
Forestry Department Food and Agriculture Organization of the United Nations
Forestry Department Food and Agriculture Organization of the United Nations Forest Health & Biosecurity Working Papers OVERVIEW OF FOREST PESTS THAILAND January 2007 Forest Resources Development Service Working Paper FBS/32E Forest Management Division FAO, Rome, Italy Forestry Department Overview of forest pests – Thailand DISCLAIMER The aim of this document is to give an overview of the forest pest1 situation in Thailand. It is not intended to be a comprehensive review. The designations employed and the presentation of material in this publication do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations concerning the legal status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. © FAO 2007 1 Pest: Any species, strain or biotype of plant, animal or pathogenic agent injurious to plants or plant products (FAO, 2004). ii Overview of forest pests – Thailand TABLE OF CONTENTS Introduction..................................................................................................................... 1 Forest pests...................................................................................................................... 1 Naturally regenerating forests..................................................................................... 1 Insects ..................................................................................................................... 1 Diseases..................................................................................................................