Diffuse Knapweed (Centaurea Diffusa): Reproductive Thresholds, Population Ecology and Responses to the Introduction of the Buprestid Beetle Sphenoptera Jugoslavica
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Integrated Noxious Weed Management Plan: US Air Force Academy and Farish Recreation Area, El Paso County, CO
Integrated Noxious Weed Management Plan US Air Force Academy and Farish Recreation Area August 2015 CNHP’s mission is to preserve the natural diversity of life by contributing the essential scientific foundation that leads to lasting conservation of Colorado's biological wealth. Colorado Natural Heritage Program Warner College of Natural Resources Colorado State University 1475 Campus Delivery Fort Collins, CO 80523 (970) 491-7331 Report Prepared for: United States Air Force Academy Department of Natural Resources Recommended Citation: Smith, P., S. S. Panjabi, and J. Handwerk. 2015. Integrated Noxious Weed Management Plan: US Air Force Academy and Farish Recreation Area, El Paso County, CO. Colorado Natural Heritage Program, Colorado State University, Fort Collins, Colorado. Front Cover: Documenting weeds at the US Air Force Academy. Photos courtesy of the Colorado Natural Heritage Program © Integrated Noxious Weed Management Plan US Air Force Academy and Farish Recreation Area El Paso County, CO Pam Smith, Susan Spackman Panjabi, and Jill Handwerk Colorado Natural Heritage Program Warner College of Natural Resources Colorado State University Fort Collins, Colorado 80523 August 2015 EXECUTIVE SUMMARY Various federal, state, and local laws, ordinances, orders, and policies require land managers to control noxious weeds. The purpose of this plan is to provide a guide to manage, in the most efficient and effective manner, the noxious weeds on the US Air Force Academy (Academy) and Farish Recreation Area (Farish) over the next 10 years (through 2025), in accordance with their respective integrated natural resources management plans. This plan pertains to the “natural” portions of the Academy and excludes highly developed areas, such as around buildings, recreation fields, and lawns. -
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 SUDAN January 2007 Forest Resources Development Service Working Paper FBS/31E Forest Management Division FAO, Rome, Italy Forestry Department Overview of forest pests – Sudan DISCLAIMER The aim of this document is to give an overview of the forest pest1 situation in the Sudan. 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 – Sudan TABLE OF CONTENTS Introduction..................................................................................................................... 1 Forest pests and diseases................................................................................................. 1 Naturally regenerating forests..................................................................................... 1 Insects ..................................................................................................................... 1 Diseases.................................................................................................................. -
Weed Biocontrol: Extended Abstracts from the 1997 Interagency Noxious-Weed Symposium
Weed Biocontrol: Extended Abstracts from the 1997 Interagency Noxious-Weed Symposium Dennis Isaacson Martha H. Brookes Technical Coordinators U.S. Department of Agriculture Forest Service Forest Health Technology Enterprise Team Morgantown, WV and Oregon Department of Agriculture Salem, OR June 1999 ACKNOWLEDGMENTS Many of the tasks of organizing a symposium such as this — and there are many — are not obvious, and, if they are handled well, the effort that goes into them can easily be overlooked. Sherry Kudna of the Oregon Department of Agriculture Weed Control staff managed most of the arrangements and took care of many, many details, which helped the symposium run smoothly. We truly appreciate her many contributions. We also acknowledge the contributions of the presenters. They not only organized their own presentations and manuscripts, but also assisted with reviewing drafts of each other’s papers in the proceedings. Several of the presenters also covered their own expenses. Such dedication speaks well of their commitment to improving the practice of weed biocontrol. Both the Oregon State Office of the Bureau of Land Management and the USDA Forest Service made major contributions to supporting the symposium. Although several individuals from both organizations provided assistance, we especially note the encouragement and advice of Bob Bolton, Oregon Bureau of Land Management Weed Control Coordinator, and the willingness to help and financial support for publishing this document from Richard C. Reardon, Biocontrol/Biopesticides Program Manager, USDA Forest Service's Forest Health Technology Enterprise Team, Morgantown, WV. We thank Tinathan Coger for layout and design and Patricia Dougherty for printing advice and coordination of the manuscript We also thank Barbra Mullin, Montana State Department of Agriculture, who delivered the keynote address; Tami Lowry, Pacific Northwest Research Station, Corvallis, who helped format the document; and Eric Coombs, who provided the photographs of weeds and agents that convey the concepts of weed biocontrol. -
Karyotype Analysis of Four Jewel-Beetle Species (Coleoptera, Buprestidae) Detected by Standard Staining, C-Banding, Agnor-Banding and CMA3/DAPI Staining
COMPARATIVE A peer-reviewed open-access journal CompCytogen 6(2):Karyotype 183–197 (2012) analysis of four jewel-beetle species (Coleoptera, Buprestidae) .... 183 doi: 10.3897/CompCytogen.v6i2.2950 RESEARCH ARTICLE Cytogenetics www.pensoft.net/journals/compcytogen International Journal of Plant & Animal Cytogenetics, Karyosystematics, and Molecular Systematics Karyotype analysis of four jewel-beetle species (Coleoptera, Buprestidae) detected by standard staining, C-banding, AgNOR-banding and CMA3/DAPI staining Gayane Karagyan1, Dorota Lachowska2, Mark Kalashian1 1 Institute of Zoology of Scientific Center of Zoology and Hydroecology, National Academy of Sciences of Armenia, P. Sevak 7, Yerevan 0014, Armenia 2 Department of Entomology, Institute of Zoology Jagiellonian University, Ingardena 6, 30-060 Krakow, Poland Corresponding author: Gayane Karagyan ([email protected]) Academic editor: Robert Angus | Received 15 February 2012 | Accepted 17 April 2012 | Published 27 April 2012 Citation: Karagyan G, Lachowska D, Kalashian M (2012) Karyotype analysis of four jewel-beetle species (Coleoptera, Buprestidae) detected by standard staining, C-banding, AgNOR-banding and CMA3/DAPI staining. Comparative Cytogenetics 6(2): 183–197. doi: 10.3897/CompCytogen.v6i2.2950 Abstract The male karyotypes of Acmaeodera pilosellae persica Mannerheim, 1837 with 2n=20 (18+neoXY), Sphe- noptera scovitzii Faldermann, 1835 (2n=38–46), Dicerca aenea validiuscula Semenov, 1895 – 2n=20 (18+Xyp) and Sphaerobothris aghababiani Volkovitsh et Kalashian, 1998 – 2n=16 (14+Xyp) were studied using conventional staining and different chromosome banding techniques: C-banding, AgNOR-band- ing, as well as fluorochrome Chromomycin 3A (CMA3) and DAPI. It is shown that C-positive segments are weakly visible in all four species which indicates a small amount of constitutive heterochromatin (CH). -
Contribution to the Knowledge of the Jewel Beetles (Coleoptera: Buprestidae) Fauna of Kurdistan Province of Iran. Part 1. Subfam
Кавказский энтомол. бюллетень 8(2): 232–239 © CAUCASIAN ENTOMOLOGICAL BULL. 2012 Contribution to the knowledge of the jewel beetles (Coleoptera: Buprestidae) fauna of Kurdistan Province of Iran. Part 1. Subfamilies julodinae, Polycestinae and Chrysochroinae Материалы к изучению фауны жуков-златок (Coleoptera: Buprestidae) провинции Курдистан, Иран. Часть 1. Подсемейства Julodinae, Polycestinae и Chrysochroinae H. Ghobari1, M.Yu. Kalashian2, J. Nozari1 Х. Гобари1, М.Ю. Калашян2, Дж. Нозари1 1Department of Plant Protection, University College of Agriculture and Natural Resources, University of Tehran, PO Box 4111, Karaj, Iran. E-mail: [email protected], [email protected] 2Institute of Zoology, Scientific Centre of Zoology and Hydroecology of the National Academy of Sciences of Armenia, P. Sevak str., 7, Yerevan 0014 Armenia. Email: [email protected] 1Отдел защиты растений Университетского колледжа сельского хозяйства и природных ресурсов Тегеранского университета, PO Box 4111, Карадж, Иран 2Иститут Зоологии, Научный центр зоологии и гидроэкологии НАН РА, ул. П. Севака, 7, Ереван 0014 Армения Key words: Coleoptera, Buprestidae, Iran, Kurdistan, fauna, new records. Ключевые слова: Coleoptera, Buprestidae, Иран, Курдистан, фауна, новые указания. Abstract. 60 species of jewel-beetles (Coleoptera: and some identifications are obviously wrong. So, faunistic Buprestidae) belonging to three subfamilies (Julodinae, composition of the fauna of Kurdistan has to be clarified. In Polycestinae and Chrysochroinae) were collected in this paper the results of study of material collected by one Kurdistan Province of Iran during 2009–2011. Of these of the authors (H. Ghobari) in 2009–2011 in the province 7 species from 6 genera are new for Iranian fauna and are presented; in general 60 species were collected, 7 of 41 species from 9 genera are new for Kurdistan them are new for Iranian fauna and 41 – for the fauna of Province. -
Enhancing the Effectiveness of Biological Control Programs Of
Enhancing the Effectiveness of Biological Control Programs of Invasive Species by Utilizing an Integrated Pest Management Approach Approved by ISAC on October 30, 2015 Preface Invasive species threaten agriculture and natural ecosystems. Methods for control and management have evolved over time, and often rely on combinations of techniques and long-term planning. This white paper discusses the benefits and increased potential for long-term success of invasive species biological control programs when utilizing an Integrated Pest Management (IPM) approach. Integrated control was first defined by Stern et al. (1959) as applied insect pest control, which combines and integrates biological control and chemical control to maintain a pest population below an economic injury level. Integrated control has evolved over time to include all taxa, as well as prevention, other control, and ecological, health and economic aspects. IPM emphasizes long-term prevention of damage through the utilization of various techniques such as chemical control, biological control, physical control, habitat manipulation, modification of cultural practices and resistant varieties using combinations that are compatible and produce the desired outcome. An IPM approach can be implemented in agricultural, residential, and natural areas (www.ipm.ucdavis.edu/GENERAL/ipmdefinition.html). Biological control is an integral component of IPM programs and has far greater potential for success when used in an IPM system. Land managers rely on information provided by researchers during the time period leading up to the release of the biological control agent (generally an insect or pathogen), to help guide them on the best procedures, approaches and use of the agent. As the number of biological control programs increase, information from successful and unsuccessful programs can be used to increase the chances for the successful establishment of biological control agents in the future. -
Biocontrol Field Guide for Utah
Special Thanks : Many of the pictures in this field guide came from Jerry Caldwell and Morgan Mendenhall. Thank you for the use of your excellent pictures. Also to: Morgan Mendenhall for editing this field guide. Jerry Caldwell, Tooele County Weed Supervisor, for your help and support. Phil McCraley, Salt Lake County Weed Supervisor, for your encouragement and enthusiasm. Sage Fitch for your advice and assistance. Bonneville CWMA 2 Table of Contents : Dalmatian Toadflax ...................................................................................... 7 Mecinus janthinus ................................................................................ 9 Field Bindweed .......................................................................................... 11 Aceria malherbae ............................................................................... 13 Diffuse Knapweed ...................................................................................... 15 Spotted Knapweed ..................................................................................... 17 Squarrose Knapweed ................................................................................ 19 Cyphocleonus achates ....................................................................... 21 Larinus minutus ................................................................................. 23 Sphenoptera jugoslavica ................................................................... 25 Urophora affinis ............................................................................... -
Myers, J.H. 2007. How Many and What Kind of Biological
BiologicalJ.H. Myers Control of Diffuse Knapweed 9 How Many and What Kind of Agents for the Biological Control of Weeds: a Case Study with Diffuse Knapweed JUDITH H. MYERS Departments of Zoology and Agroecology, University of British Columbia, 6270 University Blvd, Vancouver, British Columbia V6T 1Z4, Canada, [email protected] Overview: Following its introduction to North America, diffuse knapweed came to occupy millions of hectares of rangeland. This is the story of biological control efforts done over 25 years before an effective agent was introduced. The moral is that for optimal success of biological control, thorough work should be done to understand the ecology of the target weed and its natural enemies. Effective agents are unlikely to be abundant in the native habitat, but are likely to be able to kill the plants in the exotic habitat. Introduction Classical biological control of weeds is the introduction of natural enemies from native areas to exotic sites where their host plants have become invasive and detrimental (overview in Myers and Bazely, 2003). Three important questions that confront biological control practitioners are: (i) which species of agent are safe to introduce; (ii) what types of agents are the most likely to be effective con- trols; and (iii) how many different species of agents should be introduced? Here I describe the biological control programme against diffuse knapweed, Centaurea diffusa, which involved the introduction of 13 species and the establishment of 11 agents over a 20-year period (Bourchier et al., 2002). This is a story of a programme based on the premise that multiple species of agents would be nec- essary for successful control (Harris, 1981). -
Enhancing the Effectiveness of Biological Control Programs of Invasive Species by Utilizing an Integrated Pest Management Approa
U.S. Department of the Interior Oce of the Secretary C Street Washington, DC Enhancing the Effectiveness of Biological Control Programs of Invasive Species by Utilizing an Integrated Pest Management Approach Approved by isac on October 30, 2015 • the economic costs and benefits of anipm approach. Imple- PREFACE menting such efforts may increase the success of biological control efforts and the confidence of private and public land Invasive species threaten agriculture and natural ecosys- managers when making decisions about integrated invasive tems. Methods for control and management have evolved species management programs. over time, and often rely on combinations of techniques and This white paper will discuss: long-term planning. This white paper discusses the benefits and increased potential for long-term success of invasive spe- • benefits for biological control efforts through inclusion cies biological control programs when utilizing an Integrated in an ipm approach; Pest Management (ipm) approach. • partnership programs to facilitate the incorporation of Integrated control was first defined by Stern et al. (1959) as biological control in ipm programs of invasive species; applied insect pest control, which combines and integrates • incorporation of long-term stewardship in biological biological control and chemical control to maintain a pest control programs; population below an economic injury level. Integrated control • model program for integrated biological control of an has evolved over time to include all taxa, as well as prevention, invasive species; other control, and ecological, health, and economic aspects. • ecological approaches to maximize success of biological ipm emphasizes long-term prevention of damage through the control; utilization of various techniques such as chemical control, • genetic advances in biological control. -
Field Guide to the Biological Control of Weeds in British Columbia
forestryweeds7.qxd 11/14/99 7:42 PM Page 109 BEETLE Galerucella pusilla (Duftsschmid) (Coleoptera: Chrysomelidae) DESCRIPTION AND LIFE CYCLE Adults, 2±4 mm long, and larvae very closely resemble G. calmariensis. Refer to G. calmariensis photos for identification. Adults emerge from hibernation and feed on shoot tips and young leaves in April. Mating begins immediately, with egg laying starting approximately 1 week later and continuing until the end of July. Larvae hatch 12 days after egg laying; larvae develop over the next 2 weeks feeding first on leaf and flower buds and then on all parts of the plant in the later stages of development. Mature larvae leave the plant and pupate in leaf litter and the upper portion of the soil. Adults emerge 9±11 days later. Adults that emerge before August mate and lay eggs for a 1 month period. Adults feed on foliage and hibernate in the soil before winter. WEED ATTACKED Purple loosestrife. HABITAT Egg laying is strongly curtailed by low temperatures. Tolerates the variety of habitat conditions in which purple loosestrife is found. COLLECTION, SHIPPING, AND HANDLING Collect with the sweep net technique and use standard shipping and handling procedures. RELEASE Follow standard release procedures for insects. Take precautions not to dump the beetles in the water. MONITORING Determine presence by looking for adults on foliage in April or August. REFERENCE Blossey, B. and D. Schroeder. 1991. Study of potential biological control agents of purple loosestrife (Lythrum salicaria L.). Final Report. European Station Report. C.A.B. International Institute of Biological Control, Delemont, Switzerland. -
Chapter 12. Biocontrol Arthropods: New Denizens of Canada's
291 Chapter 12 Biocontrol Arthropods: New Denizens of Canada’s Grassland Agroecosystems Rosemarie De Clerck-Floate and Héctor Cárcamo Agriculture and Agri-Food Canada, Lethbridge Research Centre 5403 - 1 Avenue South, P.O. Box 3000 Lethbridge, Alberta, Canada T1J 4B1 Abstract. Canada’s grassland ecosystems have undergone major changes since the arrival of European agriculture, ranging from near-complete replacement of native biodiversity with annual crops to the effects of overgrazing by cattle on remnant native grasslands. The majority of the “agroecosystems” that have replaced the historical native grasslands now encompass completely new associations of plants and arthropods in what is typically a mix of introduced and native species. Some of these species are pests of crops and pastures and were accidentally introduced. Other species are natural enemies of these pests and were deliberately introduced as classical biological control (biocontrol) agents to control these pests. To control weeds, 76 arthropod species have been released against 24 target species in Canada since 1951, all of which also have been released in western Canada. Of these released species, 53 (70%) have become established, with 18 estimated to be reducing target weed populations. The biocontrol programs for leafy spurge in the prairie provinces and knapweeds in British Columbia have been the largest, each responsible for the establishment of 10 new arthropod species on rangelands. This chapter summarizes the ecological highlights of these programs and those for miscellaneous weeds. Compared with weed biocontrol on rangelands, classical biocontrol of arthropod crop pests by using arthropods lags far behind, mostly because of a preference to manage crop pests with chemicals. -
Classical Biocontrol of Weeds: Its Definitions, Selection of Effective Agents, and Administrative-Political Problems1
Reprinted with permission from: The Canadian Entomologist. 1991. 123:827-849. Published and copyrighted by: Entomological Society of Canada. Email: [email protected] Classical biocontrol of weeds: Its definitions, selection of effective agents, and 1 administrative-political problems P. HARRIS Abstract: Dilemmas in weed biocontrol are wide ranging. Even the term biological control is confusing as meanings may be restricted to the use of parasites and predators or extend to the use of all non-chemical means of control. Another problem is that two-thirds of the agents released do not become numerous enough to inflict major damage to the weed population, al- though this statistic is misleading as it includes agents costing little in pre- release studies where failure is of little consequence and those costing about two scientist years each, or currently about $400,000. Many of the suggestions for improvement are costly and time consuming. Delay is un- acceptable where agent release is seen by sponsors as a mark of progress in a program likely to require 20 years and funding is difficult. Analysis of previous biocontrol attempts for attributes of “success” have been disap- pointing, partly because there are a number of steps involved, each with its own attributes. This paper recognizes four graded “success” steps and dis- cusses many agent selection methods. There are public demands for a change in emphasis from chemical to bio- logical control; but in the absence of effective enabling legislation, the practice of biocontrol can be legally and politically hazardous; biocontrol should be carried out by a multi-disciplinary team but it is usually as- signed to a single scientist; it needs to branch in new directions to remain scientifically stimulating, but this increases the risk of failure.