25 Oomycete Diseases
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The Origin and Distribution of Phytophthora Cinnamomi
THE ORIGIN AND DISTRIBUTION OF PHYTOPHTHORA CINNAMOMI RANDS IN AUSTRALIAN NATIVE PLANT COMMUNITIES AND THE SIGNIFICANCE OF ITS ASSOCIATION WITH PARTICULAR PLANT SPECIES By B. H. PRATT* and W. A. HEATHER* [Manuscript received 23 October 1972] Abstract The origin, distribution, and disease association of P. cinnamomi in native plant communities in Australia has been examined. The fungus was isolated from the root zones of 31 plant genera in 16 families and is widespread throughout eastern and southern Australia and south-western Western Australia. Although the fungus is associated with disease in native plant communities it is also present in apparently non-diseased communities. Disease occurs usually only in environments disturbed by man, probably as a result of increase in population or activity of pre-existing fungal populations. The widespread distribution of P. cinnamomi in native vegetation in Australia, its occurrence in remote, undisturbed areas, and the apparent balance it has achieved with plant species of differing susceptibility to disease in some natural, undisturbed areas suggests that the fungus is likely to be indigenous to eastern Australia. Further, it may be partly responsible for the localized distribution of some plant species. I. INTRODUCTION The soil-borne fungus Phytophthora cinnamomi Rands is widely distributed in Australia, in horticultural plantings (Zentmyer and Thorn 1967; Pratt and Wrigley 1970; as well as personal communications from the New South Wales Department of Agriculture, Tasmanian Department of Agriculture, Victorian Department of Agriculture, and the Queensland Department of Primary Industries), and in conifer nurseries and plantings (Oxenham and Winks 1963; Bertus 1968; and personal communications from the New South Wales Forestry Commission, and the Queens land Department of Forestry). -
The Interaction of Drought and the Outbreak of Phoracantha
The interaction of drought and the outbreak of Phoracantha semipunctata (Coleoptera: Cerambycidae) on tree collapse in the Northern Jarrah (Eucalyptus marginata) forest. by Stephen Seaton (BSc Environmental Science) This thesis is presented in partial fulfilment of the requirements for the degree of Bachelor of Science (Honours) School of Biological Sciences and Biotechnology, Murdoch University, Perth, Western Australia November 2012 ii Declaration I declare that that the work contained within this thesis is an account of my own research, except where work by others published or unpublished is noted, while I was enrolled in the Bachelor of Science with Honours degree at Murdoch University, Western Australia. This work has not been previously submitted for a degree at any institution. Stephen Seaton November 2012 iii Conference Presentations Seaton, S.A.H., Matusick, G., Hardy, G. 2012. Drought induced tree collapse and the outbreak of Phoracantha semipunctata poses a risk for forest under climate change. Abstract presented at the Combined Biological Sciences Meeting (CBSM) 2012, 24th of August. University Club, University of Western Australia. Seaton, S.A.H., Matusick, G., Hardy, G. 2012. Occurrence of Eucalyptus longicorn borer (Phoracantha semipunctata) in the Northern Jarrah Forest following severe drought. To be presented at The Australian Entomological Society - 43rd AGM & Scientific Conference and Australasian Arachnological Society - 2012 Conference. 25th – 28th November. The Old Woolstore, Hobart. iv Acknowledgments I greatly appreciate the guidance, enthusiasm and encouragement and tireless support from my supervisors Dr George Matusick and Prof Giles Hardy in the Centre of Excellence for Climate Change Forests and Woodland Health. I particularly appreciate the interaction and productive discussions regarding forest ecology and entomology and proof reading the manuscript. -
Methods and Work Profile
REVIEW OF THE KNOWN AND POTENTIAL BIODIVERSITY IMPACTS OF PHYTOPHTHORA AND THE LIKELY IMPACT ON ECOSYSTEM SERVICES JANUARY 2011 Simon Conyers Kate Somerwill Carmel Ramwell John Hughes Ruth Laybourn Naomi Jones Food and Environment Research Agency Sand Hutton, York, YO41 1LZ 2 CONTENTS Executive Summary .......................................................................................................................... 8 1. Introduction ............................................................................................................ 13 1.1 Background ........................................................................................................................ 13 1.2 Objectives .......................................................................................................................... 15 2. Review of the potential impacts on species of higher trophic groups .................... 16 2.1 Introduction ........................................................................................................................ 16 2.2 Methods ............................................................................................................................. 16 2.3 Results ............................................................................................................................... 17 2.4 Discussion .......................................................................................................................... 44 3. Review of the potential impacts on ecosystem services ....................................... -
Assessment of Forest Pests and Diseases in Protected Areas of Georgia Final Report
Assessment of Forest Pests and Diseases in Protected Areas of Georgia Final report Dr. Iryna Matsiakh Tbilisi 2014 This publication has been produced with the assistance of the European Union. The content, findings, interpretations, and conclusions of this publication are the sole responsibility of the FLEG II (ENPI East) Programme Team (www.enpi-fleg.org) and can in no way be taken to reflect the views of the European Union. The views expressed do not necessarily reflect those of the Implementing Organizations. CONTENTS LIST OF TABLES AND FIGURES ............................................................................................................................. 3 ABBREVIATIONS AND ACRONYMS ...................................................................................................................... 6 EXECUTIVE SUMMARY .............................................................................................................................................. 7 Background information ...................................................................................................................................... 7 Literature review ...................................................................................................................................................... 7 Methodology ................................................................................................................................................................. 8 Results and Discussion .......................................................................................................................................... -
Taro Leaf Blight
Plant Disease July 2011 PD-71 Taro Leaf Blight in Hawai‘i Scot Nelson,1 Fred Brooks,1 and Glenn Teves2 1Department of Plant and Environmental Protection Sciences, Honolulu, HI 2 Department of Tropical Plant and Soil Sciences, Moloka‘i Extension Office, Ho‘olehua, HI aro (Colocasia es- ha (2.8 US tons/acre) Tculenta (L.) Schott) (FAOSTAT 2010 esti- grows in Hawai‘i and mates; Ramanatha et throughout the tropical al. 2010). Pacific as an edible In 2009, approx- aroid of historical and imately 1814 tonnes contemporary signifi- (2,000 US tons) of C. cance (Figure 1). Farmers esculenta were har- cultivate kalo (Hawaiian vested in Hawai‘i from for taro) in wet lowland 100 farms on 180 ha (Figure 2) or dryland (445 acres). More than (Figure 3) taro patches 80% of Hawai‘i’s pres- for its starchy, nutritious ent-day taro production corms. The heart-shaped occurs on the island of leaves are edible and Kaua‘i. The farm value can also serve as food Figure 1. A taro (Colocasia esculenta) patch in Hawai‘i. of Hawai‘i’s taro crop wrappings. Historically, in 2009 exceeded $2.4 taro crops provided nutritious food that helped early million (United States Department of Agriculture Polynesians to successfully colonize the Hawaiian 2011). Processors use mature corms of Hawaiian Islands. cultivars to make poi by steaming and macerating “Taro” refers to plants in one of four genera the taro. Cultivars processed into poi commercially within the family Araceae: Colocasia, Xanthosoma, are predominantly ‘Lehua’ types, and to a lesser Alocasia, and Cyrtosperma. -
Cultivar Resistance to Taro Leaf Blight Disease in American Samoa
Technical Report No. 34 Cultivar Resistance to Taro Leaf Blight Disease in American Samoa Fred E. Brooks, Plant Pathologist 49 grow poorly under severe blight conditions, their ABSTRACT reduced height and leaf surface should not raise the level of spores in the field enough to threaten A taro leaf blight (TLB) epidemic struck cultivar resistance. Further, American Samoans American Samoa and (Western) Samoa in 1993- are accepting the taste and texture of the new 1994, almost eliminating commercial and cultivars and planting local taro appears to have subsistence taro production (Colocasia declined. esculenta). In 1997, leaf blight-resistant cultivars from Micronesia were introduced into American Samoa. Some farmers, however, still try to raise INTRODUCTION severely diseased local cultivars among the resistant taro. This practice may increase the Taro has been a sustainable crop and dietary number of fungus spores in the field produced staple in the Pacific Islands for thousands of years by Phytophthora colocasiae and endanger plant (Ferentinos 1993). In American Samoa, it is resistance. The objective of this study was to grown on most family properties and is an determine the effect of interplanting resistant and important part of Fa’a Samoa traditional susceptible taro cultivars on TLB resistance and Samoan culture. Local production of taro, yield. Two resistant cultivars from the Republic Colocasia esculenta (L.) Schott, was devastated of Palau, P16 (Meltalt) and P20 (Dirratengadik), by an epidemic of taro leaf blight (TLB) in late were planted in separate plots and interplanted 1993-1994 (Trujillo et al. 1997). Taro production with Rota (Antiguo), a cultivar assumed to be fell from 357,000 kg (786,000 lb) per year before susceptible to TLB. -
Can Phytophthora Quercina Have a Negative Impact on Mature Pedunculate Oaks Under Field Conditions? Ulrika Jönsson-Belyazio, Ulrika Rosengren
Can Phytophthora quercina have a negative impact on mature pedunculate oaks under field conditions? Ulrika Jönsson-Belyazio, Ulrika Rosengren To cite this version: Ulrika Jönsson-Belyazio, Ulrika Rosengren. Can Phytophthora quercina have a negative impact on mature pedunculate oaks under field conditions?. Annals of Forest Science, Springer Nature (since 2011)/EDP Science (until 2010), 2006, 63 (7), pp.661-672. hal-00884017 HAL Id: hal-00884017 https://hal.archives-ouvertes.fr/hal-00884017 Submitted on 1 Jan 2006 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Ann. For. Sci. 63 (2006) 661–672 661 c INRA, EDP Sciences, 2006 DOI: 10.1051/forest:2006047 Original article Can Phytophthora quercina have a negative impact on mature pedunculate oaks under field conditions? Ulrika J¨ -B*, Ulrika R Plant Ecology and Systematics, Department of Ecology, Ecology Building, Lund University, 223 62 Lund, Sweden (Received 26 September 2005; accepted 10 March 2006) Abstract – Ten oak stands in southern Sweden were investigated to evaluate the impact of the root pathogen Phytophthora quercina on mature oaks under field conditions. Phytophthora quercina was present in five of the stands, while the other five stands were used as controls to verify the effect of the pathogen. -
Presidio Phytophthora Management Recommendations
2016 Presidio Phytophthora Management Recommendations Laura Sims Presidio Phytophthora Management Recommendations (modified) Author: Laura Sims Other Contributing Authors: Christa Conforti, Tom Gordon, Nina Larssen, and Meghan Steinharter Photograph Credits: Laura Sims, Janet Klein, Richard Cobb, Everett Hansen, Thomas Jung, Thomas Cech, and Amelie Rak Editors and Additional Contributors: Christa Conforti, Alison Forrestel, Alisa Shor, Lew Stringer, Sharon Farrell, Teri Thomas, John Doyle, and Kara Mirmelstein Acknowledgements: Thanks first to Matteo Garbelotto and the University of California, Berkeley Forest Pathology and Mycology Lab for providing a ‘forest pathology home’. Many thanks to the members of the Phytophthora huddle group for useful suggestions and feedback. Many thanks to the members of the Working Group for Phytophthoras in Native Habitats for insight into the issues of Phytophthora. Many thanks to Jennifer Parke, Ted Swiecki, Kathy Kosta, Cheryl Blomquist, Susan Frankel, and M. Garbelotto for guidance. I would like to acknowledge the BMP documents on Phytophthora that proceeded this one: the Nursery Industry Best Management Practices for Phytophthora ramorum to prevent the introduction or establishment in California nursery operations, and The Safe Procurement and Production Manual. 1 Title Page: Authors and Acknowledgements Table of Contents Page Title Page 1 Table of Contents 2 Executive Summary 5 Introduction to the Phytophthora Issue 7 Phytophthora Issues Around the World 7 Phytophthora Issues in California 11 Phytophthora -
Final Report for Project PG0102 Ramorum 060911
Measuring the economic, environmental and ecosystem services value of herita ge gardens, heathland and woodland in the context of determining potential impacts from the regulated plant pathogens Phytophthora ramorum and Phytopthora kernoviae Prepared for: Defra Prepared by: ADAS UK Ltd in conjunction with CJC Consulting, Fera, and the London School of Economics Date: 17th June 2011 0936648 Project FFG0921: TEV at risk from P. ramorum and P. kernoviae Acknowledgements The project team would like to thank the time, effort and support provided by the Defra economists, Phil Cryle, Adam Bell, Meredith Ward and internal reviewers as well as the team at Fera including Alan Inman, Keith Walters, Claire Sansford, and Judith Turner. For assistance and provision of information to: Bruce Rothnie, Jennifer Mcvey, Pat Snowdon, Olly Stephenson, Justin Gilbert, Shona Cameron and Mark Broadmeadow (Forestry Commission), Suzanne Perry and Keith Kirby (Natural England) and Ian Wright (National Trust). Project team: Glyn Jones, Ben Drake (ADAS) – lead authors and contact Nigel Boatman, John Hughes, Kate Somerwill (Fera) Bob Crabtree (CJC Consulting) Susana Mourato (London School of Economics) Project FFG0921: TEV at risk from P. ramorum and P. kernoviae Executive summary Introduction The main aim of this research is to provide estimates of the total value to society of heritage gardens, heathland and woodland which may be under threat from impacts from Phytophthora ramorum (P. ramorum) and Phytophthora kernoviae (P. kernoviae) . The estimates provide an update to the figures used in the 2008 Impact Assessment. Background P. ramorum and P. kernoviae are exotic plant pathogens that have only recently been described in the last decade. -
Phytophthora Magnolia Phosphonate Poster ICPP Aug 08
Steps towards integrated management of Forest Research Phytophthora kernoviae and P. ramorum on magnolias in British heritage gardens Sandra Denman, Susan Kirk and Alistair Whybrow Forest Research, Alice Holt Lodge, Farnham, Surrey GU10 4LH, UK. Introduction Phytophthora kernoviae (Pk) and P. ramorum (Pr) are newly invasive Phytophthora species in Britain causing disfigurement and death of ornamental plants and trees in nurseries, native woodlands and gardens (Figures 1 and 2). Many of the gardens have heritage value and house collections of rare and exotic plants (e.g. the ‘National Magnolia Collection’). These serve as an important genetic resource but the gardens are also a significant source of tourist revenue. Some of the plant species that form the essential character of the gardens are primary foliar hosts for Pr and Pk and produce Figure 1. Shoot tip dieback and Figure 2. Bleeding stem lesions abundant inoculum when infected (e.g. rhododendrons, magnolia and pieris). Infected foliage leaf necrosis of R ponticum. on Fagus sylvatica. of these showcase plants is not only disfiguring but may be subjected to plant health measures of Route to determining whether infected deciduous magnolias can be freed from disease removal and destruction. By preventing new leaf infections and controlling existing ones, inoculum (1) Is the disease cycle broken over winter Yes No production and spread to trees and other plants is reduced. (2a) Has the main external source of (2b) Is the pathogen systemic inoculum been removed (e.g. rhododendron) (i.e. in the vascular system) No Do not progress Yes No until the answer is Yes To find out if some of these valuable plants could be ‘cured’ of established infections, aff ected Yes The plant will (3bi) Determine where the most probably pathogen overwinters/stays have to be latent in winter magnolias at two National Trust gardens were selected for study. -
Syngenta's Citrus Soil Assay for Phytophthora
Photo Taken by: Kendra McCorkle Syngenta’s Citrus Soil Assay for Phytophthora Kendra McCorkle Last Updated: 10/02/16 Contents ● My Background ● Topic selection ● Module Contents ● Value of the learning module ● Acknowledgements ● Questions Photo Taken by: Kevin Langdon, Syngenta Background Information-Personal ● Florida Native - Reside on FL’s East coast ● Family in the citrus industry Photo Taken by: Kendra McCorkle Photo Taken by: Kathy Thomason http://indian-river.fl.us/citrus/district_map.gif Background Information-Personal Background Information- Professional ● Indian River State College (2008-2010) - A.A. Environmental Science ● Syngenta Internships - Summers of 2009, 2010, 2011, 2012 ● University of Florida (2010-2012) - B.S. Environmental Management - Minor Soil and Water Science ● Syngenta Crop Protection - R&D Specialist (2012) ● Iowa State University (2014-2016) - M.S. Agronomy Topic selection ● Syngenta invested in my degree ● Current role entails fungicide efficacy trials - Another research project? ● Passionate about citrus ● Topic: Syngenta’s Citrus Soil Assay program - Important piece of my history Why a learning module? ● Create a training document for Syngenta - Basic introduction to the program - Used for internal and external customers Photos Taken by: Kendra McCorkle Module Contents ● Florida citrus ● Major diseases in Florida citrus ● Citrus Phytophthora ● Citrus greening ● Phytophthora and citrus greening interaction ● Syngenta’s citrus soil assay Photo Taken by: Kendra McCorkle Florida Citrus ● 500,000 total acres of citrus in FL - 453,000 acres of oranges (~90% of total) - 46,000 acres of grapefruit (~10% of total) ● Generates $9 billion for FL economy (Florida Citrus Mutual, 2012) Photo Taken by: Kendra McCorkle ● Florida provides 80% of the orange juice produced in the U.S. -
Soil- and Waterborne Phytophthora Species Linked to Recent
REVIEW ARTICLE Soil- and waterborne Phytophthora species linked to recent outbreaks in Northern California restoration sites A review identifies several Phytophthora species found in California wildlands and discusses approaches for preventing and diagnosing the spread of these plant pathogens. by Matteo Garbelotto, Susan J. Frankel and Bruno Scanu istorically, the release of Phytophthora species Abstract in the wild has resulted in massive die-offs of Himportant native plant species, with cascading Many studies around the globe have identified plant production facilities consequences on the health and productivity of affected as major sources of plant pathogens that may be released in the wild, ecosystems (Brasier et al. 2004; Hansen 2000; Jung with significant consequences for the health and integrity of natural 2009; Lowe 2000; Rizzo and Garbelotto 2003; Swiecki ecosystems. Recently, a large number of soilborne and waterborne et al. 2003; Weste and Marks 1987). Once introduced, species belonging to the plant pathogenic genus Phytophthora have plant pathogens in general cannot be eradicated (Cun- been identified for the first time in California native plant production niffe et al. 2016; Garbelotto 2008), and costs associated facilities, including those focused on the production of plant stock used with the spread and control of exotic pathogens and in ecological restoration efforts. Additionally, the same Phytophthora pests have been estimated to surpass $100 billion per species present in production facilities have often been identified in failing year for the United States alone (Pimentel et al. 2005). restoration projects, further endangering plant species already threatened Thus, preventing the introduction of pathogens by us- or endangered. To our knowledge, the identification of Phytophthora ing pathogen-free plant stock is the most cost-effective species in restoration areas and in plant production facilities that produce and responsible approach (Parnell et al.