Of Phytophthora Cinnamomi (Rands) in Soil

Total Page:16

File Type:pdf, Size:1020Kb

Of Phytophthora Cinnamomi (Rands) in Soil SURVIVAL OF DIFFERENT LIFE STAGES OF PHYTOPHTHORA CINNAMOMI (RANDS) IN SOIL AND PLANT ROOTS UNDER MINE SITE CONDITIONS By JAMBA GYELTSHEN B.Sc. Agri. (Kerela Agrl. Uni., India); M.Sc. Crop Protection (Uni. of Reading, U.K.); Doctor of Plant Medicine (Uni. of Florida, U.S.A.) A thesis presented to Murdoch University for the degree of Doctor of Philosophy May 2, 2018 DECLARATION I declare that this thesis is my own account of research, and contains as its main content, work which has not previously been submitted for a degree at any tertiary education institution. Jamba Gyeltshen ii ACKNOWLEDGEMENTS I would like to express my deepest gratitude to my supervisors, Professor Giles Hardy, Dr. Treena Burgess, and Dr. Bill Dunstan for their profound inspiration, guidance, and support during the course of this study. Without that kind of support, it would not have been possible to complete this work on time. Their accessibility at all times and the wholehearted willingness to help was a humbling experience. Thanks are also due to Dr. Navid Moheimani (Supervisory Committee Chair) for his time and advice. I am particularly grateful for the whole-hearted support received from Diane White and Briony Williams in the laboratory, Dr. Mike Calver and Chris Shaw for statistical analysis, and all my graduate fellow-mates for various other support and cooperation. My special thanks to my wife, Kunzang Chhoden; daughters, Thinley Yangzom and Jamba Chhoden; and son, Tashi Tenzin, for their moral support, encouragement, and sacrifices. I also wish to thank Kuenga Nidup for the help rendered with photoshop to put together the pictures and graphs. Finally, I am greatly indebted to Murdoch University for the scholarship within the framework of the ARC-Linkage Project that enabled me to carry out this study. iii ABSTRACT Phytophthora cinnamomi (Rands) is a soil and water-borne plant pathogen, associated with a devastating dieback disease in the jarrah (Eucalyptus marginata) forest, in Western Australia. As the forest is an active site for extensive open-cut bauxite mining, it is a challenge to prevent the potential spread of P. cinnamomi. Despite years of research, we have not fully understood how P. cinnamomi survives the long, hot and dry Mediterranean summer in the jarrah forest ecosystem, particularly under mine site conditions where surface temperatures periodically reach 60 ºC. This study looked at the life span of oospores, chlamydospores and encysted zoospores under conditions typical of the mine sites. In particular, it compared the effect of dry and moist soil conditions on survival of oospores and chlamydospores. The study also examined the effects of exogenous materials (smoke water, fish emulsion, and the fungicides, ridomil and furalaxyl) that are known to have stimulatory or inhibitory effects on growth. These were shown not to have any significant impact on the survival structures. The findings indicate that oospores of P. cinnamomi survive in the soil for less than one year irrespective of soil moisture conditions, while chlamydospores survive for less than 12 weeks under similar conditions. Encysted zoospores under submerged conditions (similar to those in drainage sumps along haul roads) did not survive beyond one week. The effect of varying moisture levels was examined with oospores of a closely related species (P. multivora) which is associated with the dieback disease complex. At matric potentials between -1 kPa and -6 MPa, there was a clear decline in oospore viability, and at -6 MPa, which is the level of dryness typically experienced during the hot dry summers, oospore iv viability was reduced to 66% after 60 days. The possible role of non-susceptible or tolerant host plants growing on topsoil stockpiles on pathogen survival was investigated to determine how plants contribute to the long-term survival of the pathogen. Meta-barcoding and high throughput sequencing detected P. cinnamomi on 16 of the 20 plant species assessed. Unexpectedly, the technique revealed the putative presence of 24 other Phytophthora species, thereby raising more questions on the role of these plants in the Phytophthora disease cycle. Based on the findings, this study recommends that the stockpiles be maintained in situ and plant-free for at least 2-3 years to minimize the risk of spreading the pathogen and permanently removing the source of inoculum. v CONFERENCE PRESENTATION A presentation of the work (Chapter 2) was made at the 8th Congress of IUFRO Group 7.02.09: “Phytophthora in Forests and Natural Ecosystems” held in Sapa, Vietnam from 18th to 25th of March 2016. Title: The decline in viability of Phytophthora cinnamomi survival structures under moist and dry soil conditions. 1 1 1 1 Jamba Gyeltshen , William Dunstan , Treena Burgess , Giles Hardy 1Centre for Phytophthora Science and Management, School of Veterinary and Life Sciences, Murdoch University, W. Australia, 6150; [email protected] vi TABLE OF CONTENTS DECLARATION .............................................................................................................................. ii ACKNOWLEDGEMENTS ............................................................................................................ iii ABSTRACT ................................................................................................................................... iv CONFERENCE PRESENTATION ............................................................................................... vi CHAPTER 1: GENERAL INTRODUCTION AND LITERATURE REVIEW ..................................................... 1 1.1 GENERAL INTRODUCTION ................................................................................................. 1 1.1.1 Structure of the thesis .......................................................................................... 3 1.2 BIOLOGY AND LIFE CYCLE OF PHYTOPHTHORA CINNAMOMI ............................. 4 1.2.1 The phylogeny of Phytophthora cinnamomi ......................................................... 4 1.2.2 Morphology of Phytophthora cinnamomi .............................................................. 5 1.2.3 Reproduction and life cycle .................................................................................. 5 1.2.4 Dispersal ............................................................................................................. 8 1.2.5 Nutrition and the infection process ....................................................................... 8 1.2.6 Dormancy, viability, viability testing.................................................................... 10 1.2.7 Vital stain ........................................................................................................... 12 1.2.8 Survival of Phytophthora cinnamomi.................................................................. 14 vii 1.3 ECOLOGICAL FACTORS AFFECTING PHYTOPHTHORA CINNAMOMI .................... 22 1.3.1 Soil moisture (matric potential) .......................................................................... 23 1.3.2 Soil temperature ................................................................................................ 25 1.3.3 Microbial antagonism to Phytophthora ............................................................... 26 1.4 PHYTOPHTHORA DIEBACK AND BAUXITE MINING ........................................... 28 1.4.1 Jarrah forest environment & Phytophthora dieback............................................ 28 1.4.2 Host range of Phytophthora cinnamomi ............................................................. 29 1.4.3 Bauxite mining and rehabilitation ....................................................................... 30 1.4.4 Dieback management ........................................................................................ 31 1.5 THESIS AIMS AND RESEARCH OBJECTIVES ..................................................... 32 CHAPTER 2: HOW TIME, MOISTURE AND EXOGENOUS FACTORS AFFECT THE VIABILITY OF PHYTOPHTHORA CINNAMOMI PROPAGULES IN SOIL ............................................... 34 2.1 INTRODUCTION ..................................................................................................... 34 2.2 MATERIALS AND METHODS ........................................................................................ 37 2.2.1 Experiment 1: The effect of time, moisture level and exogenous factors on viability of oospores ........................................................................................... 39 2.2.2 Experiment 2: Determining the effect of time, moisture level and exogenous factors on viability of chlamydospores ................................................................ 44 2.2.3 Viability determination using Tetrazolium bromide stain (MTT) .......................... 45 2.2.4 Viability determination through RNA assay ........................................................ 48 2.2.5 Analysis of data ................................................................................................. 49 viii 2.3 RESULTS.......................................................................................................................... 50 2.3.1 Experiment 1: Determining the effect of time, moisture level and exogenous factors on viability of oospores ........................................................................... 50 2.3.2 Experiment 2: The effect of time, moisture level and exogenous factors on chlamydospore viability .....................................................................................
Recommended publications
  • Development of Fish Scraps Shredding and Mixing Machine For
    Asia Pacific Journal of Multidisciplinary Research, Vol. 3, No. 4, November 2015 Part II _______________________________________________________________________________________________________________ Asia Pacific Journal of Development of Fish Scraps Shredding and Multidisciplinary Research Mixing Machine for Fish Emulsion Fertilizer Vol. 3 No. 4,111-115 November 2015 Part II Production P-ISSN 2350-7756 E-ISSN 2350-8442 Michael A. Aloria1, John Carlo B. Mallari2, John Mark A. Del Rio3, www.apjmr.com McKartnier I. Laylo4 College of Engineering of Engineering, Architecture and Fine Arts, Batangas State University, Philippines [email protected], 2 [email protected], [email protected], [email protected] Date Received: September 2, 2015; Date Revised: October 5, 2015 Abstract – The use of organic fertilizers supports the sustainable agriculture of the Philippines through maintaining soil fertility and regaining the high yield and sustainability of the land. The development of fish scraps shredding and mixing machine can be of great help to the production of fish emulsion fertilizer in both quality and quantity. The study specifically covered the design, development and performance evaluation of the fish scraps shredding and mixing machine that was employed for fish emulsion fertilizer production. Preliminary tests were performed to establish operating conditions of the machine such as working capacity, shredding speed, mixing speed, mixing time and mixing capacity. The working capacity was found to be 750g of fish scraps. The shredding speed established was based on the variable frequency drive (VFD) at 50Hz which corresponds to 1800rpm. The actual performance of the machine was evaluated by determining the shredding rate and efficiency. Based from the results gathered from the performance evaluation of the machine, the shredding efficiency rate and efficiency was 164.19 g/s and 91.64%, respectively.
    [Show full text]
  • 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
    [Show full text]
  • Intro Outline
    THE REPRODUCTIVE ECOLOGY OF TWO TERRESTRIAL ORCHIDS, CALADENIA RIGIDA AND CALADENIA TENTACULATA RENATE FAAST Submitted for the degree of Doctor of Philosophy School of Earth and Environmental Sciences The University of Adelaide, South Australia December, 2009 i . DEcLARATION This work contains no material which has been accepted for the award of any other degree or diploma in any university or other tertiary institution to Renate Faast and, to the best of my knowledge and belief, contains no material previously published or written by another person, except where due reference has been made in the text. I give consent to this copy of my thesis when deposited in the University Library, being made available for loan and photocopying, subject to the provisions of the Copyright Act 1968. The author acknowledges that copyright of published works contained within this thesis (as listed below) resides with the copyright holder(s) of those works. I also give permission for the digital version of my thesis to be made available on the web, via the University's digital research repository, the Library catalogue, the Australasian Digital Theses Program (ADTP) and also through web search engines. Published works contained within this thesis: Faast R, Farrington L, Facelli JM, Austin AD (2009) Bees and white spiders: unravelling the pollination' syndrome of C aladenia ri gída (Orchidaceae). Australian Joumal of Botany 57:315-325. Faast R, Facelli JM (2009) Grazrngorchids: impact of florivory on two species of Calademz (Orchidaceae). Australian Journal of Botany 57:361-372. Farrington L, Macgillivray P, Faast R, Austin AD (2009) Evaluating molecular tools for Calad,enia (Orchidaceae) species identification.
    [Show full text]
  • Fishery Basics – Seafood Markets Where Are Fish Sold?
    Fishery Basics – Seafood Markets Where Are Fish Sold? Fisheries not only provide a vital source of food to the global population, but also contribute between $225-240 billion annually to the worldwide economy. Much of this economic stimulus comes from the sale and trade of fishery products. The sale of fishery products has evolved from being restricted to seaside towns into a worldwide market where buyers can choose from fish caught all over the globe. Like many other commodities, fisheries markets are fluctuating constantly. In recent decades, seafood imports into the United States have increased due to growing demands for cheap seafood products. This has increased the amount of fish supplied by foreign countries, expanded efforts in aquaculture, and increased the pursuit of previously untapped resources. In 2008, the National Marine Fisheries Service (NMFS) reported (pdf) that the U.S. imported close to 2.4 million t (5.3 billion lbs) of edible fishery products valued at $14.2 billion dollars. Finfish in all forms (fresh, frozen, and processed) accounted for 48% of the imports and shellfish accounted for an additional 36% of the imports. Overall, shrimp were the highest single-species import, accounting for 24% of the total fishery products imported into the United States. Tuna and Salmon were the highest imported finfish accounting for 18% and 10% of the total imports respectively. The majority of fishery products imported came from China, Thailand, Canada, Indonesia, Vietnam, Ecuador, and Chile. The U.S. exported close to 1.2 million t (2.6 billion lbs) valued at $3.99 billion in 2008.
    [Show full text]
  • Plant Life of Western Australia
    INTRODUCTION The characteristic features of the vegetation of Australia I. General Physiography At present the animals and plants of Australia are isolated from the rest of the world, except by way of the Torres Straits to New Guinea and southeast Asia. Even here adverse climatic conditions restrict or make it impossible for migration. Over a long period this isolation has meant that even what was common to the floras of the southern Asiatic Archipelago and Australia has become restricted to small areas. This resulted in an ever increasing divergence. As a consequence, Australia is a true island continent, with its own peculiar flora and fauna. As in southern Africa, Australia is largely an extensive plateau, although at a lower elevation. As in Africa too, the plateau increases gradually in height towards the east, culminating in a high ridge from which the land then drops steeply to a narrow coastal plain crossed by short rivers. On the west coast the plateau is only 00-00 m in height but there is usually an abrupt descent to the narrow coastal region. The plateau drops towards the center, and the major rivers flow into this depression. Fed from the high eastern margin of the plateau, these rivers run through low rainfall areas to the sea. While the tropical northern region is characterized by a wet summer and dry win- ter, the actual amount of rain is determined by additional factors. On the mountainous east coast the rainfall is high, while it diminishes with surprising rapidity towards the interior. Thus in New South Wales, the yearly rainfall at the edge of the plateau and the adjacent coast often reaches over 100 cm.
    [Show full text]
  • Management Plan Kaiserstuhl Conservation Park 2006
    Department for Environment and Heritage Management Plan Kaiserstuhl Conservation Park 2006 www.environment.sa.gov.au This plan of management was adopted on 11 January 2006 and was prepared in pursuance of section 38 of the National Parks and Wildlife Act 1972. Government of South Australia Published by the Department for Environment and Heritage, Adelaide, Australia © Department for Environment and Heritage, 2006 ISBN: 1 921018 887 Front cover photograph courtesy of Bernd Stoecker FRPS and reproduced with his permission This document may be cited as “Department for Environment and Heritage (2006) Kaiserstuhl Conservation Park Management Plan, Adelaide, South Australia” FOREWORD Kaiserstuhl Conservation Park is located approximately 80 kilometres north-east of Adelaide and approximately 12 kilometres south-east of Tanunda, in the northern Mount Lofty Ranges. The 392 hectare park was proclaimed in 1979 to conserve a remnant block of native vegetation, in particular the northern-most population of Brown Stringybark (Eucalyptus baxteri). Kaiserstuhl Conservation Park preserves a substantial number of habitats for native fauna and helps to protect the soil and watershed of Tanunda Creek. More than 360 species of native plant are found within the reserve, many of which are of conservation significance. Bird species of conservation significance recorded within the reserve include the Diamond Firetail, White-browed Treecreeper, Elegant Parrot and Crescent Honeyeater. Kaiserstuhl Conservation Park also has a rich cultural heritage. The reserve is of significance to the Peramangk people and Ngadjuri people who have traditional associations with the land. Kaiserstuhl Conservation Park has also been a valuable source of material for botanical research. Dr Ferdinand von Mueller and Dr Hans Herman Behr collected Barossa Ranges plants from the area between 1844 and 1851.
    [Show full text]
  • Flora of South Australia 5Th Edition | Edited by Jürgen Kellermann
    Flora of South Australia 5th Edition | Edited by Jürgen Kellermann KEY TO FAMILIES1 J.P. Jessop2 The sequence of families used in this Flora follows closely the one adopted by the Australian Plant Census (www.anbg.gov. au/chah/apc), which in turn is based on that of the Angiosperm Phylogeny Group (APG III 2009) and Mabberley’s Plant Book (Mabberley 2008). It differs from previous editions of the Flora, which were mainly based on the classification system of Engler & Gilg (1919). A list of all families recognised in this Flora is printed in the inside cover pages with families already published highlighted in bold. The up-take of this new system by the State Herbarium of South Australia is still in progress and the S.A. Census database (www.flora.sa.gov.au/census.shtml) still uses the old classification of families. The Australian Plant Census web-site presents comparison tables of the old and new systems on family and genus level. A good overview of all families can be found in Heywood et al. (2007) and Stevens (2001–), although these authors accept a slightly different family classification. A number of names with which people using this key may be familiar but are not employed in the system used in this work have been included for convenience and are enclosed on quotation marks. 1. Plants reproducing by spores and not producing flowers (“Ferns and lycopods”) 2. Aerial shoots either dichotomously branched, with scale leaves and 3-lobed sporophores or plants with fronds consisting of a simple or divided sterile blade and a simple or branched spikelike sporophore ..................................................................................
    [Show full text]
  • Plant, Microbiology and Genetic Science and Technology Duccio
    View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Florence Research DOCTORAL THESIS IN Plant, Microbiology and Genetic Science and Technology section of " Plant Protection" (Plant Pathology), Department of Agri-food Production and Environmental Sciences, University of Florence Phytophthora in natural and anthropic environments: new molecular diagnostic tools for early detection and ecological studies Duccio Migliorini Years 2012/2015 DOTTORATO DI RICERCA IN Scienze e Tecnologie Vegetali Microbiologiche e genetiche CICLO XXVIII COORDINATORE Prof. Paolo Capretti Phytophthora in natural and anthropic environments: new molecular diagnostic tools for early detection and ecological studies Settore Scientifico Disciplinare AGR/12 Dottorando Tutore Dott. Duccio Migliorini Dott. Alberto Santini Coordinatore Prof. Paolo Capretti Anni 2012/2015 1 Declaration I hereby declare that this submission is my own work and that, to the best of my knowledge and belief, it contains no material previously published or written by another person nor material which to a substantial extent has been accepted for the award of any other degree or diploma of the university or other institute of higher learning, except where due acknowledgment has been made in the text. Duccio Migliorini 29/11/2015 A copy of the thesis will be available at http://www.dispaa.unifi.it/ Dichiarazione Con la presente affermo che questa tesi è frutto del mio lavoro e che, per quanto io ne sia a conoscenza, non contiene materiale precedentemente pubblicato o scritto da un'altra persona né materiale che è stato utilizzato per l’ottenimento di qualunque altro titolo o diploma dell'Università o altro istituto di apprendimento, a eccezione del caso in cui ciò venga riconosciuto nel testo.
    [Show full text]
  • Background: Threat Abatement Plan for Disease in Natural Ecosystems Caused by Phytophthora Cinnamomi
    Background: Threat abatement plan for disease in natural ecosystems caused by Phytophthora cinnamomi January 2014 Background: Threat abatement plan for disease in natural ecosystems caused by Phytophthora cinnamomi © Copyright Commonwealth of Australia, 2014 ISBN: 978-1-921733-94-9 Background: Threat abatement plan for disease in natural ecosystems caused by Phytophthora cinnamomi is licensed by the Commonwealth of Australia for use under a Creative Commons By Attribution 3.0 Australia licence with the exception of the Coat of Arms of the Commonwealth of Australia, the logo of the agency responsible for publishing the report, content supplied by third parties, and any images depicting people. For licence conditions see: http://creativecommons.org/licenses/by/3.0/au/. This report should be attributed as ‘Background: Threat abatement plan for disease in natural ecosystems caused by Phytophthora cinnamomi, Commonwealth of Australia, 2014’. The views and opinions expressed in this publication are those of the authors and do not necessarily reflect those of the Australian Government or the Minister for the Environment. The contents of this document have been compiled using a range of source materials and are valid as at August 2013. While reasonable efforts have been made to ensure that the contents of this publication are factually correct, the Commonwealth does not accept responsibility for the accuracy or completeness of the contents, and shall not be liable for any loss or damage that may be occasioned directly or indirectly through the use of, or reliance on, the contents of this publication. Photo credits Front cover: Mondurup Peak, Stirling Range, 2010 (Department of Parks and Wildlife, Western Australia) Back cover: Wildflowers on Mondurup Peak, Stirling Range, 1993 (Rob Olver) ii / Background: Threat abatement plan for disease in natural ecosystems caused by Phytophthora cinnamomi Contents 1.
    [Show full text]
  • Appl. Environ. Microbiol. 60:2616–2621
    APPLIED AND ENVIRONMENTAL MICROBIOLOGY, Mar. 1998, p. 948–954 Vol. 64, No. 3 0099-2240/98/$04.0010 Copyright © 1998, American Society for Microbiology PCR Amplification of Ribosomal DNA for Species Identification in the Plant Pathogen Genus Phytophthora JEAN B. RISTAINO,* MICHAEL MADRITCH, CAROL L. TROUT, AND GREGORY PARRA Department of Plant Pathology, North Carolina State University, Raleigh, North Carolina 27695 Received 7 August 1997/Accepted 15 December 1997 We have developed a PCR procedure to amplify DNA for quick identification of the economically important species from each of the six taxonomic groups in the plant pathogen genus Phytophthora. This procedure involves amplification of the 5.8S ribosomal DNA gene and internal transcribed spacers (ITS) with the ITS primers ITS 5 and ITS 4. Restriction digests of the amplified DNA products were conducted with the restriction enzymes RsaI, MspI, and HaeIII. Restriction fragment patterns were similar after digestions with RsaI for the following species: P. capsici and P. citricola; P. infestans, P. cactorum, and P. mirabilis; P. fragariae, P. cinnamomi, and P. megasperma from peach; P. palmivora, P. citrophthora, P. erythroseptica, and P. cryptogea; and P. mega- sperma from raspberry and P. sojae. Restriction digests with MspI separated P. capsici from P. citricola and separated P. cactorum from P. infestans and P. mirabilis. Restriction digests with HaeIII separated P. citro- phthora from P. cryptogea, P. cinnamomi from P. fragariae and P. megasperma on peach, P. palmivora from P. citrophthora, and P. megasperma on raspberry from P. sojae. P. infestans and P. mirabilis digests were identical and P. cryptogea and P.
    [Show full text]
  • Wild-Caught Fish Listening Session 2:00 - 3:00 Pm Edt Chat Record
    USDA Agricultural Marketing Service (AMS) National Organic Program Thursday, March 18, 2021 Wild-Caught Fish Listening Session 2:00 - 3:00 pm edt Chat Record Participant Name Message Kirby Rootes-Murdy Hi Everyone, this Kirby Rootes-Murdy, with Atlantic States Marine Fisheries Commission Paul Zajicek Paul Zajicek, Executive Director, National Aquaculture Association jodi blanch Jodi Blanch- Gorton's Gloucester Craig Morris Craig Morris, Association of Genuine Alaska Pollock Producers Evelyn Drawec` Evelyn from Seychelles Organic Programme Amanda Johnson Amanda Johnson, Dramm Corporation Samantha Carroll Samantha Carroll - Louisiana Seafood Promotion and Marketing Board Jennifer Reed-Harry Jennifer Reed-Harry, Pennsylvania Aquaculture Advisory Commitee Colleen Coyne Colleen Coyne, Seafood Program Coordinator, Food Export USA-Northeast Christa Biggs Clara Gareis from Aptar Food Protection Joseph Logan Joe Logan, Trident Seafoods Jason Anderson Jason Anderson, O'Hara Corporation Jim Rodgers Good afternoon. Jim Rodgers with StarKist Tuna Steve Etka Steve Etka, with National Organic Coalition Andrew Nagle Andrew Nagle, John Nagle Co John Burrows John Burrows, Alaska Seafood Marketing Institute Margaret Malkoski Margaret Malkoski, National Fisheries Institute Nina Schlossman Nina Schlossman, Global Food & Nutrition & Alaska Seafood Marketing Istitute Richard McGowan Rick McGowan Biloxi Freezing & Processing Suzanne Dugas Suzanne Dugas, Twin Parish Port District (Port of Delcambre), coastal Louisiana Patty Lovera Patty Lovera, Organic Farmers
    [Show full text]
  • Aquatic Assemblages from Edna Metabarcoding 1 Casting a Broader
    1 Running Head: Aquatic assemblages from eDNA metabarcoding 2 Casting a broader net: Using microfluidic metagenomics to capture aquatic biodiversity data from 3 diverse taxonomic targets 4 Laura L. Hauck1†, Kevin A. Weitemier2†, Brooke E. Penaluna1, Tiffany Garcia2, and Richard Cronn1* 5 1U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station, 3200 SW Jefferson Way, 6 Corvallis, OR 97331, email: [email protected] 7 2Oregon State University, Department of Fisheries and Wildlife, 104 Nash Hall, Corvallis, OR 97331 8 Tel: 1 (541) 737-7291 Fax: 1 (541) 750-7329 *Author for correspondence 9 †L. Hauck and K. Weitemier should be considered joint first author. 10 11 Abstract 12 Environmental DNA (eDNA) assays for single- and multi-species detection show promise for providing 13 standardized assessment methods for diverse taxa, but techniques for evaluating multiple taxonomically- 14 divergent assemblages are in their infancy. We evaluated whether microfluidic multiplex metabarcoding and 15 high-throughput sequencing could identify diverse aquatic and riparian assemblages from 48 taxon-general and 16 taxon-specific metabarcode primers. eDNA screening was paired with electrofishing along a stream continuum 17 to evaluate congruence between methods. A fish hatchery located midway along the stream continuum 18 provided a dispersal barrier, and a point source for non-native White Sturgeon (Acipencer transmontanus). 19 Microfluidic metabarcoding detected all 13 species observed by electrofishing, with overall accuracy of 86%. 20 Taxon-specific barcoding primers were more successful than taxon-general universal metabarcoding primers at 21 classifying sequences to species. Both types of markers detected a transition from downstream sites dominated 22 by multiple fish species, to upstream sites dominated by a single species; however, we failed to detect a 23 transition in amphibian population structure.
    [Show full text]