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Public & Environmental Health Services STRONGER TOGETHER Public & Environmental Health Services Australia & New Zealand The Public and Environmental Health service line of Eurofins Agroscience Services undertakes laboratory and field research in the development of products and strategies to control, inhibit and repel urban pests. Field work is conducted in residential, commercial and natural environments. All laboratory trials are conducted on site at our Gosford facility (New South Wales) in four 20m3 stainless steel lined test chambers with adjustable ventilation. These chambers are suitable for testing aerosols, liquid emanating devices and total release devices for crawling and flying insects and also for cockroach and ant bait evaluations. Mosquito, fly, leech, tick, sandfly and march fly repellent testing can also be conducted in the chambers or in the field with human volunteers. Our insectary at Gosford maintains colonies of mosquitoes, houseflies, Australian sheep blowflies, American cockroaches, German cockroaches, silverfish, stored product pests, snails and slugs. Species that are not bred in the insectary are collected from the field and include ants, spiders, termites, bronze orange bugs and aphids. We have experience in conducting trials in more than 40 different species in both field and lab studies. The species list includes (but is not limited to): • Black House Ants (Ochetellus glaber) • Housefly (Musca domestica) • Coastal Brown Ants (Pheidole megacephala) • Sheep Blowfly (Lucilia cuprina) • Green Head Ants (Rhytidoponera metallica) • Vinegar Fly (Drosophila spp.) • Meat Ants (Iridomyrmex purpureus) • Sand Fly (Austrosimulium sp.) • White Footed Ants (Technomyrmex albipes) • March Fly (Tabanidae family) • Carpet Beetles (Anthrenus verbasci) • Garden Snails (Helix aspersa) • Common Hide Beetles (Dermestes maculatus) • Grey Garden Slug (Deroceras reticulatum) • Elephant Weevil (Orthorhinus cylindrirostris) • Leopard Slug (Limax maximus) • Flour Beetles (Tribolium sp.) • Brown House Mosquito • Litter Beetles (Alphitobius diaperinus) (Culex quinquefasciatus) • American Cockroach (Periplaneta americana) • Dengue Mosquito (Aedes aegypti) • German Cockroach (Blatella germanica) • Cotton Bollworm Moth (Helicoverpa sp) • Cat Flea (Ctenocephalides felis) • Indian Meal Moth (Plodia interpunctella) STRONGER TOGETHER • Bronze Orange Bug (Musgraveia sulciventris) • Black House Spiders (Badumna insignis) • Rodents (Rattus; Mus) • Cellar Spiders (Pholcus phalangioides) • Paper Nest Wasps (Polistes humilis) • Coptotermes termites • Silverfish (Lepisma saccharina) • Mastotermes termites • Portuguese Millipedes • Schedorhinotermes termites (Ommatoiulus moreleti) • Brown Dog Tick (Rhipicephalus sanguineus) • Crickets (Gryllidae family) • Paralysis Tick (Ixodes holocyclus) • Earwigs (Forficula auricularia) • Reptiles (snakes) Below are some examples of the types of trials that have been run by the Public and Environmental Health service line. List of treatment types tested to date: • Liquid Bait formulations • In vitro applications • Dust formulations • Liquid vapourizers • Direct sprays • Lotions • Surface sprays • Pellet formulations • Dispensers • Biological actives • Sheet treatments • Copper treatments • Total release aerosols • Gel formulations • Gel baits • Granular formulations • Ingestion treatments • Coils • Light treatments • Arm bands • Suspension concentrates • Roll-ons • Bait application • Liquid formulations • Aerosol formulations • Wax formulations • Space sprays • Barrier formulations • LED treatments • Chemical impregnation • CSED treatments Type of studies conducted: • Palatability • Bioassays • Efficacy • Barrier potential • Bio-equivalence • Chemical Rainfastness • Knockdown • Plant Phytotoxicity • Mortality • Bite inhibition • Residual control • Weathering potential • Attractiveness • Preference • Repellency • Long term barrier protection Regulatory Services provided: • Chemistry and Manufacture • Occupational Health and Safety • Toxicology • Environment • Metabolism and Kinetics • Efficacy and Safety • Residues • Label extensions Eurofins Agroscience Services If you would like to discuss how Eurofins Agroscience Services can assist you, please contact Richard Fenwick Senior Research Scientist t. +61 (0)2 4322 8510 / +61 (0)408 867 965 e. [email protected] Eurofins Agroscience Services Group [email protected] http://agroscience.eurofins.com.au/.
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  • Ben Hoffmann CV
    CURRICULUM VITAE - BEN HOFFMANN Personal details Name : Benjamin Daniel Hoffmann Date of Birth : 4th December 1975 Contact Details (work) (home) CSIRO Ecosystem Sciences PO Box 1682 PMB 44 Winnellie Humpty Doo NT 0822 NT 0835 Ph. +61 8 89448432 Ph. +61 8 8988 1315 Mobile +61 418 820 718 Email [email protected] Education Undergraduate Bachelor of Science (Bsc). 1993-1995, Northern Territory University, Darwin Bsc. (Honours). 1996 , Northern Territory University, Darwin Honours Project Title - Ecology of the introduced ant Pheidole megacephala in the Howard Springs region of Australia’s Northern Territory. Postgraduate PhD. 1997-2001 , Northern Territory University, Darwin Thesis Title - Responses of ant communities to land use impacts in Australia. Employment of Relevance 2004 – present CSIRO Darwin. Research of invasive ant biology, ecology, impacts and management. Coordinating exotic ant eradications. Member on scientific advisory panels providing advise to other ant management programs. Research into disturbance ecology particularly minesite rehabilitation, utilizing ants as biological indicators. 1998 – 2004 CSIRO Darwin, Numerous small consultancies, particularly minesite rehabilitation assessments and sorting ants for other researchers. Journal articles (51) Hoffmann BD , Courchamp F (in review) Biological invasions and natural colonisations: are they different? Trends in Ecology and Evolution Hoffmann BD , Broadhurst LM (in review) The economic cost of invasive species to Australia. BioScience Gibb H, Sanders NJ, Dunn RR, Photakis M, Abril S, Andersen AN, Angulo E, Armbrecht I, Arnan, X, Baccaro FB, Boulay R, Castracani C, Del Toro I, Delsinne T, Diaz M, Donoso DA, Enríquez ML, Fayle TM, Feener Jr DH, Fitzpatrick M, Gómez C, Grasso DA, Groc S, Heterick B, Hoffmann BD , Lach L, Lattke J, Leponce M, Lessard JP, Longino J, Lucky A, Majer J, Menke SB, Mezger D, Mori A, Nia OP, Perace-Duvet J, Pfeiffer M, Philpott S, de Souza JLP, Tista M, Vonshak M, Parr CL (in review) Climate regulates the effects of anthropogenic disturbance on ant assemblage structure.
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  • Hymenoptera: Formicidae
    16 The Weta 30: 16-18 (2005) Changes to the classification of ants (Hymenoptera: Formicidae) Darren F. Ward School of Biological Sciences, Tamaki Campus, Auckland University, Private Bag 92019, Auckland ([email protected]) Introduction This short note aims to update the reader on changes to the subfamily classification of ants (Hymenoptera: Formicidae). Although the New Zealand ant fauna is very small, these changes affect the classification and phylogeny of both endemic and exotic ant species in New Zealand. Bolton (2003) has recently proposed a new subfamily classification for ants. Two new subfamilies have been created, a revised status for one, and new status for four. Worldwide, there are now 21 extant subfamilies of ants. The endemic fauna of New Zealand is now classified into six subfamilies (Table 1), as a result of three subfamilies, Amblyoponinae, Heteroponerinae and Proceratiinae, being split from the traditional subfamily Ponerinae. Bolton’s (2003) classification also affects several exotic species in New Zealand. Three species have been transferred from Ponerinae: Amblyopone australis to Amblyoponinae, and Rhytidoponera chalybaea and R. metallica to Ectatomminae. Currently there are 28 exotic species in New Zealand (Table 1). Eighteen species have most likely come from Australia, where they are native. Eight are global tramp species, commonly transported by human activities, and two species are of African origin. Nineteen of the currently established exotic species are recorded for the first time in New Zealand as occurring outside their native range. This may result in difficulty in obtaining species-specific biological knowledge and assessing their likelihood of becoming successful invaders. In addition to the work by Bolton (2003), Phil Ward and colleagues at UC Davis have started to resolve the phylogenetic relationships among subfamilies and genera of all ants using molecular data (Ward et al, 2005).
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  • 36 Wood Destroying Insects
    CHAPTER 36 THE BEST CONTROL OR HOW TO PERMANENTLY AND SAFELY CONTROL ALL WOOD DESTROYING ORGANISMS http://www.pctonline.com/copesan/ (without killing yourself) The February 1999 issue of Pest Control magazine on page 18 quotes Dr. Austin Frishman as saying, “We know that termiticides alone will not solve most termite problems.” This chapter will show you how to safely solve them without using any volatile termiticide poisons. At the time a live tree is cut down, nearly half its weight consists of water! The most destructive factor to wood in structures is excessive moisture, not wood destroying insects. Correct all moisture and humidity problems and you will also control almost all wood destroying insect problems without using any poisons. Use ventilation, moisture barriers, fans, air conditioners and/or dehumidifiers first, last and always. 1347 FORWARD Far more volatile, “registered,” synthetic pesticide poison is used to control termites than any other structural pest you will ever encounter. No volatile synthetic residual insecticide or economic poison is completely safe no matter what the professional pest control industry claims. The U. S. Environmental Protection Agency (EPA), when it approves one of the economic poisons, basically is only concerned with the harmful effects that occur from a single exposure of only the active ingredient by any route of entry or its acute toxicity expressed as its LD50 or LC50 value which is the lethal dose or concentration (relative amount) of only the active ingredient required to kill 50 % of a test population, e.g., male rats. LD50 values are recorded in milligrams of active ingredient per kilogram of body weight of the test animal.
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  • Invasive Ants Reduce Nesting Success of an Endangered Hawaiian Yellow-Faced Bee, Hylaeus Anthracinus
    NeoBiota 64: 137–154 (2021) A peer-reviewed open-access journal doi: 10.3897/neobiota.64.58670 RESEARCH ARTICLE NeoBiota https://neobiota.pensoft.net Advancing research on alien species and biological invasions Invasive ants reduce nesting success of an endangered Hawaiian yellow-faced bee, Hylaeus anthracinus Sheldon Plentovich1, Jason R. Graham2, William P. Haines3, Cynthia B.A. King3 1 Pacific Islands Coastal Program, U.S. Fish and Wildlife Service, 300 Ala Moana Blvd, Rm 3-122, Honolulu, HI 96750, USA 2 Bishop Museum, 1525 Bernice Street, Honolulu, HI 96817, USA 3 Hawai‘i Department of Land and Natural Resources, Division of Forestry and Wildlife, 1151 Punchbowl St. Rm. 325, Honolulu, HI 96813, USA Corresponding author: Sheldon Plentovich ([email protected]) Academic editor: J. Sun | Received 23 September 2020 | Accepted 21 December 2020 | Published 28 January 2021 Citation: Plentovich S, Graham JR, Haines WP, King CBA (2021) Invasive ants reduce nesting success of an endangered Hawaiian yellow-faced bee, Hylaeus anthracinus. NeoBiota 64: 137–154. https://doi.org/10.3897/neobiota.64.58670 Abstract Hawaii has a single group of native bees belonging to the genus Hylaeus (Hymenoptera: Colletidae) and known collectively as Hawaiian yellow-faced bees. The majority of the 63 species have experienced sig- nificant declines in range and population. In 2016, seven species received federal protection under the Endangered Species Act of 1973. Competitors and predators, such as invasive bees, wasps and ants, are thought to be important drivers of range reductions and population declines, especially at lower elevations where more non-native species occur. We evaluated the effects of invasive ants on nesting Hylaeus anthra- cinus using artificial nest blocks that allowed us to track nest construction and development.
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  • Important Pest Ants of Australia
    IMPORTANT PEST ANTS OF AUSTRALIA Argentine Ant Black House Ant Bulldog Ant (Bull Ant) Carpenter Ant (Linepithema humile) (Ochetellus glaber) (Myrmecia spp.) (Camponotus spp.) Key Features Key Features Key Features Key Features › The Argentine ant is similar to some Iridomyrmex spp. in body › A small, intensely-black ant › One of the largest ants in Australia › Variable in colour – from black to dark brown to brownish orange shape and colour, but it has more teeth on the mandibles, a more › This ant has a prominent node (petiole) which is a distinguishing › Red/black in colour › Has a smooth, evenly rounded, thorax tear-drop shaped head (the widest point well above the eyes) the feature from the white-footed house ant › Very aggressive › Large in size eyes are placed relatively lower on the front of the head › This ant is slightly smaller and stockier than the white-footed › Very long straight mandibles › Distinct single node on pedicel (petiole) › It has 5-8 large teeth on the mandibles and 5 to 13 smaller denticles house ant › Large eyes › Mandibles have 5-8 teeth › Resembles the white-footed house ant but is light brown in colour Food preferences › Polymorphic (multiple worker size) › Lacks a strong smell when crushed Food preferences Sugary liquids (hence common habit of tending aphids and bugs Proteins (other insects primarily). Food preferences Food preferences on domestic plants). Size Sugary liquids (hence tendency to tend aphids and bugs Sugary liquids (hence common habit of tending aphids and bugs Size on plants). on domestic plants). 15 – 36 mm. Approximately 2.5 mm.
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  • Norfolk Island Quarantine Survey 2012-2014 – a Comprehensive Assessment of an Isolated Subtropical Island
    Norfolk Island Quarantine Survey 2012-2014 – a Comprehensive Assessment of an Isolated Subtropical Island G.V.MAYNARD1, B.J.LEPSCHI2 AND S.F.MALFROY1 1Department of Agriculture and Water Resources, GPO Box 858, Canberra ACT 2601, Australia; and 2Australian National Herbarium, Centre for Australian National Biodiversity Research, GPO Box 1700, Canberra, ACT 2601, Australia Published on 10 March 2018 at https://openjournals.library.sydney.edu.au/index.php/LIN/index Maynard, G.V., Lepschi, B.J. and Malfroy, S.F. (2018). Norfolk Island quarantine survey 2012-2014 – a comprehensive assessment of an isolated subtropical island. Proceedings of the Linnean Society of New South Wales 140, 7-243 A survey of Norfolk Island, Australia was carried out during 2012-2014 to develop a baseline of information on plant pests, and diseases and parasites of domestic animals for biosecurity purposes. The Norfolk Island Quarantine Survey covered introduced vascular plants, invertebrate pests of plants and animals; plant pathogens; pests and diseases of bees, and diseases and parasites of domestic animals. 1747 species were recorded across all organism groups during the course of the survey, of which 658 are newly recorded for Norfolk Island. Details of all organisms recorded during the survey are presented, along with a bibliography of plants and animals of Norfolk Island, with particular reference to introduced taxa. Manuscript received 25 July 2017, accepted for publication 30 January 2018. KEYWORDS: animal diseases, bees, invertebrates, Norfolk Island, plant biosecurity, plant pathogens, plant pests, quarantine survey. INTRODUCTION uninhabited islands - Nepean Island, 1 km to the south, and Philip Island 6 km to the south (Fig.
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  • Improving Invasive Ant Eradication As a Conservation Tool: a Review
    Biological Conservation 198 (2016) 37–49 Contents lists available at ScienceDirect Biological Conservation journal homepage: www.elsevier.com/locate/bioc Review Improving invasive ant eradication as a conservation tool: A review Benjamin D. Hoffmann a,⁎,GloriaM.Luqueb,c, Céline Bellard d,NickD.Holmese,C.JoshDonlanc,f,⁎⁎ a CSIRO Land & Water Flagship, Tropical Ecosystems Research Centre, PMB 44, Winnellie, NT, Australia b Ecologie, Systématique & Evolution, UMR CNRS, Univ. Paris-Sud, F-91405 Orsay Cedex, France c Advanced Conservation Strategies, Cordoba, Spain d Department of Genetics, Evolution and Environment, Center for Biodiversity and Environment Research, University College of London, UK e Island Conservation, Santa Cruz, CA, USA f Department of Ecology and Evolutionary Biology, Cornell University, Ithaca, NY, USA article info abstract Article history: While invasive species eradications are at the forefront of biodiversity conservation, ant eradication failures are Received 11 July 2015 common. We reviewed ant eradications worldwide to assess the practice and identify knowledge gaps and Received in revised form 19 March 2016 challenges. We documented 316 eradication campaigns targeting 11 species, with most occurring in Australia Accepted 30 March 2016 covering small areas (b10 ha). Yellow crazy ant was targeted most frequently, while the bigheaded ant has Available online xxxx been eradicated most often. Of the eradications with known outcomes, 144 campaigns were successful, totaling approximately 9500 ha, of which 8300 ha were from a single campaign that has since been partially re-invaded. Keywords: fi Invasive alien species Three active ingredients, often in combination, are most commonly used: pronil, hydramethylnon, and juvenile Pests hormone mimics. Active ingredient, bait, and method varied considerably with respect to species targeted, which Eradication made assessing factors of eradication success challenging.
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  • The Riddle of the Sphinx: Population Ecology of the Endangered Blackburnʻs Sphinx Moth, Manduca Blackburni (Lepidoptera: Sphingidae) on an Invasive Host Plant
    The Riddle of the Sphinx: Population Ecology of the Endangered Blackburnʻs Sphinx Moth, Manduca blackburni (Lepidoptera: Sphingidae) on an Invasive Host Plant. A THESIS SUBMITTED TO THE GRADUATE DIVISION OF THE UNIVERSITY OF HAWAIʻI AT MĀNOA IN PARTIAL FULFILLMENT OF THE REQUIREMENTS FOR THE DEGREE OF MASTER OF SCIENCE IN ENTOMOLOGY (ECOLOGY, EVOLUTION, AND CONSERVATION BIOLOGY) DECEMBER 2019 By: Christine H. Elliott Thesis Committee: Dr. Daniel Rubinoff, Committee Chair Dr. William Haines Dr. Mark Wright Keywords: Blackburn’s sphinx moth, Manduca blackburni, relative abundance, ecological life table, oviposition DEDICATION This thesis is dedicated to my family: my two beautiful boys, Jacob and Phineas; my loving and supportive husband, Tim; and my Spartan mother, Barbara. Without your encouragement and support this could never have happened. I love you, I love you, I just love you! ACKNOWLEDGEMENTS This thesis was completed with tremendous support and assistance from my committee. Three years ago, Dr. Daniel Rubinoff was willing to take a risk and hire me. I will never be able to accurately convey my gratitude for this opportunity. Additionally, his clarity of thought and purpose was a trenchant force in keeping this work focused and on track. I also have tremendous appreciation for the vast knowledge and gentle expertise of Dr. William Haines. His generosity in time, editing, and advice was critical to my research and this thesis. Last but not least, Dr. Mark Wright was an invaluable sounding board and resource throughout my time, for which I am deeply grateful. His statistical guidance prevented my work from going off the rails and his eloquence under pressure has enriched my idiolect.
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  • Final Environmental Assessment Lehua Island Ecosystem Restoration Project July 2017
    Final Environmental Assessment Lehua Island Ecosystem Restoration Project July 2017 Co-Lead Agency: U.S. Fish and Wildlife Service Hawaiʻi Department of Land and Natural Resources, Division of Forestry and Wildlife Cooperating Federal Agencies: U.S. Department of Homeland Security, U.S. Coast Guard U.S. Department of Agriculture, Animal and Plant Health Inspection Service, Wildlife Services, National Wildlife Research Center i Executive Summary Lehua Island is a 115 hectare island located 1.2 km off the northern shore of Niʻihau (a privately owned, 18,650 hectare island). Lehua is a state-designated seabird sanctuary managed by the Hawaiʻi Department of Land and Natural Resources (DLNR) and federally owned by the U.S. Coast Guard (USCG). Lehua is one of Hawaiʻi’s most important seabird colonies because of its size and height above sea level. It also offers an opportunity for restoring an island ecosystem in the main Hawaiian Islands. DLNR-Division of Forestry and Wildlife (DOFAW), in conjunction with federal sponsors U.S. Fish and Wildlife Service (USFWS), technical partner Island Conservation (IC), and the cooperating members of the Lehua Island Restoration Steering Committee (LIRSC) are proposing to complete the eradication of rats from Lehua Island so further restoration efforts can move forward in the future. The LIRSC is a multidisciplinary stakeholder body including representatives from DOFAW, USFWS, the U.S. Department of Agriculture, Animal and Plant Health Inspection Service, Wildlife Services (USDA), U.S. Coast Guard (USCG), National Tropical Botanical Garden (NTBG), the owners of Niʻihau, and IC. In 2005, DOFAW and the USFWS embarked on a plan to restore Lehua Island.
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  • Common Names for Australian Ants (Hymenoptera: Formicidae)
    Australian Journal of Entomology (2002) 41, 285–293 Common names for Australian ants (Hymenoptera: Formicidae) Alan N Andersen CSIRO Sustainable Ecosystems, Tropical Ecosystems Research Centre, PMB 44, Winnellie, NT 0822, Australia. Abstract Most insects do not have common names, and this is a significant barrier to public interest in them, and to their study by non-specialists. This holds for even highly familiar insect groups such as ants. Here, I propose common names for all major native Australian ant genera and species-groups, as well as for many of the most abundant and distinctive species. Sixty-two genera, 142 species-groups and 50 species are given names. The naming system closely follows taxonomic structure; typically a genus is given a general common name, under which species-group and species names are nested. Key words ant species, communicating entomology, species-groups, taxonomic nomenclature. INTRODUCTION ‘little black ones’ (the remaining several thousand Australian species). Here, I attempt to redress this situation by propos- Common names are powerful aids for the popular communi- ing common names for all major native Australian ant genera cation of information about plant and animal species. Such and species-groups, as well as for many abundant and names use familiar and easily remembered words, in contrast distinctive species. to the taxonomic nomenclature that is so daunting for most people without formal scientific training. All higher-profile vertebrates and vascular plants have widely accepted common names. These increase the accessibility of these species to a PROPOSED ANT COMMON NAMES wide public audience, and promote interest in them. In Proposed common names, and explanations for them, for contrast, the vast majority of insects and other arthropods 62 genera, 142 species-groups and 50 species of Australian have no common name beyond the ordinal level, unless they ants are presented in Appendix I, Table A1.
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  • Survey for Ants on the Island of Maui, Hawaii, with Emphasis on the Little Fire Ant (Wasmannia Auropunctata)
    CORE Metadata, citation and similar papers at core.ac.uk Provided by ScholarSpace at University of Hawai'i at Manoa PACIFIC COOPERATIVE STUDIES UNIT UNIVERSITY OF HAWAI`I AT MĀNOA Dr. David C. Duffy, Unit Leader Department of Botany 3190 Maile Way, St. John #408 Honolulu, Hawai’i 96822 T Technical Report 156 SURVEY FOR ANTS ON THE ISLAND OF MAUI, HAWAII, WITH EMPHASIS ON THE LITTLE FIRE ANT (WASMANNIA AUROPUNCTATA) May 2008 1 1 2 Forest Starr , Kim Starr , and Lloyd L. Loope 1 Pacific Cooperative Studies Unit, Department of Botany, University of Hawaii, Honolulu, HI 96822 2 U.S. Geological Survey, Pacific Island Ecosystems Research Center, Haleakala Field Station, P.O. Box 369, Makawao, HI 96768 Image of Wasmannia auropunctata by April Noble (AntWeb) ABSTRACT The little fire ant (LFA), Wasmannia auropunctata, is an aggressive pest ant with a painful sting that has spread to many parts of the world through human commerce. In the State of Hawaii, LFA had been intercepted previously as early as 1930, but only recently, in 1999, were established populations found in the Puna District, on the island of Hawaii (Big Island), occupying residential and agricultural sites, such as fruit orchards and plant nurseries. A single population was found on Kauai in 1999, but it has been contained and nearly eradicated. However, on Hawaii island, LFA is now well established in the Puna/Hilo area, with at least 50 sites covering at least several hundred acres. Even though nursery shipments leaving Hilo are checked for LFA by inspectors of the Hawaii Department of Agriculture, it is likely that LFA-infested shipments have reached Maui.
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  • Ant and Termite Distributions on Oahu, Hawai'i a Thesis
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