TANSY RAGWORT (Senecio Jacobaea)
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Protection of Pandora Moth (Coloradia Pandora Blake) Eggs from Consumption by Golden-Mantled Ground Squirrels (Spermophilus Lateralis Say)
AN ABSTRACT OF THE THESIS OF Elizabeth Ann Gerson for the degree of Master of Science in Forest Science presented on 10 January, 1995. Title: Protection of Pandora Moth (Coloradia pandora Blake) Eggs From Consumption by Golden-mantled Ground Squirrels (Spermophilus lateralis Say) Abstract approved: Redacted for Privacy William C. McComb Endemic populations of pandora moths (Coloradia pandora Blake), a defoliator of western pine forests, proliferated to epidemic levels in central Oregon in 1986 and increased dramatically through 1994. Golden-mantled ground squirrels (Spermophilus lateralis Say) consume adult pandora moths, but reject nutritionally valuable eggs from gravid females. Feeding trials with captive S. lateralis were conducted to identify the mode of egg protection. Chemical constituents of fertilized eggs were separated through a polarity gradient of solvent extractions. Consumption of the resulting hexane, dichloromethane, and water egg fractions, and the extracted egg tissue residue, was evaluated by randomized 2-choice feeding tests. Consumption of four physically distinct egg fractions (whole eggs, "whole" egg shells, ground egg shells, and egg contents) also was evaluated. These bioassays indicated that C. pandora eggs are not protected chemically, however, the egg shell does inhibit S. lateralis consumption. Egg protection is one mechanism that enables C. pandora to persist within the forest food web. Spermophilus lateralis, a common and often abundant rodent of central Oregon pine forests, is a natural enemy of C. pandora -
Checklist of the Vascular Plants of Redwood National Park
Humboldt State University Digital Commons @ Humboldt State University Botanical Studies Open Educational Resources and Data 9-17-2018 Checklist of the Vascular Plants of Redwood National Park James P. Smith Jr Humboldt State University, [email protected] Follow this and additional works at: https://digitalcommons.humboldt.edu/botany_jps Part of the Botany Commons Recommended Citation Smith, James P. Jr, "Checklist of the Vascular Plants of Redwood National Park" (2018). Botanical Studies. 85. https://digitalcommons.humboldt.edu/botany_jps/85 This Flora of Northwest California-Checklists of Local Sites is brought to you for free and open access by the Open Educational Resources and Data at Digital Commons @ Humboldt State University. It has been accepted for inclusion in Botanical Studies by an authorized administrator of Digital Commons @ Humboldt State University. For more information, please contact [email protected]. A CHECKLIST OF THE VASCULAR PLANTS OF THE REDWOOD NATIONAL & STATE PARKS James P. Smith, Jr. Professor Emeritus of Botany Department of Biological Sciences Humboldt State Univerity Arcata, California 14 September 2018 The Redwood National and State Parks are located in Del Norte and Humboldt counties in coastal northwestern California. The national park was F E R N S established in 1968. In 1994, a cooperative agreement with the California Department of Parks and Recreation added Del Norte Coast, Prairie Creek, Athyriaceae – Lady Fern Family and Jedediah Smith Redwoods state parks to form a single administrative Athyrium filix-femina var. cyclosporum • northwestern lady fern unit. Together they comprise about 133,000 acres (540 km2), including 37 miles of coast line. Almost half of the remaining old growth redwood forests Blechnaceae – Deer Fern Family are protected in these four parks. -
Appendix C Plant and Animal Species Observed
Appendix C Plant and Animal Species Observed This list includes vascular plants, mammals, birds, reptiles, and amphibians observed in the BSA by biologists during various surveys in 2005 and 2006. This list does not include invertebrate species. Invertebrates that would be most commonly encountered on the site would include butterflies, flies, dragonflies, damselflies, beetles, earwigs, grasshoppers, crickets, termites, true bugs, mantids, lacewings, bees, wasps, ants, and spiders. PLANT SPECIES OBSERVED Scientific Name Common Name Invasive Plant Rating CLUB AND SPIKE MOSSES Selaginellaceae Spike moss family Selaginella cinerascens Mesa spikemoss TRUE FERNS Azollaceae Mosquito fern family Azolla filiculoides Pacific mosquito fern Marsileaceae Marsilea family Marsilea vestita Hairy waterclover Pilularia americana American pillwort Pteridaceae Lip fern family Pellaea andromedifolia Coffee fern Pentagramma triangularis Goldenback fern PINOPHYTA GYMNOSPERMS Cupressaceace Cypress family Juniperus californica California juniper DICOT FLOWERING PLANTS Aizoaceae Carpet weed family Carpobrotus edulis* Hottentot-fig HIGH Mesembryanthemum nodiflorum* Slender-leaved ice plant Trianthema portulacastrum Horse-purslane Amaranthaceae Amaranth family Amaranthus albus* Tumbling pigweed Amaranthus palmeri Palmer’s pigweed Amaranthus sp. Pigweed Anacardiaceae Sumac family Malosma laurina Laurel sumac Rhus ovata Sugar bush Rhus trilobata Skunkbush sumac Schinus molle* Peruvian pepper tree LIMITED Schinus terebinthifolius* Brazilian pepper tree LIMITED Mid -
NEWSLETTER• of the MICHIGAN ENTOMOLOGICAL SOCIETY
NEWSLETTER• of the MICHIGAN ENTOMOLOGICAL SOCIETY Volume 38, Numbers 4 December, 1993 Impacts ofBt on Non-Target Lepidoptera John W. Peacock, David L. Wagner, and Dale F. Schweitzer USDA Forest Service, Hamden, CT; University of Connecticut, Storrs, CT; and The Nature Conservancy, Port Norris, NT, respectively Introduction gypsy moth in Oregon. Sample et a1. ing attempts bycertain birds. In another (1 993) have likewise reported a signifi study, Bellocq et al. (1992) showed that Bacillus thuringiensis Berliner var. cant reduction inspecies abundance and the use of Btk increased immigration kurstaki (Btk) is one of the pesticides richness in non-target Lepidoptera in rates andcaused d ietary shifts inshrews. most commonly employed against lepi field studies in eastern West Virginia. We report here a summary of our dopteran forest pests. In the eastern U.S., James et al. (1993) haveshown thatBtk is studies aimed at determining the effect where millionsofhectares of deciduous toxic to late, but not early, instar larvae of Btko n non-target Lepidoptera inboth forest have been defoliated by the ''Eu of the beneficial cinnabar moth, Tyria laboratoryand field studies. Laboratory ropean" gypsy moth, Lymantria dispar jacobaeae (L.). bioassays were conducted on larvae in (L.), Btk has been used extenSively to In addition to its direct effects on seven families of native eastern U.S. slow the spread of this pest and to re native Lepidoptera, Btk can indirectly Macrolepidoptera. Field studies were duce defoliation. In 1992 alone, over affect other animals that rely on lepi carried out in Rockbridge County, Vir 300,000 ha were treated with Btk, in dopterous larvae as a primary source of ginia, and were the first to evaluate non cluding gypsy moth suppression activi food. -
Poisonous Weeds and Toxic Factors in Hay Crops
Poisonous Weeds And Toxic Factors In Hay Crops: Why You Should Worry Birgit Puschner Veterinary Toxicologist [email protected] School of Veterinary Medicine, UC Davis Overview of Today’s Talk • When to suspect a poisoning • Toxic plants: • Nitrate accumulators • Pyrrolizidine alkaloids • Oleander • Grasses that cause mechanical irritation Factors Contributing to Poisoning • Animal • Plant • Sensitive species • Palatable? • Adaptation to tolerate • Right time of the year? toxic plants is possible à concentrations of • What other feed is toxins vary with season available? • Does the plant remain • Unable to avoid toxic toxic when dried? plant (i.e. in hay cubes) Resources • Textbooks: • A Guide to Plant Poisoning of Animals in North America: by A.P. Knight and R.G. Walter, 1st edition, 2001. Teton NewMedia. www.tetonnm.com • UCANR publication: http://anrcatalog.ucdavis.edu/pdf/8398.pdf Detailed publication on Livestock-poisoning Plants of California (link on CERE under Lab resources) • Websites (with images and location) • https://www.ars.usda.gov/pacific-west- area/logan-ut/poisonous-plant- research/docs/poisonous-plants-by-toxic- syndrome/ • http://plants.usda.gov/about_plants.html Nitrate/Nitrite Accumulators • Sorghum spp (Sudan grass, Johnson grass) • Pigweed (Amaranthus retroflexus) • Lamb’s-quarters (Chenopodium album) • Alfalfa, oat, corn, nightshades (Solanum) Chenopodium album Pigweed Johnson grass Sudan grass Orchard Grass Hay 5,900 ppm Nitrate Pigweed Sudan Hay 18,800 ppm Nitrate Amaranthus retroflexus Nitrate/Nitrite – Mechanism • Only ruminants and pseudoruminants are susceptible • Nitrate in plants à converted to toxic nitrite • Nitrite à methemoglobin • Methemoglobin: incapable of Oxygen transport à Anoxia NO3/NO2 – Clinical signs • Acute syndrome: – Onset within 1/2 - 4 hours after feeding – GI irritation, difficulty breathing, tremors, ataxia – Rapid, weak heart beat – Convulsions, death in 6 - 24 hours – Abortions, esp. -
BSBI News Index 121-130 ABC 8Pt FINAL
BSBI News INDEX to Nos 121 – 130 September 2012 to September 2015 Compiled by GWYNN ELLIS ISSN 2397-8813 1 GUIDE TO THE INDEX ABBREVIATIONS AEM Annual Exhibition Meeting Illus. Illustration AGM Annual General Meeting Infl. Inflorescence ASM Annual Summer Meeting Lvs Leaves cf. confer (compare) photo © photo copyright holder congrats congratulations Rev. Review CS Colour Section Rpt Report del. delineavit (drawn) s.l. sensu lato (broad sense) Descr. Description s.s. sensu stricto (narrow sense) Diag. Diagram v.c. vice-county Exbn Exhibition v.cc. vice-counties Exbt Exhibit (♀) female parent Fld Mtg Rpt Field Meeting Report (♂) male parent Fls Flowers ACKNOWLEDGEMENTS: The compiler wishes to thank David Pearman for much helpful advice and for scrutinising the final text. However, responsibility for checking the index and its final form rests solely with the compiler. BOOKS et al. are italicised as are Periodicals and scientific names COLOUR PAGES: In the index all colour page numbers are distinguished by being underlined with the cover pages enclosed in square brackets [ ]. The front cover and inside front cover are numbered [i] and [ii] respectively while the inside back and back cover pages are numbered according to the number of pages, thus with an issue of 76 pages the inside back cover is [77] and the back cover [78]. Colour Section plates are numbered CS1, CS2, CS3, CS4. Photographers are now indexed by name with the qualification (photo ©) COMPILATION: Using the original text on computer, the entries for each issue were generated by deleting all unwanted text. After checking, the entries were then sorted into alphabetical order, condensed, and finally output as pdf files for the Printer. -
APPENDIX A—CHECKLIST of VASCULAR PLANTS Observed in the Vicinity of Sheffield
PLANTS CHECKLIST APPENDIX A—CHECKLIST OF VASCULAR PLANTS Observed in the Vicinity of Sheffield COMMON NAME ORIGIN HORSETAILS HORSETAILS (Family Equisetaceae) ❏ Equisetum arvense field horsetail N ❏ Equisetum hyemale tall scouring-rush N FERNS ADDER’S-TONGUES (Family Ophioglossaceae) ❏ Botrychium multifidum leathery grape fern N (E) ROYAL FERNS (Family Osmundaceae) ❏ Osmunda regalis royal fern N HAY-SCENTED (Family Dennstaedtiaceae) ❏ Dennstaedtia punctilobula hay-scented fern N SPLEENWORTS (Family Aspleniaceae) ❏ Asplenium platyneuron ebony spleenwort N WOOD FERNS (Family Dryopteridaceae) ❏ Cystopteris fragilis brittle fern or fragile fern N (X) ❏ Cystopteris protrusa lowland fragile fern N ❏ Dryopteris marginalis leathery wood fern N ❏ Matteuccia struthiopteris ostrich fern N ❏ Onoclea sensibilis sensitive fern N ❏ Polystichum acrostichoides Christmas fern N GYNOSPERMS (GINKGOS & CONIFERS) GINKGOS (Family Ginkgoaceae) ❏ Ginkgo biloba ginkgo or maidenhair tree C PINES (Family Pinaceae) ❏ Picea glauca conica dwarf Alberta spruce C ❏ Picea pungens gluca blue spruce C ❏ Pinus nigra Austrian pine C ❏ Pinus strobus eastern white pine N ❏ Pseudotsuga menziesii Douglas fir C ❏ Tsuga canadensis eastern hemlock N CYPRESSES (Family Cupressaceae) ❏ Juniperus virginiana eastern red-cedar N ❏ Thuja occidentalis arbor vitae N YEWS (Family Taxaceae) ❏ Taxus canadensis Canada yew N ANGIOSPERMS (FLOWERING PLANTS) DICOTYLEDONS (CLASS MAGNOLIOPSIDA) MAGNOLIAS (Family Magnoliaceae) ❏ Liriodendron tulipifera tulip-tree or tulip-poplar N ❏ Magnolia acuminata -
Common Groundsel Senecio Vulgaris L
PNW 466 • July 1994 Common Groundsel Senecio vulgaris L. S. Aldrich-Markham C ommon groundsel, native to Europe, is now common throughout the temperate re- gions of the world. It is wide- spread in Oregon, Washington, and Idaho, but most common west of the Cascade Mountains. This weed is found in many crops, including forages, cere- als, mint, berries, and row crops, as well as in ornamentals and vegetable gardens. Groundsel is especially a problem in forage crops be- cause it is toxic to livestock. The toxins are four pyrrolizidine alkaloids, which cause irrevers- ible liver damage. Some of the same alkaloids are found in tansy ragwort (Senecio jacobea L.), but tansy ragwort also con- tains two additional alkaloids that are more toxic. Poisoning occurs most com- monly in situations where ani- mals cannot separate out the toxic plants—when they are mixed with the forage in a pas- ture, or when they are fed in hay or silage. The liver disease is chronic and progressive, re- sulting in death months later in most animals, with few or no Susan Aldrich-Markham, Extension agent, Yamhill County, Oregon State University. Figure 1.—Common groundsel grows from 4 to 18 inches tall. Leaves are deeply lobed with toothed margins. The lower stems and undersides of basal leaves usually are purplish-colored. A Pacific Northwest Extension Publication • Oregon • Idaho • Washington symptoms until 2 or 3 days be- hairy or woolly. Leaves have the base of the plant, becoming fore death. little or no leaf stalk, and are increasingly smaller toward the A lethal amount for cattle or arranged along the stem in a top. -
Genetic Basis of Speed of Development in Senecio Vulgaris L
Heredity 77 (1996) 544—554 Received 19 January 1996 Genetic basis of speed of development in Senecio vulgaris L. var. vulgaris, S. vulgaris ssp. denticulatus (O.F. Muell.) P.D. Sell, and Senecio vernalis Waldst. & Kit. HANS PETER COMES* & JOACHIM W. KADEREIT Institut für Spezielle Botanik u. Botanischer Garten, Johannes Gutenberg-Universitat Mainz, Bentze/weg 9, 55099 Mainz, Germany Thegenetic basis of differences in speed of development from germination to first bud formation was investigated in Senecio vulgaris var. vulgaris and S. vulgaris ssp. denticulatus, and also in S. vernalis sampled from Israel and Germany. In the case of S. vulgaris, F2 segregation analysis and the recovery of very late and very early lines from extreme F2 phenotypes showed that differences can be explained by a single major gene model, whereas segregation data from F2 and backcross progenies in S. vernalis are not incompatible with a digenic model of inheritance. Senecio vernalis from Israel and S. vulgaris var. vulgaris reached the different developmental stages in a substantially shorter time than did C. European S. vemalis and S. vulgaris ssp. denticulatus. In both species the increased speed of development was achieved through drastic abbreviation of the rosette stage of development rather than through an acceleration of the entire developmental programme. It is suggested that the genes controlling speed of development in S. vulgaris and S. vemalis may be homologous to major heterochronic genes identified from mutants of Arabidopsis thaliana (e.g. early flowering [elfl—3]). Keywords:earlyflowering mutants, genetic basis, life history trait, Senecio vemalis, Senecio vulgaris, speed of development. Introduction required for development from germination to first flower bud formation, anthesis, and fruiting. -
And Ragwort Flea Beetle, Cinnabar Moths and Other Organisms That Feed on Ragwort
Copyright is owned by the Author of the thesis. Permission is given for a copy to be downloaded by an individual for the purpose of research and private study only. The thesis may not be reproduced elsewhere without the permission of the Author. Interaction of population processes in ragwort (Senecio jacobaea L.) and ragwort flea.bee tle (Longitarsus jacobaeae Waterbouse) A Thesis presented in partial fulflllment of the requirements for the Degree of Doctor of Philosophy in Ecology at Massey University. April 2000 11 Declaration of Originality This thesis represents the original work of the author, except where otherwise acknowledged. It has not been submitted previously for a degree at any University. Aung Kyi III Acknowledgements I am sincerely grateful to my supervisors, Professor Brian Springett, Dr lan Stringer (Ecology, the Institute of Natural Resources, Massey University), and Dr Peter McGregor (Landcare Research) for their encouragement, supervision and patience over this study and their help in drafting this thesis. I am also indebted to Mr Keith Betteridge (AgResearch) for his valuable advice on the laboratory study on the movement of first instar larvae of ragwort flea beetle in different soils; Dr. Ed Minot (Ecology, Massey University) for explaining how to use the STELLA model; Dr. Jill Rapson (Ecology, Massey University) for comments on my PhD thesis proposal; Dr. Siva Ganesh, Dr. Jenny Brown and Mr. Duncan Hedderley (Statistics, Massey University) for help with univariate and multivariate analyses; and Dr. Kerry Harrington (Plant Science, Institute of Natural Resources, Massey University) for his comments and suggestion on the toxicity of ragwort and its chemical control. -
Developing Host Range Testing for Cotesia Urabae
1 Appendix 2 Appendix 2: Risks to non-target species from potential biological control agent Cotesia urabae against Uraba lugens in New Zealand L.A. Berndt, A. Sharpe, T.M. Withers, M. Kimberley, and B. Gresham Scion, Private Bag 3020, Rotorua 3046, New Zealand, [email protected] Introduction Biological control of insect pests is a sustainable approach to pest management that seeks to correct ecological imbalances that many new invaders create on arrival in a new country. This is done by introducing carefully selected natural enemies of the pest, usually from its native range. This method is the only means of establishing and maintaining self-sustaining control of pest insects and it is highly cost effective in the long term (Greathead, 1995). However there is considerable concern for the risk new biological control agents might pose to other species in the country of introduction, and most countries now have regulations to manage decisions on whether to allow biological control introductions (Sheppard et al., 2003). A key component of the research required to gain approval to release a new agent is host range testing, to determine what level of risk the agent might pose to native and valued species in the country of introduction. Although methods for this are well developed for weed biological control, protocols are less established for arthropod biological control, and the challenges in conducting tests are greater (Van Driesche and Murray, 2004; van Lenteren et al., 2006; Withers and Browne, 2004). This is because insect ecology and taxonomy are relatively poorly understood, and there are many more species that need to be considered. -
Is the Spread of Non-Native Plants in Alaska Accelerating?
Meeting the Challenge: Invasive Plants in Pacific Northwest Ecosystems IS THE SPREAD OF NON-NATIVE PLANTS IN ALASKA ACCELERATING? Matthew L. Carlson1 and Michael Shephard2 ABSTRACT Alaska has remained relatively unaffected by non-native plants; however, recently the state has started to experience an influx of invasive non-native plants that the rest of the U.S. underwent 60–100 years ago. With the increase in population, gardening, development, and commerce there have been more frequent introductions to Alaska. Many of these species, such as meadow hawkweed (Hieracium caespitosum), Canada thistle (Cirsium arvense), and spotted knapweed (Centaurea biebersteinii), have only localized populations in Alaska. Other species such as reed canary grass (Phalaris arundinacea) and white sweetclover (Melilotus officinalis), both formerly used in roadside seed mixes, are now very widespread and are moving into riparian areas and wetlands. We review the available literature and Alaska’s statewide invasive plant database (AKEPIC, Alaska Exotic Plant Clearinghouse) to summarize changes in Alaska’s non-native flora over the last 65 years. We suggest that Alaska is not immune to invasion, but rather that the exponential increase in non-native plants experienced else- where is delayed by a half century. This review highlights the need for more intensive detection and rapid response work if Alaska is going to remain free of many of the invasive species problems that plague the contiguous U.S. KEYWORDS: Alaska, invasion patterns, invasive plants, non-native plants, plant databases. INTRODUCTION presence of non-native plants. Recently, however, popula- Most botanists and ecologists thought Alaska was immune tions of many non-native species appear to be expanding to the invasion of non-native plants the rest of the United and most troubling, a number of species are spreading into States had experienced, and continue to experience, given natural habitats.