The Role of the Novel Weapons and Enemy Release
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Biological Control of St John's Wort Using Chrysolina Leaf Beetles (DSE
June 1999 Biological control of St John's wort LC0152 with the chrysolina leaf beetles ISSN 1329-833X Keith Turnbull Research Institute (Frankston) Common and scientific names Pupae - in globular cells in the soil at up to 5 cm depth. St John’s wort leaf beetles Life cycle Chrysolina hyperici (Förster) Females lay eggs on the undersides of leaves or leaf buds Chrysolina quadrigemina (Suffrian) in autumn. C. quadrigemina larvae emerge after about 3 Background weeks and overwinter as larvae. C. hyperici overwinters in the egg stage. Larvae consume the young leaves and buds St John’s wort, Hypericum perforatum, was introduced in of procumbent autumn and winter growth. Larger larvae the Ovens Valley of Victoria as a medicinal plant in the leave the plant during the day and return to feed at night. 1860s. It spread rapidly and was well established by the When mature, they pupate in the soil at a depth of a few early 1900s. It is a serious weed of improved pastures, centimetres. The pupal stage lasts 2 to 3 weeks and adults roadsides and neglected areas in north east Victoria and is emerge in the spring. Adult beetles defoliate the erect an increasing problem in dry forests and woodlands. In spring plants and enter a resting stage (aestivation or natural areas it is a serious environmental weed which can diapause) under the bark of trees during summer. out-compete other ground storey plants. St John’s wort is a Regionally Prohibited Weed in the Corangamite and Port Phillip West Catchment and Land Protection Regions, and a Regionally Controlled Weed in all other areas of Victoria except Mallee CaLP Region. -
And Belowground Insect Herbivory Mediates Invasion Dynamics and Impact of an Exotic Plant
plants Article Release from Above- and Belowground Insect Herbivory Mediates Invasion Dynamics and Impact of an Exotic Plant Lotte Korell 1,2,3,4,* , Martin Schädler 3,4, Roland Brandl 5, Susanne Schreiter 6 and Harald Auge 3,4 1 Plant Ecology and Geobotany, Department of Ecology, University of Marburg, Karl-von-Frisch-Str. 8, 35032 Marburg, Germany 2 Institute of Biology, Martin Luther University Halle-Wittenberg, Am Kirchtor 1, 06108 Halle (Saale), Germany 3 Department of Community Ecology, Helmholtz-Centre for Environmental Research -UFZ, Theodor-Lieser-Str. 4, 06120 Halle, Germany; [email protected] (M.S.); [email protected] (H.A.) 4 German Centre for Integrative Biodiversity Research (iDiv), Halle-Jena-Leipzig, Deutscher Platz 5e, 04103 Leipzig, Germany 5 Animal Ecology, Department of Ecology, University of Marburg, Karl-von-Frisch-Str. 8, 35032 Marburg, Germany; [email protected] 6 Department of Soil System Science, Helmholtz-Centre for Environmental Research - UFZ, Theodor-Lieser-Str. 4, 06120 Halle, Germany; [email protected] * Correspondence: [email protected] Received: 28 October 2019; Accepted: 21 November 2019; Published: 26 November 2019 Abstract: The enemy-release hypothesis is one of the most popular but also most discussed hypotheses to explain invasion success. However, there is a lack of explicit, experimental tests of predictions of the enemy-release hypothesis (ERH), particularly regarding the effects of above- and belowground herbivory. Long-term studies investigating the relative effect of herbivores on invasive vs. native plant species within a community are still lacking. Here, we report on a long-term field experiment in an old-field community, invaded by Solidago canadensis s. -
Review of the National Ambient Air Quality Standards for Ozone
Review of the National Ambient Air Quality Standards for Ozone: Policy Assessment of Scientific and Technical Information Appendices to OAQPS Staff Paper EPA-452/R-07-003 January 2007 Review of the National Ambient Air Quality Standards for Ozone: Policy Assessment of Scientific and Technical Information Appendices to OAQPS Staff Paper U.S. Environmental Protection Agency Office of Air Quality Planning and Standards Research Triangle Park, North Carolina APPENDICES APPENDIX 2A. PLOTS OF DIURNAL POLICY RELEVANT BACKGROUND OZONE PATTERNS FOR 12 URBAN AREAS BASED ON RUNS OF THE GEOS- CHEM MODEL FOR APRIL-OCTOBER 2001 ..................................................................... 2A-1 APPENDIX 3A. MECHANISMS OF TOXICITY ................................................................. 3A-1 APPENDIX 3B. TABLE OF KEY EPIDEMIOLOGICAL STUDIES................................... 3B-1 APPENDIX 3C. TABLE OF KEY CONTROLLED HUMAN EXPOSURE STUDIES....... 3C-1 APPENDIX 4A: EXPOSURE TABLES................................................................................. 4A-1 APPENDIX 5A.1: OZONE AIR QUALITY INFORMATION FOR 12 URBAN AREAS... 5A-1 APPENDIX 5A.2: SCATTER PLOTS.................................................................................. 5A-10 APPENDIX 5B1: TABLES OF STUDY-SPECIFIC INFORMATION................................. 5B-1 APPENDIX 5B2: CONCENTRATION-RESPONSE FUNCTIONS AND HEALTH IMPACT FUNCTIONS............................................................................................................ 5B-8 APPENDIX 5B3: -
Biological Control
KLAMATH WEED (= ST. JOHN'S WORT) Hypericum perforatum L. – Hypericaceae Dr. E. Fred Legner, University of California Retrieved from: http://faculty.ucr.edu/~legneref/biotact/ch-66.htm This weed is of European origin, and was first reported as a pest in northern California near the Klamath River. It increased and spread rapidly and by 1944 had occupied over two million acres of rangeland in thirty counties of California. Not only were food forage plants greatly reduced but cattle and sheep lost weight when eating the weed because of its toxic effect, sensitizing them to sunlight. This resulted in such a great decrease in land values that it became almost impossible for ranchers to borrow money for development (DeBach 1974). Chemical herbicides were available but not practical because of cost and the inaccessibility of most of the infested land. Dr. Harry S. Smith, head of biological control work in California, proposed the importation of insects that attacked the weed as early as 1922, but the thought of deliberately introducing a plant feeding insect was not acceptable at that time. At the same time, in Australia phytophagous insects to control Klamath weed were being introduced from England and Europe beginning in 1929, and Dr. Smith in California followed the progress there with great interest through correspondence with Dr. A. J. Nicholson, Chief Entomologist for the Commonwealth Scientific and Industrial Research Organization (CSIRO). Authorization was finally obtained in 1944 to import three species of beetles that showed promise against the weed in Australia. It was not possible then to consider importations from Europe because of World War II, but rather simple to bring material from Australia through the cooperation of the United States Army Transport Command. -
Title Geographic Variations in Phenotypic Traits of the Exotic Herb Solidago Altissima and Abundance of Recent Established Exoti
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Kyoto University Research Information Repository Geographic variations in phenotypic traits of the exotic herb Title Solidago altissima and abundance of recent established exotic herbivorous insects Author(s) Sakata, Yuzu; Ohgushi, Takayuki; Isagi, Yuji Citation Journal of Plant Interactions (2013), 8(3): 216-218 Issue Date 2013-04-10 URL http://hdl.handle.net/2433/193002 The Version of Record of this manuscript has been published Right and is available in Journal of Plant Interactions (2013) http://www.tandfonline.com/10.1080/17429145.2013.779036. Type Journal Article Textversion author Kyoto University 1 Geographic variations in phenotypic traits of the exotic herb Solidago altissima 2 and abundance of recent established exotic herbivorous insects 3 Author: Yuzu Sakataa, Takayuki Ohgushib, Yuji Isagia 4 Address: a Laboratory of Forest Biology, Division of Forest and Biomaterials Science, 5 Graduate School of Agriculture, Kyoto University, Kyoto 606-8502, Japan 6 b Center for Ecological Research, Kyoto University, Otsu 520-2113, Japan 7 Author for correspondence: [email protected] 8 Tel: +81 075-753-6129 9 Fax: +81 075-753-6129 10 11 12 13 14 Abstract 15 Many invasive plants increase aggressiveness after introduction. Since 16 evolutionary forces such as herbivore pressure may change over different time scales, 17 understanding the changes in biotic interactions in invasive plants through time can 18 clarify the mechanism of their evolution in aggressiveness. In this study we examined 19 the geographic variation in phenotypic traits of Solidago altissima and the abundance of 20 two exotic herbivorous insect species (the aphid, Uroleucon nigrotuberculatum and the 21 lacebug, Corythucha marmorata), which are recently expanding their habitat on S. -
Floristic Quality Assessment Report
FLORISTIC QUALITY ASSESSMENT IN INDIANA: THE CONCEPT, USE, AND DEVELOPMENT OF COEFFICIENTS OF CONSERVATISM Tulip poplar (Liriodendron tulipifera) the State tree of Indiana June 2004 Final Report for ARN A305-4-53 EPA Wetland Program Development Grant CD975586-01 Prepared by: Paul E. Rothrock, Ph.D. Taylor University Upland, IN 46989-1001 Introduction Since the early nineteenth century the Indiana landscape has undergone a massive transformation (Jackson 1997). In the pre-settlement period, Indiana was an almost unbroken blanket of forests, prairies, and wetlands. Much of the land was cleared, plowed, or drained for lumber, the raising of crops, and a range of urban and industrial activities. Indiana’s native biota is now restricted to relatively small and often isolated tracts across the State. This fragmentation and reduction of the State’s biological diversity has challenged Hoosiers to look carefully at how to monitor further changes within our remnant natural communities and how to effectively conserve and even restore many of these valuable places within our State. To meet this monitoring, conservation, and restoration challenge, one needs to develop a variety of appropriate analytical tools. Ideally these techniques should be simple to learn and apply, give consistent results between different observers, and be repeatable. Floristic Assessment, which includes metrics such as the Floristic Quality Index (FQI) and Mean C values, has gained wide acceptance among environmental scientists and decision-makers, land stewards, and restoration ecologists in Indiana’s neighboring states and regions: Illinois (Taft et al. 1997), Michigan (Herman et al. 1996), Missouri (Ladd 1996), and Wisconsin (Bernthal 2003) as well as northern Ohio (Andreas 1993) and southern Ontario (Oldham et al. -
Response of Two Chrysolina Species to Different Hypericum Hosts
Seventeenth Australasian Weeds Conference Response of two Chrysolina species to different Hypericum hosts Ronny Groenteman', Simon V. Fowler' and Jon J. Sullivan2 ' Landcare Research, Gerald Street, PO Box 40, Lincoln, New Zealand 2Bio-Protection Research Centre, PO Box 84, Lincoln University, Lincoln, New Zealand Corresponding author: [email protected] SummaryChrysolina hyperici and C. quadrigemina introduced in 1963 but, for many years was thought (Coleoptera: Chrysomelidae) were introduced to to have failed to establish (reviewed by Hancox et al. New Zealand for biological control of St John's wort 1986). Chrysolina quadrigemina was rediscovered in (SJW), Hypericum perforatum, following successful the late 1980s (Fraser and Emberson 1987). It is now biological control in Australia. In other parts of the abundant in mixed populations with C. hyperici (R. invaded range of SJW worldwide C. quadrigemina is Groenteman personal observations). generally accepted as the more significant contributor St John's wort beetles are not strictly restricted to to SJW successful biocontrol. Their ability to feed and H. perforatum, and are known to be able to develop on develop on indigenous Hypericum species was not other Hypericum species (some examples are reviewed tested. Chrysolina hyperici established well while C. by Harris 1988). New Zealand hosts 10 naturalised quadrigemina was initially thought to have failed to es- (Healy 1972) and four indigenous (Heenan 2008) tablish in New Zealand, although it is now widespread. Hypericum species. Little is known about the suit- Thus, identifying differences between Chrysolina spe- ability and impacts of either Chrysolina species on cies in host preference and performance would have these Hypericum species. -
Paolo Romagnoli & Bruno Foggi Vascular Flora of the Upper
Paolo Romagnoli & Bruno Foggi Vascular Flora of the upper Sestaione Valley (NW-Tuscany, Italy) Abstract Romagnoli, P. & Foggi B.: Vascular Flora of the upper Sestaione Valley (NW-Tuscany, Italy). — Fl. Medit. 15: 225-305. 2005. — ISSN 1120-4052. The vascular flora of the Upper Sestaione valley is here examined. The check-list reported con- sists of 580 species, from which 8 must be excluded (excludendae) and 27 considered doubtful. The checked flora totals 545 species: 99 of these were not found during our researches and can- not be confirmed. The actual flora consists of 446 species, 61 of these are new records for the Upper Sestaione Valley. The biological spectrum shows a clear dominance of hemicryptophytes (67.26 %) and geophytes (14.13 %); the growth form spectrum reveals the occurrence of 368 herbs, 53 woody species and 22 pteridophytes. From phytogeographical analysis it appears there is a significant prevalence of elements of the Boreal subkingdom (258 species), including the Orohypsophyle element (103 species). However the "linkage groups" between the Boreal subkingdom and Tethyan subkingdom are well represented (113 species). Endemics are very important from the phyto-geographical point of view: Festuca riccerii, exclusive to the Tuscan- Emilian Apennine and Murbeckiella zanonii exclusive of the Northern Apennine; Saxifraga aspera subsp. etrusca and Globularia incanescens are endemic to the Tuscan-Emilian Apennine and Apuan Alps whilst Festuca violacea subsp. puccinellii is endemic to the north- ern Apennines and Apuan Alps. The Apennine endemics total 11 species. A clear relationship with the Alpine area is evident from 13 Alpine-Apennine species. The Tuscan-Emilian Apennine marks the southern distribution limit of several alpine and northern-central European entities. -
Native Plants and Why It Matters
Module 14: Native Plants and Why They Matter LSU AgCenter Home Gardening Certificate Course Dr. Joe Willis, Dr. Paula Barton-Willis, Anna Timmerman & Chris Dunaway What is a Native Plant? So many answers! Iris fulva Copper Louisiana Iris A native plant is… Coreopsis tinctoria Plains Coreopsis One that exists in a given region through non-human introduction, directly or indirectly. (Lady Bird Johnson Wildflower Center) Cephalanthus occidentalis Buttonbush A plant that lives or grows naturally in a particular region without direct or indirect human intervention. (USDA National Arboretum) Saurunus cernuus Lizard’s Tail With respect to a particular ecosystem, a species that, other than as a result of an introduction, historically occurred, or currently occurs, in that ecosystem. (US Fish and Wildlife Service) Magnolia grandiflora Southern Magnolia Why Do Native Plants Belong in Our Gardens? Solidago sempervirens Seaside Goldenrod 1. Gain a new appreciation of American flora, which is rich, diverse, and beautiful. “Sense of Place” and “Belonging” in a garden. Salvia coccinea Scarlet Sage 2. Create “mini ecosystems” within habitat that has been developed over time. Hydrangea quercifolia Oakleaf Hydrangea 3. Native plants are best suited to local conditions and adapt to challenges related to weather and soil conditions. Chamaecrista fasticulata Partridge Pea 4. Foster diversity within a garden landscape. Aquilegia chrysantha var. hinckleyana Hinckley’s Columbine 5. Connect to local ecological history and indigenous traditions. Eyrthrina herbacea Coralbean aka Mamou 6. Support pollinators and other beneficial insect species. Native plants are a “better” choice for meeting insect food/habitat needs. “Specialist” species are unable to switch host plants as easy as “Generalist” feeders. -
Fresh Floral Resource Guide Seasonal Floral
Fresh Floral RESOURCE GUIDE SEASONAL FLORAL Everyday Spring Summer Fall Winter Alstroemeria Agapanthus Agapanthus Autumn Leaves Amaryllis Anthurium Amaryllis Amaranthus Chrysanthemum Anemone Aster Anemone Astilbe Dahlia Evergreen Bells of Ireland Cherry Blossom Cosmos Heather Heather Bupleurum Daffodil Dahlia Nerine Lily Muscari Calla Lily Dogwood Daisy Ranunculus Nerine Lily Carnation Forsythia Delphinium Seasonal Berries Poinsettia Craspedia Heather Garden Rose Sunflower Ranunculus Eryngium Hyacinth Gladiolus Tuberose Tulip Fiddlehead Fern Lilac Lady Mantle Waxflower Freesia Lily of the Valley Larkspur Gardenia Muscari Nerine Lily Gerbera Nerine Lily Scabiosa Gloriosa Lily Peony Snapdragon Hydrangea Ranunculus Tuberose Hypericum Sweet Pea Violet Iris Tuberose Zinnia Kermit’ Pompom Tulip Liatris Viburnum Lily Waxflower Limonium Lisianthus Lotus Pod Orchird Ornithogalum Arabicum Queen Anne’s Lace Rose Solidago Solidaster Spider Gerbera Statice Stephanotis Stock Trachelium Viking Mini Pompom BloomNet Fresh Floral Resource Guide 1 CARE & HANDLING Alstroemeria Alstroemeria is extremely ethylene sensitive. Remove any foliage that will go below the water line, as it deteriorates quickly. Then cut stems and place in a vase with room temperature water and floral food. Category: Basic Color: Yellow, Orange, White, Pink, Red, Lavender, Purple, Magenta, Peach, Bi Color Amaryllis Do not store amaryllis at below 41 degrees as this may discolor blooms. Amaryllis flowers damage very easily in bud or bloom stage. Allow space around the blooms in a bucket or design to prohibit damage. Category: Novelty Color: White, Pink, Red, Peach, Orange, Bi Color Anthurium An extremely long lasting Tropical flower with a vase life from 15 to 30 days (mini and small grades tend to have a shorter vase life). -
Fire in the Southeastern Grasslands, By
Fire in the Southeastern Grasslands RICHARD J. VOGL Department of Biology California State University Los Angeles, CA 90032 INTRODUCTION ~ERE has been more research on the effects of fire in the southeastern United States than in any region of North America. Most studies have been concerned with the effects of fire on the trees, including the role of fire in controlling hardwood suc cession, fire damage to trees, the effects of fire on soils and litter, the influence of fire on conifer growth and reproduction, and the relationships of fire to tree diseases (Garren 1943; Ahlgren and Ahlgren 1960; Cushwa 1968). A lesser, but stilI substantial number of studies have been focused on the effects of fire on forage yields and livestock production (Wahlenberg et al. 1939), and the use of fire in wildlife management in the Southeast. But academic or phy tosociological studies of the vegetational composition and of the effects of fire on the understory vegetation are generally lacking. Except for some range and wildlife research and several general studies (Wells and Shunk 1931; Leukel and St<Jkes 1939; Biswell and Lemon 1943; Burton 1944; Lemon 1949, 1967; Campbell 1955; Biswell1958; Hodgkins 1958; Arata 1959; Cushwa et al. 1966, 1970; Wolters 1972) , most investigators have ignored the herbaceous cover or grassland vegetation under southeastern trees. Even early botanists often became more interested in the unusual botanical features such as the southern extent of Appalachian tree species (Harper 1943, 1952), the description of the silaceous dunes of the 175 RICHARD J. VOGL Gulf Coast (Kurz 1942), the habits of eastern red cedar (Harper 1912), the vegetation of the Okefenokee Swamp (Wright and Wright 1932), or why the Black Belt Prairie of Alabama was treeless (Ranking and Davis 1971), thereby neglecting the widespread and common grassland vegetation and its relationship to fire. -
Germinative Response to Heat Treatments in Relation to Resprouting Ability
Journal of Ecology 2008, 96, 543–552 doi: 10.1111/j.1365-2745.2008.01359.x BurningBlackwell Publishing Ltd seeds: germinative response to heat treatments in relation to resprouting ability S. Paula and J. G. Pausas* Centro de Estudios Ambientales del Mediterráneo (CEAM), Charles R. Darwin 14, Parc Tecnològic, Paterna, València 46980, Spain Summary 1. In Mediterranean fire-prone ecosystems, plant species persist and regenerate after fire by resprouting, by recruiting new individuals from a seed bank (post-fire seeding), or by both resprouting and post-fire seeding. Since species with resprouting ability are already able to persist in fire-prone ecosystems, we hypothesize that they have been subjected to lower evolutionary pressure to acquire traits allowing or enhancing post-fire recruitment. Consequently, we predict that the germination of non-resprouters is more likely to be increased or at least unaffected by heat than the germination of resprouters. 2. To test this hypothesis we compiled published experiments carried out in Mediterranean Basin species where seeds were exposed to different heat treatments. We compared the probability of heat-tolerant germination (i.e. heated seeds had greater or equal germination than the control), the probability of heat-stimulated germination (i.e. heated seeds had greater germination than the control) and the stimulation magnitude (differences in proportion of germination of the heated seeds in relation to the untreated seeds, for heat-stimulated treatments) between resprouters and non-resprouters. 3. Non-resprouters showed higher probability of heat-tolerance, higher probability of heat- stimulation and higher stimulation magnitude even when phylogenetic relatedness was considered. Differences between life-forms and post-fire seeding ability do not explain this pattern.