The Green Spruce Aphid in Western Europe
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Picea Sitchensis (Bong.) Carr. Sitka Spruce Pinaceae Pine Family A
Picea sitchensis (Bong.) Carr. Sitka Spruce Pinaceae Pine family A. S. Harris Sitka spruce (Picea sitchensis), known also as tideland spruce, coast spruce, and yellow spruce, is the largest of the world’s spruces and is one of the most prominent forest trees in stands along the northwest coast of North America. This coastal species is seldom found far from tidewater, where moist maritime air and summer fogs help to main- tain humid conditions necessary for growth. Throughout most of its range from northern Califor- nia to Alaska, Sitka spruce is associated with western hemlock (Tsuga heterophylla) in dense stands where growth rates are among the highest in North America. It is a valuable commercial timber species for lumber, pulp, and many special uses (15,16). Habitat Native Range Sitka spruce (fig. 1) grows in a narrow strip along the north Pacific coast from latitude 61” N. in south- central Alaska to 39” N. in northern California. The most extensive portion of the range in both width and elevation is in southeast Alaska and northern British Columbia, where the east-west range extends for about 210 km (130 mi) to include a narrow main- land strip and the many islands of the Alexander Archipelago in Alaska and the Queen Charlotte Is- lands in British Columbia (24). North and west of southeast Alaska, along the Gulf of Alaska to Prince William Sound, the range is restricted by steep mountains and Piedmont glaciers edging the sea. Within Prince William Sound, the range again widens to about 105 km (65 mi) to include many offshore islands. -
Coleoptera: Coccinellidae) in Turkey
Türk. entomol. bült, 2017, 7 (2): 113-118 ISSN 2146-975X DOI: http://dx.doi.org/10.16969/entoteb.331402 E-ISSN 2536-4928 Original article (Orijinal araştırma) First record of Anatis ocellata (Linnaeus, 1758) (Coleoptera: Coccinellidae) in Turkey Anatis ocellata (Linnaeus, 1758) (Coleoptera: Coccinellidae)’nın Türkiye’deki ilk kaydı Şükran OĞUZOĞLU1* Mustafa AVCI1 Derya ŞENAL2 İsmail KARACA3 Abstract Coccinellids sampled in this study were collected from the Taurus cedar (Cedrus libani A. Rich.) at Gölcük Natural Park in Isparta and Crimean pine (Pinus nigra Arnold.) in Bilecik Şeyh Edebali University Campus. Anatis ocellata (Linnaeus, 1758) was found among the collected coccinellids and is reported for the first time in Turkish coccinellid fauna, after the identification of samples. Morphological features and taxonomic characters of this species are given with distribution and habitat notes. Keywords: Anatis ocellata, Bilecik, coccinellid, Isparta, new record Öz Gelin böcekleri, Isparta’da Gölcük Tabiat Parkı’nda Toros sediri (Cedrus libani A. Rich.) ve Bilecik Şeyh Edebali Üniversitesi Kampüsü’nde karaçam (Pinus nigra Arnold.) üzerinden toplanmıştır. Teşhis sonucunda toplanan örnekler arasında Anatis ocellata’nın bulunduğu ve Türkiye gelin böcekleri faunası için yeni kayıt olduğu belirlenmiştir. Bu çalışmada türün morfolojik özellikleri ile taksonomik karakteristikleri, yayılış ve habitat notları verilmiştir. Anahtar sözcükler: Anatis ocellata, Bilecik, coccinellid, Isparta, yeni kayıt 1 Süleyman Demirel Üniversitesi, Orman Fakültesi, -
Green-Tree Retention and Controlled Burning in Restoration and Conservation of Beetle Diversity in Boreal Forests
Dissertationes Forestales 21 Green-tree retention and controlled burning in restoration and conservation of beetle diversity in boreal forests Esko Hyvärinen Faculty of Forestry University of Joensuu Academic dissertation To be presented, with the permission of the Faculty of Forestry of the University of Joensuu, for public criticism in auditorium C2 of the University of Joensuu, Yliopistonkatu 4, Joensuu, on 9th June 2006, at 12 o’clock noon. 2 Title: Green-tree retention and controlled burning in restoration and conservation of beetle diversity in boreal forests Author: Esko Hyvärinen Dissertationes Forestales 21 Supervisors: Prof. Jari Kouki, Faculty of Forestry, University of Joensuu, Finland Docent Petri Martikainen, Faculty of Forestry, University of Joensuu, Finland Pre-examiners: Docent Jyrki Muona, Finnish Museum of Natural History, Zoological Museum, University of Helsinki, Helsinki, Finland Docent Tomas Roslin, Department of Biological and Environmental Sciences, Division of Population Biology, University of Helsinki, Helsinki, Finland Opponent: Prof. Bengt Gunnar Jonsson, Department of Natural Sciences, Mid Sweden University, Sundsvall, Sweden ISSN 1795-7389 ISBN-13: 978-951-651-130-9 (PDF) ISBN-10: 951-651-130-9 (PDF) Paper copy printed: Joensuun yliopistopaino, 2006 Publishers: The Finnish Society of Forest Science Finnish Forest Research Institute Faculty of Agriculture and Forestry of the University of Helsinki Faculty of Forestry of the University of Joensuu Editorial Office: The Finnish Society of Forest Science Unioninkatu 40A, 00170 Helsinki, Finland http://www.metla.fi/dissertationes 3 Hyvärinen, Esko 2006. Green-tree retention and controlled burning in restoration and conservation of beetle diversity in boreal forests. University of Joensuu, Faculty of Forestry. ABSTRACT The main aim of this thesis was to demonstrate the effects of green-tree retention and controlled burning on beetles (Coleoptera) in order to provide information applicable to the restoration and conservation of beetle species diversity in boreal forests. -
DEFOLIATORS Insect Sections
Alaska. Reference is made to this map in selected DEFOLIATORS insect sections. (Precipitation information from Schwartz, F.K., and Miller, J.F. 1983. Probable maximum precipitation and snowmelt criteria for Fewer defoliator plots (27 plots) were visited during southeast Alaska: National Weather Service the 1999 aerial survey than in previous years (52 plots) Hydrometeorological Report No. 54. 115p. GIS layer throughout southeast Alaska. An effort was made to created by: Tim Brabets, 1997. distribute these plots evenly across the archipelago. URL:http://agdc.usgs.gov/data/usgs/water) The objectives during the 1999 season were to: ¨ Spend more time covering the landscape during Spruce Needle Aphid the aerial survey, Elatobium abietinum Walker ¨ Allow more time to land and identify unknown mortality and defoliation, and Spruce needle aphids feed on older needles of Sitka ¨ Avoid visit sites that were hard to get to and had spruce, often causing significant amounts of needle few western hemlocks. drop (defoliation). Defoliation by aphids cause reduced tree growth and can predispose the host to Hemlock sawfly and black-headed budworm larvae other mortality agents, such as the spruce beetle. counts were generally low in 1999 as they were in Severe cases of defoliation alone may result in tree 1998. The highest sawfly larvae counts were from the mortality. Spruce in urban settings and along marine plots in Thorne Bay and Kendrick Bay, Prince of shorelines are most seriously impacted. Spruce aphids Wales Island. Larval counts are used as a predictive feed primarily in the lower, innermost portions of tree tool for outbreaks of defoliators. For example, if the crowns, but may impact entire crowns during larval sample is substantially greater in 1999, then an outbreaks. -
Lepidoptera of North America 5
Lepidoptera of North America 5. Contributions to the Knowledge of Southern West Virginia Lepidoptera Contributions of the C.P. Gillette Museum of Arthropod Diversity Colorado State University Lepidoptera of North America 5. Contributions to the Knowledge of Southern West Virginia Lepidoptera by Valerio Albu, 1411 E. Sweetbriar Drive Fresno, CA 93720 and Eric Metzler, 1241 Kildale Square North Columbus, OH 43229 April 30, 2004 Contributions of the C.P. Gillette Museum of Arthropod Diversity Colorado State University Cover illustration: Blueberry Sphinx (Paonias astylus (Drury)], an eastern endemic. Photo by Valeriu Albu. ISBN 1084-8819 This publication and others in the series may be ordered from the C.P. Gillette Museum of Arthropod Diversity, Department of Bioagricultural Sciences and Pest Management Colorado State University, Fort Collins, CO 80523 Abstract A list of 1531 species ofLepidoptera is presented, collected over 15 years (1988 to 2002), in eleven southern West Virginia counties. A variety of collecting methods was used, including netting, light attracting, light trapping and pheromone trapping. The specimens were identified by the currently available pictorial sources and determination keys. Many were also sent to specialists for confirmation or identification. The majority of the data was from Kanawha County, reflecting the area of more intensive sampling effort by the senior author. This imbalance of data between Kanawha County and other counties should even out with further sampling of the area. Key Words: Appalachian Mountains, -
GIS Handbook Appendices
Aerial Survey GIS Handbook Appendix D Revised 11/19/2007 Appendix D Cooperating Agency Codes The following table lists the aerial survey cooperating agencies and codes to be used in the agency1, agency2, agency3 fields of the flown/not flown coverages. The contents of this list is available in digital form (.dbf) at the following website: http://www.fs.fed.us/foresthealth/publications/id/id_guidelines.html 28 Aerial Survey GIS Handbook Appendix D Revised 11/19/2007 Code Agency Name AFC Alabama Forestry Commission ADNR Alaska Department of Natural Resources AZFH Arizona Forest Health Program, University of Arizona AZS Arizona State Land Department ARFC Arkansas Forestry Commission CDF California Department of Forestry CSFS Colorado State Forest Service CTAES Connecticut Agricultural Experiment Station DEDA Delaware Department of Agriculture FDOF Florida Division of Forestry FTA Fort Apache Indian Reservation GFC Georgia Forestry Commission HOA Hopi Indian Reservation IDL Idaho Department of Lands INDNR Indiana Department of Natural Resources IADNR Iowa Department of Natural Resources KDF Kentucky Division of Forestry LDAF Louisiana Department of Agriculture and Forestry MEFS Maine Forest Service MDDA Maryland Department of Agriculture MADCR Massachusetts Department of Conservation and Recreation MIDNR Michigan Department of Natural Resources MNDNR Minnesota Department of Natural Resources MFC Mississippi Forestry Commission MODC Missouri Department of Conservation NAO Navajo Area Indian Reservation NDCNR Nevada Department of Conservation -
Biodiversity Climate Change Impacts Report Card Technical Paper 12. the Impact of Climate Change on Biological Phenology In
Sparks Pheno logy Biodiversity Report Card paper 12 2015 Biodiversity Climate Change impacts report card technical paper 12. The impact of climate change on biological phenology in the UK Tim Sparks1 & Humphrey Crick2 1 Faculty of Engineering and Computing, Coventry University, Priory Street, Coventry, CV1 5FB 2 Natural England, Eastbrook, Shaftesbury Road, Cambridge, CB2 8DR Email: [email protected]; [email protected] 1 Sparks Pheno logy Biodiversity Report Card paper 12 2015 Executive summary Phenology can be described as the study of the timing of recurring natural events. The UK has a long history of phenological recording, particularly of first and last dates, but systematic national recording schemes are able to provide information on the distributions of events. The majority of data concern spring phenology, autumn phenology is relatively under-recorded. The UK is not usually water-limited in spring and therefore the major driver of the timing of life cycles (phenology) in the UK is temperature [H]. Phenological responses to temperature vary between species [H] but climate change remains the major driver of changed phenology [M]. For some species, other factors may also be important, such as soil biota, nutrients and daylength [M]. Wherever data is collected the majority of evidence suggests that spring events have advanced [H]. Thus, data show advances in the timing of bird spring migration [H], short distance migrants responding more than long-distance migrants [H], of egg laying in birds [H], in the flowering and leafing of plants[H] (although annual species may be more responsive than perennial species [L]), in the emergence dates of various invertebrates (butterflies [H], moths [M], aphids [H], dragonflies [M], hoverflies [L], carabid beetles [M]), in the migration [M] and breeding [M] of amphibians, in the fruiting of spring fungi [M], in freshwater fish migration [L] and spawning [L], in freshwater plankton [M], in the breeding activity among ruminant mammals [L] and the questing behaviour of ticks [L]. -
Green Parties and Elections to the European Parliament, 1979–2019 Green Par Elections
Chapter 1 Green Parties and Elections, 1979–2019 Green parties and elections to the European Parliament, 1979–2019 Wolfgang Rüdig Introduction The history of green parties in Europe is closely intertwined with the history of elections to the European Parliament. When the first direct elections to the European Parliament took place in June 1979, the development of green parties in Europe was still in its infancy. Only in Belgium and the UK had green parties been formed that took part in these elections; but ecological lists, which were the pre- decessors of green parties, competed in other countries. Despite not winning representation, the German Greens were particularly influ- enced by the 1979 European elections. Five years later, most partic- ipating countries had seen the formation of national green parties, and the first Green MEPs from Belgium and Germany were elected. Green parties have been represented continuously in the European Parliament since 1984. Subsequent years saw Greens from many other countries joining their Belgian and German colleagues in the Euro- pean Parliament. European elections continued to be important for party formation in new EU member countries. In the 1980s it was the South European countries (Greece, Portugal and Spain), following 4 GREENS FOR A BETTER EUROPE their successful transition to democracies, that became members. Green parties did not have a strong role in their national party systems, and European elections became an important focus for party develop- ment. In the 1990s it was the turn of Austria, Finland and Sweden to join; green parties were already well established in all three nations and provided ongoing support for Greens in the European Parliament. -
Invasive Species in Europe: Ecology, Status and Policy
Loyola University Chicago Loyola eCommons Institute of Environmental Sustainability: Faculty Publications and Other Works Faculty Publications 2011 Invasive Species in Europe: Ecology, Status and Policy Reuben P. Keller Loyola University Chicago, [email protected] Juergen Geist Johnathan M. Jeschke Ingolf Kuhn Follow this and additional works at: https://ecommons.luc.edu/ies_facpubs Part of the Life Sciences Commons Recommended Citation Keller, R, J Geist, JM Jeschke, and I Kuhn. "Invasive Species in Europe: Ecology, Status and Policy." Environemtal Sciences Europe 23(23), 2011. This Article is brought to you for free and open access by the Faculty Publications at Loyola eCommons. It has been accepted for inclusion in Institute of Environmental Sustainability: Faculty Publications and Other Works by an authorized administrator of Loyola eCommons. For more information, please contact [email protected]. This work is licensed under a Creative Commons Attribution-Noncommercial-No Derivative Works 3.0 License. © Keller et al., 2011. Keller et al. Environmental Sciences Europe 2011, 23:23 http://www.enveurope.com/content/23/1/23 COMMENTARY Open Access Invasive species in Europe: ecology, status, and policy Reuben P Keller1*, Juergen Geist2†, Jonathan M Jeschke3† and Ingolf Kühn4† Abstract Globalization of trade and travel has facilitated the spread of non-native species across the earth. A proportion of these species become established and cause serious environmental, economic, and human health impacts. These species are referred to as invasive, and are now recognized as one of the major drivers of biodiversity change across the globe. As a long-time centre for trade, Europe has seen the introduction and subsequent establishment of at least several thousand non-native species. -
Balsam Woolly Aphid Predator Studies, British Columbia, 1959-1967
BALSAM WOOLLY APHID PREDATOR STUDIES, BRITISH COLUMBIA, 1959-1967 b, J. W. E. Ho..II, J. C. V. Holml and A. F. O.wlon FOREST RESEARCH LABORATORY VICTORIA, BRITISH COLUMBIA INFORMATION REPORT BC·X·23 ...... ..N .......,_u., .......t ,,",_.. FORESTRY BRANCH JULY, 1968 BAlBAM \l)()LLY APHID PllEDATOll STUDIES. BRITISH COLUYillIA, 1959-1967 by J. W. E. Harris, J. C. V. Holms and A. F. Dawson FOIlliST ru,;S~ARCH L\ BORA T'JRY VICTORIA, BRITISH COLl/llllIA INFtmhATIotJ fU,P\)HT dG-'<-2J D~PARrnENT OF FORESTRY AND RURAL D~\I];lJ)PHF.NT JOLY, 1968 BAlSMl WOOLLY APHID PREDATOR STUDIES, BRITISH COLUMBIA, 1959-1966 by J. w. E. Harris, J. C. V. Halms and A. F. Dawson1/ INTRODUCTION The balsam woolly aphid Adelges pleate (Ratzburg) (Homoptera: Adelgidae), is an important pest of true firs Abies species) in British Columbia where it was first found in 1958, near Vancouver. It was intro duced to North America from Europe early in the century, and has since spread or been re-introduced to the ~~ritirne Provinces and Quebec, the northeastern United States as far south as North Carolina, northern California, Oregon and 'hashington. On the mainland amabills fir (Abies amabilis (DougL) Forb.) is the principal infested species. Compared with other native true firs it is moderate~ susceptible to attack but because most infestation has occurred in mature and Qvermature stands, mortality has been heavy. The pest is found at Salmon Inlet and Howe Sound, in the mountains north of Vancouver, the Indian River Valley and the Lower Fraser River Valley east to the Harrison River drainage. -
Spruce Spider Mite Oligonychus Ununguis Order Acari, Family Tetranychidae; Spider Mites Native Pest
Pests of Trees and Shrubs Spruce spider mite Oligonychus ununguis Order Acari, Family Tetranychidae; spider mites Native pest Host plants: Blue spruce, Norway, and white spruce are preferred, but arborvitae, cedar, cryptomeria, dawn redwood, Douglas-fir, hemlock, juniper, larch, and pine, are also susceptible. Description: Adult mites are approximately 0.5 mm long with eight legs. They are dark green when young but turn darker green as they mature. Protonymphs are smaller and lighter. Eggs are reddish-orange and oval to circular. Life history: This is a cold tolerant spider mite not active in hot summer temperatures. Eggs hatch in April and May. Feeding damage may be first observed after feeding started. Activity eases in summer with the arrival of 90 degree F temperatures and resumes with cooler weather in fall. There are several generations a year. Overwintering: Eggs on bark and needles. Damage to blue spruce in June caused by spruce spider mite; Damage symptoms: Mite feeding causes color changes note discoloration on the older needles. (234) in needles, giving them first a mottled appearance, then Photo: Cliff Sadof turning needles yellow and finally bronze. Damaged needles may drop prematurely. Severe infestations can cause loss of foliage, twig dieback, even branch dieback. Host trees may be killed, if extremely heavy infestations occur when they are stressed. Monitoring: Eggs hatch when PJM rhododendron blooms in mid April (Herms). Look for fine stippling turning into bronzing of needles beginning in June. To confirm mite presence, hold a sheet of white paper under a branch and tap the branch to dislodge mites. -
How Will Aphids Respond to More Frequent Drought?
bioRxiv preprint doi: https://doi.org/10.1101/2020.06.24.168112; this version posted December 10, 2020. The copyright holder for this preprint (which was not certified by peer review) is the author/funder, who has granted bioRxiv a license to display the preprint in perpetuity. It is made available under aCC-BY-NC 4.0 International license. 1 1 Stressful times in a climate crisis: how will aphids respond to more 2 frequent drought? 3 Running title: Aphid-plant interactions under drought stress 4 Abstract 5 Aim 6 Aphids are abundant in natural and managed vegetation, supporting a diverse 7 community of organisms and causing damage to agricultural crops. Using a meta- 8 analysis approach, we aimed to advance understanding of how increased drought 9 incidence will affect this ecologically and economically important insect group, and to 10 characterise the underlying mechanisms. 11 Location 12 Global. 13 Time period 14 1958–2020. 15 Major taxa studied 16 Aphids. 17 Methods 18 We used qualitative and quantitative synthesis techniques to determine whether 19 drought stress has a negative, positive, or null effect on aphid fitness. We examined 20 these effects in relation to 1) aphid biology, 2) the aphid-plant. species combination. 21 We compiled two datasets: 1) a “global” dataset (n = 55 from 55 published studies) 22 comprising one pooled effect size per study, and 2) an “expanded” dataset (n = 93) 23 containing multiple datapoints per study, separated into different measures of aphid 24 fitness but pooled across aphid-plant combinations. Where reported, we extracted 25 data on the effect of drought on plant vigour, and plant tissue concentrations of 26 nutrients and defensive compounds, to capture the potential causes of aphid 27 responses.