Biodiversity Assessment: Moving Towards an Evidence-Based
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ELYTRON, 2002. VOL. 16: 00-00 ISSN: 0214-1353 89 DESCRIPTION O A NEW SPECIES O ATHOUS AND RECORD O THE EMALE O A. AZORICUS PLATIA & GUDENZI ROM THE AZORES (COLEOPTERA: ELATERIDAE)1 Giuseppe Platia Via Molino Vecchio, 21 47030 GATTEO (C). ITALY [email protected] Paulo A. V. Borges Univ.dos Açores, Dep. Ciências Agrárias, CITA-A, 9700-851 ANGRA DO HEROÍSMO. TERCEIRA. AÇORES Unidade de Macroecologia e Conservação (UMC), Univ. de Évora, ábrica dos Leões 7000-730 ÉVORA. PORTUGAL [email protected] ABSTRACT Description of a new species of Athous and record of the female of A. azoricus Platia & Gudenzi from the Azores (Coleoptera: Elateridae) Athous (Orthathous) pomboi n. sp. is described from the Santa Maria Island. It is the second species of this genus known from the Azorean Archipelago. The distinctive characters of the female of A. azoricus are given. Key words: Coleoptera, Elateridae, new species, Athous, Azores. INTRODUCTION The Azores, an archipelago of nine islands located in the North Atlantic, is not particularly rich in endemic beetles and other arthropods when compared with the other Macaronesian archipelagoes of Madeira and Canaries (BORGES, 1992). However, after a recent intensive survey of 15 Natural orest Reserves and other Azorean reserves (BALA «Biodiversity of Arthropods of the Laurisilva of the Azores» 1998-2002, see BORGES et al. 2000) several new arthropod taxa was discovered including some beetles (see BLAS & BORGES, 1999; BORGES et al., 1 This is the article number 11 of the Project BALA (see (http://www.nrel.colostate.edu/IBOY/ europe_ap.html#BALA) 90 G. PLATIA & P. -
ED45E Rare and Scarce Species Hierarchy.Pdf
104 Species 55 Mollusc 8 Mollusc 334 Species 181 Mollusc 28 Mollusc 44 Species 23 Vascular Plant 14 Flowering Plant 45 Species 23 Vascular Plant 14 Flowering Plant 269 Species 149 Vascular Plant 84 Flowering Plant 13 Species 7 Mollusc 1 Mollusc 42 Species 21 Mollusc 2 Mollusc 43 Species 22 Mollusc 3 Mollusc 59 Species 30 Mollusc 4 Mollusc 59 Species 31 Mollusc 5 Mollusc 68 Species 36 Mollusc 6 Mollusc 81 Species 43 Mollusc 7 Mollusc 105 Species 56 Mollusc 9 Mollusc 117 Species 63 Mollusc 10 Mollusc 118 Species 64 Mollusc 11 Mollusc 119 Species 65 Mollusc 12 Mollusc 124 Species 68 Mollusc 13 Mollusc 125 Species 69 Mollusc 14 Mollusc 145 Species 81 Mollusc 15 Mollusc 150 Species 84 Mollusc 16 Mollusc 151 Species 85 Mollusc 17 Mollusc 152 Species 86 Mollusc 18 Mollusc 158 Species 90 Mollusc 19 Mollusc 184 Species 105 Mollusc 20 Mollusc 185 Species 106 Mollusc 21 Mollusc 186 Species 107 Mollusc 22 Mollusc 191 Species 110 Mollusc 23 Mollusc 245 Species 136 Mollusc 24 Mollusc 267 Species 148 Mollusc 25 Mollusc 270 Species 150 Mollusc 26 Mollusc 333 Species 180 Mollusc 27 Mollusc 347 Species 189 Mollusc 29 Mollusc 349 Species 191 Mollusc 30 Mollusc 365 Species 196 Mollusc 31 Mollusc 376 Species 203 Mollusc 32 Mollusc 377 Species 204 Mollusc 33 Mollusc 378 Species 205 Mollusc 34 Mollusc 379 Species 206 Mollusc 35 Mollusc 404 Species 221 Mollusc 36 Mollusc 414 Species 228 Mollusc 37 Mollusc 415 Species 229 Mollusc 38 Mollusc 416 Species 230 Mollusc 39 Mollusc 417 Species 231 Mollusc 40 Mollusc 418 Species 232 Mollusc 41 Mollusc 419 Species 233 -
Lessons from Genome Skimming of Arthropod-Preserving Ethanol Benjamin Linard, P
View metadata, citation and similar papers at core.ac.uk brought to you by CORE provided by Archive Ouverte en Sciences de l'Information et de la Communication Lessons from genome skimming of arthropod-preserving ethanol Benjamin Linard, P. Arribas, C. Andújar, A. Crampton-Platt, A. P. Vogler To cite this version: Benjamin Linard, P. Arribas, C. Andújar, A. Crampton-Platt, A. P. Vogler. Lessons from genome skimming of arthropod-preserving ethanol. Molecular Ecology Resources, Wiley/Blackwell, 2016, 16 (6), pp.1365-1377. 10.1111/1755-0998.12539. hal-01636888 HAL Id: hal-01636888 https://hal.archives-ouvertes.fr/hal-01636888 Submitted on 17 Jan 2019 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. 1 Lessons from genome skimming of arthropod-preserving 2 ethanol 3 Linard B.*1,4, Arribas P.*1,2,5, Andújar C.1,2, Crampton-Platt A.1,3, Vogler A.P. 1,2 4 5 1 Department of Life Sciences, Natural History Museum, Cromwell Road, London SW7 6 5BD, UK, 7 2 Department of Life Sciences, Imperial College London, Silwood Park Campus, Ascot 8 SL5 7PY, UK, 9 3 Department -
Diplomarbeit
DIPLOMARBEIT Carabid assemblages of various forest communities of the National Park Thayatal (northern part), Lower Austria angestrebter akademischer Grad Magister der Naturwissenschaften (Mag. rer.nat.) Verfasser: Wolfgang Prunner Matrikel-Nummer: 0009403 Studienrichtung /Studienzweig Zoologie (lt. Studienblatt): Betreuer: Ao. Univ.-Prof. Dr. Wolfgang Waitzbauer Wien, im Juni 2009 Summary The study took place in the Nationalpark “Thayatal-Podyjí” (northern Lower Austria) on seven sites from April to October 2005 and additionally on two different sites from April to October 2006. The carabid assemblages of this different sampling sites, which vary in their geology and forest type, were examined by using pitfall traps. Carabids were suitable bioindicators for this study because they are easy to trap and their ecological preferences are well known. The carabid assemblages were characterised by composition of wing morphology types, body sizes and ecological valences and by three ecological parameters which were Shannon Index, Eveness, and Forest Affinity Index (FAI). In total 17 different species were identified and the species number varied from 1 to 10 among the sites. Aptinus bombarda was the most abundant species but could only be found at two sites followed by Abax parallelepipedus, Abax ovalis and Molops piceus. Abax paralellepipedus was the most wide spread species and appeared at six sites. In total more than 80 % of all registrated species were brachypterous, 30 % were stenoecious and 70 % were body size category IV and V which means that large species were in the majority. The Shannon Index was highest with 2.01 at the very well structured oaktree mixed forest MXG3, and the FAI Index showed its highest value at the oaktree hornbeam forest ES and at the beechwood forest MXG2 with 0.98 each. -
Local Development Framework Committee Committee
Local Development Framework Committee Town Hall, Colchester 28 September 2009 at 6.00pm The Local Development Framework Committee deals with the Council's responsibilities relating to the Local Development Framework. Information for Members of the Public Access to information and meetings You have the right to attend all meetings of the Council, its Committees and Cabinet. You also have the right to see the agenda, which is usually published 5 working days before the meeting, and minutes once they are published. Dates of the meetings are available at www.colchester.gov.uk or from Democratic Services. Have Your Say! The Council values contributions from members of the public. Under the Council's Have Your Say! policy you can ask questions or express a view to meetings, with the exception of Standards Committee meetings. If you wish to speak at a meeting or wish to find out more, please pick up the leaflet called “Have Your Say” at Council offices and at www.colchester.gov.uk Private Sessions Occasionally meetings will need to discuss issues in private. This can only happen on a limited range of issues, which are set by law. When a committee does so, you will be asked to leave the meeting. Mobile phones, pagers, cameras, audio recorders Please ensure that all mobile phones and pagers are turned off before the meeting begins and note that photography or audio recording is not permitted. Access There is wheelchair access to the Town Hall from St Runwald Street. There is an induction loop in all the meeting rooms. If you need help with reading or understanding this document please take it to Angel Court Council offices, High Street, Colchester or telephone (01206) 282222 or textphone 18001 followed by the full number that you wish to call and we will try to provide a reading service, translation or other formats you may need. -
Coleoptera: Carabidae
ZOBODAT - www.zobodat.at Zoologisch-Botanische Datenbank/Zoological-Botanical Database Digitale Literatur/Digital Literature Zeitschrift/Journal: Acta Entomologica Slovenica Jahr/Year: 2004 Band/Volume: 12 Autor(en)/Author(s): Polak Slavko Artikel/Article: Cenoses and species phenology of Carabid beetles (Coleoptera: Carabidae) in three stages of vegetational successions on upper Pivka karst (SW Slovenia) Cenoze in fenologija vrst kresicev (Coleoptera: Carabidae) v treh stadijih zarazcanja krasa na zgornji Pivki (JZ Slovenija) 57-72 ©Slovenian Entomological Society, download unter www.biologiezentrum.at LJUBLJANA, JUNE 2004 Vol. 12, No. 1: 57-72 XVII. SIEEC, Radenci, 2001 CENOSES AND SPECIES PHENOLOGY OF CARABID BEETLES (COLEOPTERA: CARABIDAE) IN THREE STAGES OF VEGETATIONAL SUCCESSION IN UPPER PIVKA KARST (SW SLOVENIA) Slavko POLAK Notranjski muzej Postojna, Ljubljanska 10, SI-6230 Postojna, Slovenia, e-mail: [email protected] Abstract - The Carabid beetle cenoses in three stages of vegetational succession in selected karst area were studied. Year-round phenology of all species present is pre sented. Species richness of the habitats, total number of individuals trapped and the nature conservation aspects of the vegetational succession of the karst grasslands are discussed. K e y w o r d s : Coleoptera, Carabidae, cenose, phenology, vegetational succession, karst Izvleček CENOZE IN FENOLOGIJA VRST KREŠIČEV (COLEOPTERA: CARABIDAE) V TREH STADIJIH ZARAŠČANJA KRASA NA ZGORNJI PIVKI (JZ SLOVENIJA) Raziskali smo cenoze hroščev krešičev -
The Antinociceptive Effects of Hydroalcoholic Extract of Bryonia
Avicenna J Neuro Psych Physio. 2015 February; 2(1): e25761. DOI: 10.17795/ajnpp-25761 Published online 2015 February 20. Research Article The Antinociceptive Effects of Hydroalcoholic Extract ofBryonia dioica in Male Rats Mohammad Zarei 1,2; Saeed Mohammadi 3,*; Nasreen Abolhassani 4; Mahtab Asgari Nematian 5 1Neurophysiology Research Center, Hamadan University of Medical Sciences, Hamadan, IR Iran 2Department of Physiology, Hamadan University of Medical Sciences, Hamadan, IR Iran 3Department of Biology, Faculty of Basic Sciences, Islamic Azad University, Hamadan, IR Iran 4Department of Biology, Faculty of Basic Sciences, Science and Research Branch, Islamic Azad University, Tehran, IR Iran 5Department of Biology, Hamadan Branch, Payam-noor University, Hamadan, IR Iran *Corresponding author: Saeed Mohammadi, Professor Mussivand Blvd, Hamadan Branch, Islamic Azad University, Hamadan, IR Iran. Tel: +98-8134494000, Fax: +98-8134494026, E-mail: [email protected] Received: December 1, 2014; Revised: January 2, 2015; Accepted: January 8, 2015 Background: Side effects of synthetic analgesic drugs in the clinical practice have drawn researchers’ attention on developing the herbal medicine as more appropriate analgesic agents. Objectives: This study aimed to investigate the antinociceptive effect of hydroalcoholic leaf extract of Bryonia dioica (HEBD) on male rats. Materials and Methods: In this experimental study, 42 adult male rats were divided into 7 groups: control, HEBD (80, 100, and 300 mg/ kg, ip), morphine (1 mg/kg, ip), indomethacin (1 mg/kg, ip), and naloxone (1 mg/kg ip). In order to assess the analgesic effects of the extract, writhing, tail-flick, and formalin tests were used. Also, Tukey post hoc and 1-way analysis of variance (ANOVA) tests were used to analyze the data. -
Colchester Borough Local Plan 2017 – 2033
Publication Draft The Publication Draft stage of the Colchester Borough Local Plan 2017 – 2033 June 2017 CONTENTS Introduction ................................................................................................................ 1 Local Plan: The Process ......................................................................................... 1 National planning guidance ................................................................................. 1 County Level Plans ............................................................................................. 2 Borough Strategies ............................................................................................. 3 Duty to Co-operate .............................................................................................. 3 Evidence Base .................................................................................................... 4 Sustainability Appraisal ....................................................................................... 4 Habitat Regulations Assessment ........................................................................ 5 Local Plan: Structure of the Plan and other related documents .............................. 5 Other Colchester Planning Documents ................................................................... 6 How to respond....................................................................................................... 7 What Happens Next? ............................................................................................. -
(Coleoptera: Carabidae) and Habitat Fragmentation
REVIEW Eur. J.Entomol. 98: 127-132, 2001 ISSN 1210-5759 Carabid beetles (Coleóptera: Carabidae) and habitat fragmentation: a review Ja r i NIEMELÁ Department ofEcology and Systematics, PO Box 17, FIN-00014 University ofHelsinki, Finland e-mail:[email protected] Key words. Carabids, conservation, dispersal, forests, habitat fragmentation, habitat heterogeneity, metapopulations, species richness, generalists, specialists Abstract. I review the effects of habitat fragmentation on carabid beetles (Coleoptera, Carabidae) and examine whether the taxon could be used as an indicator of fragmentation. Related to this, I study the conservation needs of carabids. The reviewed studies showed that habitat fragmentation affects carabid assemblages. Many species that require habitat types found in interiors of frag ments are threatened by fragmentation. On the other hand, the species composition of small fragments of habitat (up to a few hec tares) is often altered by species invading from the surroundings. Recommendations for mitigating these adverse effects include maintenance of large habitat patches and connections between them. Furthermore, landscape homogenisation should be avoided by maintaining heterogeneity ofhabitat types. It appears that at least in the Northern Hemisphere there is enough data about carabids for them to be fruitfully used to signal changes in land use practices. Many carabid species have been classified as threatened. Mainte nance of the red-listed carabids in the landscape requires species-specific or assemblage-specific measures. INTRODUCTION HABITAT FRAGMENTATION AND CARABID ASSEMBLAGES Destruction and fragmentation of habitats, overkill, introduction of alien species, and cascading effects of Effects of fragmentation on carabid assemblages species extinctions have been labelled the “evil quartet”, Habitat fragmentation is the partitioning of a con i.e. -
Supplementary Materials To
Supplementary Materials to The permeability of natural versus anthropogenic forest edges modulates the abundance of ground beetles of different dispersal power and habitat affinity Tibor Magura 1,* and Gábor L. Lövei 2 1 Department of Ecology, University of Debrecen, Debrecen, Hungary; [email protected] 2 Department of Agroecology, Aarhus University, Flakkebjerg Research Centre, Slagelse, Denmark; [email protected] * Correspondence: [email protected] Diversity 2020, 12, 320; doi:10.3390/d12090320 www.mdpi.com/journal/diversity Table S1. Studies used in the meta-analyses. Edge type Human Country Study* disturbance Anthropogenic agriculture China Yu et al. 2007 Anthropogenic agriculture Japan Kagawa & Maeto 2014 Anthropogenic agriculture Poland Sklodowski 1999 Anthropogenic agriculture Spain Taboada et al. 2004 Anthropogenic agriculture UK Bedford & Usher 1994 Anthropogenic forestry Canada Lemieux & Lindgren 2004 Anthropogenic forestry Canada Spence et al. 1996 Anthropogenic forestry USA Halaj et al. 2008 Anthropogenic forestry USA Ulyshen et al. 2006 Anthropogenic urbanization Belgium Gaublomme et al. 2008 Anthropogenic urbanization Belgium Gaublomme et al. 2013 Anthropogenic urbanization USA Silverman et al. 2008 Natural none Hungary Elek & Tóthmérész 2010 Natural none Hungary Magura 2002 Natural none Hungary Magura & Tóthmérész 1997 Natural none Hungary Magura & Tóthmérész 1998 Natural none Hungary Magura et al. 2000 Natural none Hungary Magura et al. 2001 Natural none Hungary Magura et al. 2002 Natural none Hungary Molnár et al. 2001 Natural none Hungary Tóthmérész et al. 2014 Natural none Italy Lacasella et al. 2015 Natural none Romania Máthé 2006 * See for references in Table S2. Table S2. Ground beetle species included into the meta-analyses, their dispersal power and habitat affinity, and the papers from which their abundances were extracted. -
Edge Effect on Carabid Assemblages Along Forest-Grass Transects
Web Ecology 2: 7–13. Edge effect on carabid assemblages along forest-grass transects T. Magura, B. Tóthmérész and T. Molnár Magura, T., Tóthmérész, B. and Molnár, T. 2001. Edge effect on carabid assemblages along forest-grass transects. – Web Ecol. 2: 7–13. During 1997 and 1998, we have tested the edge-effect for carabids along oak-hornbeam forest-grass transects using pitfall traps in Hungary. Our hypothesis was that the diver- sity of carabids will be higher in the forest edge than in the forest interior. We also focused on the characteristic species of the habitats along the transects and the relation- ships between their distribution and the biotic and abiotic factors. Our results proved that there was a significant edge effect on the studied carabid com- munities: the Shannon diversity increased significantly along the transects from the forest towards the grass. The diversity of the carabids were significantly higher in the forest edge and in the grass than in the forest interior. The carabids of the forest, the forest edge and the grass are separated from each other by principal coordinates analysis and by indicator species analysis (IndVal), suggesting that each of the three habitats has a distinct species assemblages. There were 5 distinctive groups of carabids: 1) habitat generalists, 2) forest generalists, 3) species of the open area, 4) forest edge species, and 5) forest specialists. It was demonstrated by multiple regression analyses, that the relative air moisture, temperature of the ground, the cover of leaf litter, herbs, shrubs and cano- py cover, abundance of the carabids’ preys are the most important factors determining the diversity and spatial pattern of carabids along the studied transects. -
Appendix O19749
Oikos o19749 Gerisch, M., Agostinelli, V., Henle, K. and Dziock, F. 2011. More species, but all do the same: contrasting effects of flood disturbance on ground beetle functional and species diversity. – Oikos 121: 508–515. Appendix A1 Tabelle1 Table A1. Full species list representing the standardized number of individuals per species for the study sites Steckby, Woerlitz, and Sandau. Density expresses the proportion of species standardized abundances to total abundance. Macropterous = winged, brachypterous = wingless, dimorphic = both forms can appear with a species. Body size is the average of maximum and minimum values found in the literature (for references see below). Wing Reproduction Body size Species names Steckby Woerlitz Sandau Density Morphology Season In mm Acupalpus dubius 0.032 0 0.016 0 macropterous spring 2.6 Acupalpus exiguus 1.838 1.019 0.71 0.005 macropterous spring 2.7 Acupalpus parvulus 0.081 0.038 0.032 0 macropterous spring 3.6 Agonum dolens 0.032 0.038 0.081 0 dimorph spring 8.8 Agonum duftschmidi 14.966 2.755 0.016 0.025 macropterous spring 8.2 Agonum emarginatum 116.659 4.472 25.194 0.208 macropterous spring 7.2 Agonum fuliginosum 0.097 0.038 0 0 dimorph spring 6.7 Agonum lugens 0.177 0 0.081 0 macropterous spring 9 Agonum marginatum 0.371 0.075 0.113 0.001 macropterous spring 9.2 Agonum micans 19.502 4.208 23.71 0.067 macropterous spring 6.6 Agonum muelleri 0 0.019 0 0 macropterous spring 8.2 Agonum piceum 0.468 0 0.016 0.001 macropterous spring 6.4 Agonum sexpunctatum 0.032 0 0.016 0 macropterous spring 8.2 Agonum