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Commune de Moigny-sur-Ecole Plan Local d’Urbanisme 1.3 Annexes du rapport de Présentation Dossier arrêté en Conseil municipal le : Mise à l’Enquête publique : Dossier approuvé en Conseil municipal le : Du 10 mars 2017 au 10 avril 2017 6 juin 2017 27 septembre 2016 SOMMAIRE 1. Annexe I – Inventaire des espèces végétales……………………………………………………………………………………3 2. Annexe II – Inventaire des espèces animales……………………………………………………………………………………19 Annexe I - Espèces végétales Liste rouge Rareté Dernière obs. Taxon de référence Nom vernaculaire Protection ZNIEFF ECOGEE rég. Essonne FLORA Acer campestre L. Érable champêtre TC 2012 2007 Acer platanoides L. Érable plane TC 2001 Acer pseudoplatanus L. Érable sycomore TC 2012 2015 Achillea millefolium L. Achillée millefeuille TC 2012 2016 Agrimonia eupatoria L. Aigremoine TC 2012 2016 Agrostis canina L. Agrostide des chiens AC 2000 Agrostis capillaris L. Agrostide capillaire TC 2012 Agrostis stolonifera L. Agrostide stolonifère TC 2001 Ailanthus altissima (Mill.) Swingle Faux-vernis du Japon AC 2001 Aira caryophyllea L. Canche caryophillée AC 2012 Aira praecox L. Canche printanière AC 2012 Ajuga chamaepytis (L.) Schreb. Bugle petit-pin AC 2007 Ajuga genevensis L. Bugle de Genève AC 2012 Ajuga reptans L. Bugle rampante TC 2010 2007 Alliaria petiolata (M.Bieb.) Cavara & Grande Alliaire TC 1997 2015 Allium sphaerocephalon L. Ail à tête ronde AR 2012 2015 Allium vineale L. Ail des vignes C 1997 Alnus glutinosa (L.) Gaertn. Aulne glutineux TC 2011 2007 Amaranthus hybridus L. Amarante hybride TC 2001 Ambrosia artemisiifolia L. Ambroise élevée R 2008 Amelanchier ovalis Medik. Amélanchier PR oui AR 2012 Anacamptis morio (L.) R.M.Bateman Orchis bouffon VU oui AC 2000 Anemone nemorosa L. Anémone des bois C 2000 Anemone pulsatilla L. Pulsatille vulgaire 2012 2007 Angelica sylvestris L. Angélique sauvage TC 2011 2015 Anisantha sterilis (L.) Nevski Brome stérile TC 2001 2016 Anisantha tectorum (L.) Nevski Brome des toits AC 1997 Anthoxanthum odoratum L. Flouve odorante TC 2012 2007 Anthriscus sylvestris (L.) Hoffm. Cerfeuil des bois TC 2000 Anthyllis vulneraria L. Anthyllide vulnéraire AC 1997 Aphanes arvensis L. Alchémille des champs C 2000 Aphanes australis Rydb. Alchémille oubliée AR 1997 Arabidopsis thaliana (L.) Heynh. Arabette de thalius TC 2012 Arabis hirsuta (L.) Scop. Arabette poilue AC 2012 Arctium lappa L. Grande bardane TC 2011 Arctium minus (Hill) Bernh. Bardane à petites têtes TC 2001 Arenaria leptoclados (Rchb.) Guss. Sabline à parois fines AC 2000 Arenaria serpyllifolia L. Sabline à feuilles de serpolet TC 2012 2016 1/15 Annexe I - Espèces végétales Liste rouge Rareté Dernière obs. Taxon de référence Nom vernaculaire Protection ZNIEFF ECOGEE rég. Essonne FLORA Argentina anserina (L.) Rydb. Potentille des oies 2001 Aristolochia clematitis L. Aristoloche clématite AR 2013 Armeria arenaria (Pers.) Schult. Armérie faux-plantain AR 2012 Arrhenatherum elatius (L.) P.Beauv. ex J.Presl & C.Presl Fromental élevé TC 2001 2016 Artemisia annua L. Armoise annuelle AR 2001 Artemisia vulgaris L. Armoise commune TC 2012 2016 Artemisia verlotiorum Lamotte Armoise de Chine R 2016 Arum italicum Mill. Gouet d'Italie C 2008 Arum maculatum L. Gouet tâcheté TC 2003 2007 Asplenium adiantum-nigrum L. Doradille noire AC 2012 Asplenium ceterach L. Cétérach 2012 Asplenium scolopendrium L. Scolopendre 2000 2015 Asplenium trichomanes L. Capillaire des murailles TC 2012 Athyrium filix-femina (L.) Roth Fougère femelle AC 2007 Atropa belladonna L. Belladone EN R 2012 Avenella flexuosa (L.) Drejer Foin tortueux 2012 Avenula pubescens (Huds.) Dumort. Avoine pubescente 1993 Barbarea vulgaris R.Br. Barbarée commune C 2011 Bellis perennis L. Pâquerette TC 2012 2016 Betonica officinalis L. Épiaire officinale 2012 Betula pendula Roth Bouleau verruqueux TC 2012 2007 Betula pubescens Ehrh. Bouleau blanc C 1997 Blackstonia perfoliata (L.) Huds. Chlorette AC 2000 2007 Brachypodium pinnatum (L.) P.Beauv. Brachypode penné TC 2012 Brachypodium sylvaticum (Huds.) P.Beauv. Brachypode des bois TC 2012 Bromus hordeaceus L. Brome mou TC 2016 Bryonia cretica L. 2012 Bupleurum falcatum L. Buplèvre en faux C 2000 Calamagrostis epigejos (L.) Roth Calamagrostide épigéios C 2012 Callitriche brutia Petagna Callitriche pédonculé R 2012 Callitriche obtusangula Le Gall Callitriche à angles obtus R 2011 Calluna vulgaris (L.) Hull Callune C 2012 2015 Caltha palustris L. Populage des marais AC 2011 2007 Calystegia sepium (L.) R.Br. Liseron des haies TC 2009 Campanula rapunculus L. Campanule raiponce TC 2012 2016 Capsella bursa-pastoris (L.) Medik. Capselle bourse-à-pasteur TC 2001 Cardamine amara L. Cardamine amère AR 2000 Cardamine hirsuta L. Cardamine hérissée TC 2000 2/15 Annexe I - Espèces végétales Liste rouge Rareté Dernière obs. Taxon de référence Nom vernaculaire Protection ZNIEFF ECOGEE rég. Essonne FLORA Cardamine pratensis L. Cardamine des prés C 2000 Carex acutiformis Ehrh. Laîche des marais C 2011 Carex caryophyllea Latourr. Laîche printanière AC 2012 Carex divulsa Stokes Laîche écartée C 2012 Carex flacca Schreb. Laîche glauque TC 2012 2007 Carex halleriana Asso Laîche de Haller PR oui AC 2000 Carex hirta L. Laîche hérissée TC 2001 2015 Carex humilis Leyss. Laîche humble AR 1925 Carex paniculata L. Laîche paniculée AC 2011 Carex pendula Huds. Laîche à épis pendants AC 2009 2015 Carex pilulifera L. Laîche à pilules C 2012 Carex riparia Curtis Laîche des rives C 2011 Carex spicata Huds, Laîche en épis AC 2016 Carex sylvatica Huds. Laîche des bois TC 2000 Carpinus betulus L. Charme TC 2012 2007 Castanea sativa Mill. Chataignier TC 2012 2015 Catapodium rigidum (L.) C.E.Hubb. Pâturin rigide C 1993 Centaurea scabiosa L. Centaurée scabieuse C 2000 Centaurium erythraea Rafn Petite centaurée commune TC 2000 2015 Cephalanthera damasonium (Mill.) Druce Céphalanthère à grandes fleurs C 1991 Cephalanthera rubra (L.) Rich. Céphalanthère rouge PR EN oui NR 2009 Cerastium brachypetalum Desp. ex Pers. Céraiste à pétales courts AC 2000 Cerastium fontanum Baumg. Céraiste commune TC 2012 Cerastium glomeratum Thuill. Céraiste aggloméré TC 2012 Cerastium semidecandrum L. Céraiste à 5 étamines C 2012 Cervaria rivini Gaertn. Peucédan Herbe aux cerfs PR VU oui AR 2000 2015 Chaerophyllum temulum L. Chérophylle penché TC 2012 Chelidonium majus L. Grande chélidoine TC 2001 2016 Chenopodium album L. Chénopode blanc TC 2001 Cirsium arvense (L.) Scop. Cirse des champs TC 2001 2016 Cirsium oleraceum (L.) Scop. Cirse des maraicher C 2011 Cirsium palustre (L.) Scop. Cirse des marais TC 2011 Cirsium vulgare (Savi) Ten. Cirse commun TC 2009 2016 Cladanthus mixtus (L.) Chevall. Anthémis panaché CR oui 2011 Clematis vitalba L. Clématite des haies TC 2012 2016 Clinopodium acinos (L.) Kuntze Calament acinos 2012 Clinopodium nepeta (L.) Kuntze Calament glanduleux 2010 Clinopodium vulgare L. Sariette commune TC 2012 3/15 Annexe I - Espèces végétales Liste rouge Rareté Dernière obs. Taxon de référence Nom vernaculaire Protection ZNIEFF ECOGEE rég. Essonne FLORA Convallaria majalis L. Muguet C 2012 Convolvulus arvensis L. Liseron des champs TC 2001 2016 Cornus mas L. Cornouiller mâle AC 2010 Cornus sanguinea L. Cornouiller sanguin TC 2012 2007 Coronilla minima L. Coronille naine AC 1925 Coronilla varia L. Coronille changeante 2012 Corylus avellana L. Noisetier TC 2012 2007 Corynephorus canescens (L.) P.Beauv. Corynéphore blanchâtre AR 2010 Crassula vaillantii (Willd.) Roth Bulliarde de Vaillant PR CR oui R 1945 Crataegus germanica (L.) Kuntze Néflier commun C 2012 2007 Crataegus laevigata (Poir.) DC. Aubépine à deux styles C 2012 Crataegus monogyna Jacq. Aubépine à un style TC 2012 2007 Crepis capillaris (L.) Wallr. Crépide capillaire TC 2012 Crepis setosa Haller f. Crépide hérissée TC 2001 Cymbalaria muralis P.Gaertn. Cymbalaire TC 2000 2015 Cynodon dactylon (L.) Pers. Cynodon dactyle AC 2011 Cynosurus cristatus L. Cynosure crételle AR 2012 Cytisus scoparius (L.) Link Genêt à balai TC 2012 2007 Dactylis glomerata L. Dactyle aggloméré TC 2012 2016 Danthonia decumbens (L.) DC. Danthonie AC 2012 2007 Daphne laureola L. Daphné lauréole C 2000 2007 Daucus carota L. Carotte sauvage TC 2008 2016 Dianthus armeria L. Œillet velu AC 2015 Dianthus carthusianorum L. Oeillet des chartreux AC 2012 2015 Dioscorea communis (L.) Caddick & Wilkin Sceau de Notre Dame 2012 2007 Dipsacus fullonum L. Cabaret des oiseaux TC 2001 Draba verna L. Drave de printemps 2010 Dryopteris affinis (Lowe) Fraser-Jenk. Dryoptéris écailleux oui R 2009 Dryopteris carthusiana (Vill.) H.P.Fuchs Dryoptéris des chartreux TC 2012 Dryopteris dilatata (Hoffm.) A.Gray Dryoptéris dilaté C 2012 Dryopteris filix-mas (L.) Schott Fougère mâle TC 2012 2007 Echinochloa crus-galli (L.) P.Beauv. Échinochloé Pied-de-coq TC 2001 Elodea canadensis Michx. Élodée du Canada AR 2011 2015 Elytrigia repens (L.) Desv. ex Nevski Chiendent commun TC 2011 Epilobium hirsutum L. Épilobe hérissé TC 2011 2015 Epipactis atrorubens (Hoffm.) Besser Épipactis rouge sombre AC 1925 Epipactis helleborine (L.) Crantz Épipactis à larges feuilles TC 2012 Epipactis microphylla (Ehrh.) Sw. Épipactis à petites feuilles CR oui R 1925 4/15 Annexe I - Espèces végétales Liste rouge Rareté Dernière obs. Taxon de référence Nom vernaculaire Protection ZNIEFF ECOGEE rég. Essonne FLORA Epipactis muelleri Godfery Épipactis de Müller EN oui AR 1999 Equisetum arvense L. Prêle des champs TC 2011 Equisetum fluviatile L. Prêle des eaux AR 2010 Equisetum palustre L. Prêle des marais C 2011 Erica cinerea L. Bruyère cendrée C 2012 2007 Erigeron annuus (L.) Desf. Vergerette annuelle
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  • Troncais DOCOB-2013

    Troncais DOCOB-2013

    Réseau Natura 2000 Document d’Objectifs Zone Spéciale de Conservation Forêt de Tronçais FR 830 1021 Département de l’Allier (03) Région Auvergne Décembre 2013 Annexes Document d’Objectifs - Forêt de Tronçais - Site Natura 2000 « FR8301021» ONF Berry Bourbonnais Décembre 2013 ANNEXE 1 FICHES HABITATS HABITATS RELEVANT DE LA DIRECTIVE HABITATS FAUNE FLORE 92/43/CE ANNEXE 1 Rédacteur principal : Bruno GRAVELAT. Conservatoire Botanique National du Massif Central. Février 2002 Compléments : Yves Le JEAN et Laurent LATHUILLIERE. ONF (Habitats forestiers + landes à Erica tetralix). 2013. Docob Natura 2000. Site de la forêt de Tronçais « FR 8301021 ». Annexe 1. 1 Docob Natura 2000. Site de la forêt de Tronçais « FR 8301021 ». Annexe 1. 2 FICHE N° 1 EAUX OLIGOTROPHES DES PLAINES SABLONNEUSES ATLANTIQUES Code Natura 2000 : 3110 Code CORINE biotopes : 22.11 x 22.31 Habitat prioritaire : Habitat d’intérêt communautaire : X Surface couverte par cet habitat : 1, 14 ha Statut phytosociologique : Littorelletea uniflorae Braun-Blanq. & Tüxen ex V. Wetsth., Dijk & Passchier 1946 ; Littorelletalia uniflorae W. Koch 1926 ; Elodo palustris-Sparganion Braun-Blanq. & Tüxen 1943 in Oberd. 1957 Caractères diagnostiques de l’habitat Caractéristiques stationnelles Les groupements amphibies des Littorelletalia se rencontrent dans les eaux oligotrophes et mésotrophes. Ils se développent sur les rives sablonneuses acides, parfois graveleuses ou plus rarement dans les zones vaseuses. Un immersion hivernale suivie d’une exondation estivale relative des plages abritant ces communautés (eau quasiment affleurante) est indispensable au développement de cet habitat. La fraction organique des substrats est en principe peu élevée, mais nous avons rencontré des stations dans lesquelles une certaine épaisseur de débris végétaux était présente, ce qui devenait préjudiciable aux tapis de Littorelles.
  • The Example of Plant-Pollinator Networks

    The Example of Plant-Pollinator Networks

    Author's personal copy Biological Conservation 143 (2010) 2092–2101 Contents lists available at ScienceDirect Biological Conservation journal homepage: www.elsevier.com/locate/biocon How to monitor ecological communities cost-efficiently: The example of plant–pollinator networks Stein Joar Hegland a,*, Jennifer Dunne b,c, Anders Nielsen d, Jane Memmott e a University College of Sogn and Fjordane, Faculty of Science, P.O. Box 133, 6851 Sogndal, Norway b Santa Fe Institute, 1399 Hyde Park Road, Santa Fe, NM 87501, USA c Pacific Ecoinformatics and Computational Ecology Lab, Berkeley, CA 94703, USA d Centre for Ecological and Evolutionary Synthesis, University of Oslo, P.O. Box 1066, Blindern, 0316 Oslo, Norway e University of Bristol, School of Biological Sciences, Woodland Road, Bristol BS8 1UG, United Kingdom article info abstract Article history: Conservation practitioners often lack tools to monitor functioning of communities because time and Received 17 June 2009 monetary constraints create a gap between the optimal monitoring methods and the practical needs in Received in revised form 20 April 2010 conservation. Interaction networks provide a framework that has proven useful in ecological research. Accepted 25 May 2010 However, they are considered time consuming and too expensive for conservation purposes. We inves- Available online 17 June 2010 tigate whether it is possible to sample interaction networks cost-efficiently and whether a compromise exists between data quality and amount of resources required to sample the data by using a highly Keywords: resolved mutualistic plant–pollinator network sampled over two years in Norway. The dataset was Cost efficiency resampled with decreasing sampling intensity to simulate decreasing monitoring costs and we investi- Habitat management Mutualism gated the cost-efficiency of these monitoring regimes.
  • The Pyrenees

    The Pyrenees

    The Pyrenees A Greentours Holiday for the Alpine Garden Society 10th to 23rd June 2011 Led by Paul Cardy Trip Report and Systematic Lists by Paul Cardy Day 1 Friday 10 th June Arrival and Transfer to Formigueres Having driven from the south western Alps and reached Carcassonne the previous evening, I continued to Toulouse to meet the group at the airport. I was unexpectedly delayed by French customs who stopped me at the toll booth entering the city. There followed a lengthy questioning, as I had to unpack the contents of my suspiciously empty Italian mini-bus and show them my two large boxes of books, suitcase full of clothes, picnic supplies, etc., to convince them my purpose was a botanical tour to the Pyrenees. Now a little late I arrived breathlessly at Toulouse airport and rushed to the gate to meet Margaret, and the New Zealand contingent of Chris, Monica, Archie and Lynsie, hurriedly explaining the delay. Anyway we were soon back on the motorway and heading south towards Foix. White Storks in a field on route was a surprise. We made a picnic stop at a functional aire where there were tables, and a selection of weedy plants. Black Kite soared overhead. Once past Foix and Ax-les- Thermes the scenery became ever more interesting as we wound our way up to a misty Col de Puymorens. There a short stop yielded Pulsatilla vernalis in fruit and Trumpet Gentians. Roadside cliffs had Rock Soapwort, Saxifraga paniculata , and Elder-flowered Orchids became numerous. Now in the Parc Naturel Régional des Pyrénées Catalanes, a fascinating route down into the valley took us through Saillagouse and Mont-Louis before heading up a minor road to the village of Formigueres, our base for the first three nights.
  • Nachtvlinderonderzoek in De Wassenaarse Duinen

    Nachtvlinderonderzoek in De Wassenaarse Duinen

    Nachtvlinderonderzoek in de Wassenaarse duinen Wouter Moerland Neeltje van Zuytbrouckhof 50 2311 WD Leiden [email protected] In de duinen bij Wassenaar worden sinds 2004 nachtvlinders gevangen. De eerste vlinderinventarisaties vonden plaats als onderdeel van de veldcursus ‘dierecologie’ aan de Leidse universiteit. Tegenwoordig zijn er particuliere initiatieven, zoals excursies van de NJN of de Leidse biologenclub. Kleinschalig vlinder- onderzoek toonde al de aanzienlijke vlinderdiversiteit in de Hollandse duinen: resultaten tot 2006 wor- den gepresenteerd door Van Alphen (2006). Sindsdien is het onderzoek voortgezet, met enkele grote inventarisaties. In juli 2007 en 2008 is in verband met de toen nieuwe website www.microlepidoptera.nl de omgeving van veldstation De Klip grondig bemonsterd. Ook buiten dit ‘vlinderhoogseizoen’ is volop gevlinderd, van maart tot in de december. Op basis van deze aanvullende vangsten presenteert dit artikel een herziene en geactualiseerde soortenlijst van nachtvlinders. Het geeft een overzicht van de resultaten van zeven jaar nachtvlinderen in de Wassenaarse duinen. Onderzoek naar nachtvlinders Vlinders (Lepidoptera) vormen in Nederland een diverse groep insecten: ongeveer 2200 soorten zijn er gevestigd (Noordijk et al. 2010). Een niet-wetenschappelijk maar pragmatisch onderscheid wordt gemaakt tussen de ‘grote’ en ‘kleine’ vlinders. Een derde van die 2200 soorten wordt gerekend tot die grote vlinders, de macrolepidoptera (macro’s), inclusief dagvlinders. Het overige deel, de kleine vlinders, wordt microlepidoptera (micro’s) genoemd. Alle vlinders die niet tot de dagvlinders worden gerekend, bestempelt men als nachtvlinders. Figuur 1. Directe omgeving De Klip in de schemering – op de bunker een nachtvlinderlaken. Foto WM 16 Holland’s Duinen nr 57, april 2011 Nachtvlinderonderzoek in de Wassenaarse duinen Veel van de nachtvlinders vliegen ’s nachts of in de schemering.
  • Lepidoptera) of Warsaw City Centre1

    Lepidoptera) of Warsaw City Centre1

    MUSEUM AND INSTITUTE OF ZOOLOGY POLISH ACADEMY OF SCIENCES FRAGMENTA FAUNISTICA Fragm. faun. Warszawa, 30.06.2003 46 69-91 G rażynaW INIARSKA Long-term changes in communities ofNoctuidae, Pantlieidae and Nolidae (Lepidoptera) of Warsaw city centre1 Abstract: In the centre of Warsaw 209 species of noctuid moths (Noctuidae, Pantheidae and Nolidae) were recorded, accounting for about 69% of all species ever found in this agglomeration. Only 15 species were classified as very abundant or abundant while as many as 174 were few and single. The following species were the most abundant: Xestia c-nigrum, Autographa gamma, Discestra trifolii, Mythimna pallens, M. l-album, Agrotis exclamatiotiis, A. segetwn, Hoplodrina ambigua and Luperina testacea. These species occurred abun­ dantly everywhere. They are chiefly associated with open-area habitats (including anthropogenic ones). Noctuid communities in the centre of Warsaw have changed considerably over the last 50 years. The most abundant species have remained a constant element but rare (few and single) species have begun to disap­ pear from the city centre, probably as a result of unfavourable environmental changes due to intensive urbanization of this area. Key words: Noctuidae, Pantheidae, Nolidae, Lepidoptera, urban habitats, big city centre, Warsaw, strong settlement pressure Author's address: Museum and Institute of Zoology PAS, Wilcza 64, 00-679 Warszawa, POLAND INTRODUCTION The town is a human creation. Contemporary cities are a common element of landscape in many regions of our planet. Increasing urbanization induces a number of changes in the environment that have a restrictive effect on the occurrence of most plant and animal species in areas subjected to these impacts.