Ecological Restoration in the Czech Republic

Total Page:16

File Type:pdf, Size:1020Kb

Ecological Restoration in the Czech Republic Ecological restoration in the Czech Republic Editors Ivana Jongepierová, Pavel Pešout, Jan Willem Jongepier & Karel Prach Ecological restoration in the Czech Republic Editors Ivana Jongepierová, Pavel Pešout, Jan Willem Jongepier & Karel Prach Nature Conservation Agency of the Czech Republic Prague 2012 Front cover photograph: — Šumava foothills near Želnava. (Z. Patzelt) Back cover photographs: — Raking hay in Javorůvky NR, Bílé Karpaty PLA. (J.W. Jongepier) — Disturbing sites with Gentianella lutescens, Pod Hribovňou NR, Bílé Karpaty PLA. (I. Jongepierová) — Removing eutrophic soil layers, Váté písky NR, Bzenec. (I. Jongepierová) — Sheep grazing in Central Bohemian Uplands (České středohoří) PLA. (J. Marešová) — Elimination of scrub in Vápenice NR, Velký Kosíř Nature Park. (Archive ZO ČSOP Hořepník) Editors Ivana Jongepierová, Pavel Pešout, Jan Willem Jongepier & Karel Prach Reviewers Ladislav Miko Tomáš Kučera Graphic design David Jongepier Printed by Boma Print, Kyjov *is publication was issued on the occasion of the 8th European Conference on Ecological Restoration held in České Budějovice (Budweis) 9–14 September 2012. Published by Nature Conservation Agency of the Czech Republic, © AOPK ČR ISBN 978-80-87457-31-3 CATALOGUING-IN-PUBLICATION – NATIONAL LIBRARY OF THE CZECH REPUBLIC Ecological restoration in the Czech Republic / editors Ivana Jongepierová ... [et al.]. – Prague : Nature Conservation Agency of the Czech Republic, 2012. – 147 p. : ill. ISBN 978-80-87457-32-0 (pbk.) 502.5+712 * 502.174 * 502.171:574.4/.5 * 502.171:574.2 * (437.3) — landscape assessment – Czechia — restoration ecology – Czechia — ecosystem management – Czechia — habitat protection – Czechia — case studies 363.7 – Environmental protection [2] Contents Foreword . .6 Introduction . .7 Nomenclature, abbreviations and explanatory notes . .8 Restoration ecology and ecological restoration in the Czech Republic . .9 Forests . 11 Introduction . 13 Active restoration and management of forest habitats . 17 Conversion of pine monocultures to mixed deciduous forests in Podyjí National Park . 20 Can ,re and secondary succession assist in the regeneration of forests in a national park? . 24 Restoration of forests damaged by air pollution in the Jizera Mountains . 27 Spontaneous recovery of mountain spruce forests a-er bark beetle attack . 31 Grasslands. 33 Introduction . 35 Experimental restoration and subsequent degradation of an alluvial meadow . 39 Restoration management of wetland meadows in the Podblanicko region . 42 Recreation of species rich grasslands in the Bílé Karpaty Mountains . 45 Grazing of dry grasslands in the Bohemian Karst . 47 Resumption of grazing management on abandoned upland grasslands in the Jizera Mountains . 51 Restoring heterogeneity in submontane meadows for the butter/y Euphydryas aurinia . 53 Optimising management at Gentianella praecox subsp. bohemica sites . 56 Restoration of sands as part of the Action Plan for Dianthus arenarius subsp. bohemicus . 59 Restoration of the alpine tundra ecosystem above the timberline in the Giant Mountains . 61 Wetlands and streams . 65 Introduction . 67 Restoration of the Černý potok stream, Krušné hory Mts. 74 Revitalising e0ects of a near-natural bypass at a migration barrier on the Blanice river . 77 Restoration of drained mires in the Šumava National Park . 80 Restoration of the mined peatbog Soumarský Most . 83 Mining and post-industrial sites . 87 Introduction . 89 Restoration and conservation of sand and gravel-sand pits . 94 Coal mining spoil heaps in the Most region: restoration potential of spontaneous succession . 97 Restoration of spoil heaps by spontaneous succession in the Sokolov coal mining area . 99 Restoration of dry grassland vegetation in the abandoned Hády limestone quarry near Brno . 102 Experimental restoration of species-rich deciduous forest on mining deposits in Mokrá limestone quarry . 104 Experimental acceleration of primary succession on abandoned tailings: role of surface biological crust . 106 Abandoned military areas . .109 Introduction . 111 Disturbance management, a way to preserve species-rich communities in abandoned military areas . 114 Restoring disturbance and open vegetation in the former military training area Na Plachtě . 117 Landscapes . .121 Introduction . 123 Reclamation of rural landscapes at Velké Bílovice . 127 Restoration of the Včelnička stream catchment, Bohemian-Moravian Uplands . 130 Restoration of greenery elements in the Podblanicko region . 134 Restoration of standard orchard at Habrůvka . 136 Restoration of semi-natural vegetation in old ,elds in the Bohemian Karst . 138 Conclusions . 141 List of authors . 142 Nature Conservation Agency of the Czech Republic . 145 Society for Ecological Restoration (SER). Working Group for Restoration Ecology, České Budějovice, Czech Republic . 146 Foreword František Pelc Despite strong e0orts and partly positive results in the ,eld of nature conservation, we have recently witnessed continuing deterioration of the natural environment and decrease in biodiversity on a global as well as a national scale. It is therefore no wonder that rather lively discussions have been going on between conservationists, biologists and other interested parties on ways of securing the protection of the most valuable natural environment, usually concentrated in small fragments, in total covering a few percent of our country’s area. Sometimes this problem has unfortunately been centred around two rivalling visions: the approach of ‘conservation’ management (by some considered obsolete), based on non-intervention and preference of natural processes, on the one hand, and ‘active’ management (o-en considered modern), based on sys- tematic intervention by man. *e dispute about what is more correct has led to endless discussions. I am convinced that most protected areas need some kind of active management. However, there will always be a wide range of options depending on what we want to protect – from preferring absolute protec- tion of natural processes to very speci,c management simulating e.g. abandoned farming methods or preserving selected sites or protected species. Both approaches must be part of an integral concept of modern conservation and restoration of our natural heritage. *ey are mutually complementary and no antipodes. It is important to make clear what to protect and how to achieve this, taking into consideration the natural potential and historical context of a given area. Based on this, a long-term, sustainable strategic decision can be adopted, which must however not unpredictably be changed in the short term. In general it would be desirable to respect the fact that man cannot steer everything in the natural environment, and protected areas are no exception. He does not have su1cient knowledge or means. A-er all, it is just a small step from here to the misused noosphere concept by Russian philosopher Vernadský. On the other hand, man has in/uenced the environment and environmental processes in such a way that many natural phenomena cannot be protected or rehabilitated anymore without his intervention. *e present publication is a representative display of restoration management case studies realised in various environments such as forests, wetlands, grasslands as well as speci,c sites damaged or created by mining or other activities. It should also contribute to the so desirable integra- tion of views by scientists, conservationists, foresters, farmers, ,shermen and other interested parties, and their application. As such it should become the starting point of a more e0ective use of scienti,c knowledge to preserve our nature and protect our landscape better. Although the case studies mainly deal with so-called active management, I hope their overall impression will contribute to creating a state in which the management of protected areas and natural habitats will not be divided into ‘conservational’ and ‘active’, but rather be judged as good or bad. František Pelc, Director Nature Conservation Agency of the Czech Republic 6 Introduction *e Czech Republic, a country in central Europe, used to consist of a , ne-scale mosaic of natural, semi-natural and anthropogenous ecosystems. However, this mosaic has been substantially disturbed in the second half of the 20th century under the communist regime. Many ecosystems were disturbed, degraded or destroyed. *e traditional nature conservation approach in the Czech Republic was, similarly to other countries, strictly protecting well-preserved ecosystems. Only in the past three decades, more active approaches utilising methods of ecological restoration have been adopted. *ese are ap- plied to both existing ecosystems, such as meadows, and newly developing ones, for example sites disturbed by mining or developed on former arable land. Recently, also some attempts have been made to.
Recommended publications
  • Potential European Bison (Bison Bonasus) Habitat in Germany
    PROJECT REPORT Potential European bison (Bison bonasus) habitat in Germany Tobias Kuemmerle Humboldt-University Berlin Benjamin Bleyhl Humboldt-University Berlin Wanda Olech University of Warsaw & European Bison Friends Society Kajetan Perzanowski Carpathian Wildlife Research Station MIZ, PAS & European Bison Friends Society 1 PROJECT REPORT CONTENTS CONTENTS ...............................................................................................................................................................2 INTRODUCTION .......................................................................................................................................................3 HISTORIC DISTRIBUTION OF EUROPEAN BISON IN EUROPE .....................................................................................4 EUROPEAN BISON HABITAT PREFERENCES ..............................................................................................................6 HABITAT USE OF CONTEMPORARY EUROPEAN BISON POPULATIONS .......................................................................................... 6 PALEO-ECOLOGICAL DATA ON EUROPEAN BISON HABITAT USE ............................................................................................... 10 MAPPING EUROPEAN BISON HABITAT IN GERMANY ............................................................................................ 10 APPROACH .................................................................................................................................................................
    [Show full text]
  • The Sphingidae (Lepidoptera) of the Philippines
    ©Entomologischer Verein Apollo e.V. Frankfurt am Main; download unter www.zobodat.at Nachr. entomol. Ver. Apollo, Suppl. 17: 17-132 (1998) 17 The Sphingidae (Lepidoptera) of the Philippines Willem H o g e n e s and Colin G. T r e a d a w a y Willem Hogenes, Zoologisch Museum Amsterdam, Afd. Entomologie, Plantage Middenlaan 64, NL-1018 DH Amsterdam, The Netherlands Colin G. T readaway, Entomologie II, Forschungsinstitut Senckenberg, Senckenberganlage 25, D-60325 Frankfurt am Main, Germany Abstract: This publication covers all Sphingidae known from the Philippines at this time in the form of an annotated checklist. (A concise checklist of the species can be found in Table 4, page 120.) Distribution maps are included as well as 18 colour plates covering all but one species. Where no specimens of a particular spe­ cies from the Philippines were available to us, illustrations are given of specimens from outside the Philippines. In total we have listed 117 species (with 5 additional subspecies where more than one subspecies of a species exists in the Philippines). Four tables are provided: 1) a breakdown of the number of species and endemic species/subspecies for each subfamily, tribe and genus of Philippine Sphingidae; 2) an evaluation of the number of species as well as endemic species/subspecies per island for the nine largest islands of the Philippines plus one small island group for comparison; 3) an evaluation of the Sphingidae endemicity for each of Vane-Wright’s (1990) faunal regions. From these tables it can be readily deduced that the highest species counts can be encountered on the islands of Palawan (73 species), Luzon (72), Mindanao, Leyte and Negros (62 each).
    [Show full text]
  • Conservation Covenants
    Law Commission Consultation Paper No 211 CONSERVATION COVENANTS A Consultation Paper ii THE LAW COMMISSION – HOW WE CONSULT About the Law Commission: The Law Commission was set up by section 1 of the Law Commissions Act 1965 for the purpose of promoting the reform of the law. The Law Commissioners are: The Rt Hon Lord Justice Lloyd Jones, Chairman, Professor Elizabeth Cooke, David Hertzell, Professor David Ormerod QC and Frances Patterson QC. The Chief Executive is Elaine Lorimer. Topic of this consultation: This Consultation Paper examines the case for introducing “conservation covenants” into the law of England and Wales, and considers how a scheme of conservation covenants might be framed. A conservation covenant is a private agreement made by a landowner, for the purposes of conservation. We discuss the current law and set out a number of provisional proposals and options for reform on which we invite consultees’ views. Geographical scope: The Consultation Paper applies to the law of England and Wales. Impact assessment: In Chapter 9 of this Consultation Paper, consultees are asked also to comment on the likely costs and benefits of any changes provisionally proposed. Consultees’ responses will inform our final recommendations and a formal impact assessment document that will be published with our Report. Availability of materials: This Consultation is available on our website at: http://lawcommission.justice.gov.uk/consultations/conservation-covenants.htm. Duration of the consultation: We invite responses from 28 March 2013 to 21 June 2013. Comments may be sent: By email to: [email protected] or By post to: Luke Campbell, Law Commission, Steel House, 11 Tothill Street, London SW1H 9LJ Tel: 020 3334 0200 / Fax: 020 3334 0201 If you send your comments by post, it would be helpful if, whenever possible, you could send them to us electronically as well (for example, on CD or by email to the above address, in any commonly used format).
    [Show full text]
  • Land Use Element of the General Plan
    General Plan Land Use Element Adopted December 15, 1993 Amended November 9, 2011 Amended July 22, 2015 Amended July 26, 2016 Amended April 26, 2017 Amended September 26, 2017 Amended December 13, 2017 Amended December 17, 2019 Amended October 6, 2020 County of Sacramento Office of Planning and Environmental Review . This page is blank County of Sacramento General Plan Land Use Element Amended October 6, 2020 Table of Contents SECTION I ..................................................................................................................................... 1 ELEMENT INTRODUCTION ....................................................................................................... 1 Required Contents of the Land Use Element .............................................................................. 1 Concepts of the Land Use Element ............................................................................................. 1 Relationship to Other Elements .................................................................................................. 2 Relationship to Other County Planning Tools ............................................................................ 3 Relationship to Regional Planning Efforts ................................................................................. 6 THE GENERAL PLAN LAND USE DIAGRAM ......................................................................... 7 How to Use the Land Use Diagram ..........................................................................................
    [Show full text]
  • The Development of the Health and Social Care Sector in the Regions of the Czech Republic in Comparison with Other EU Countries
    social sciences $€ £ ¥ Article The Development of the Health and Social Care Sector in the Regions of the Czech Republic in Comparison with other EU Countries Erika Urbánková Department of Economic Theories, Faculty of Economics and Management, Czech University of Life Sciences, Prague 16500, Czech Republic; [email protected] Received: 6 April 2019; Accepted: 29 May 2019; Published: 3 June 2019 Abstract: In this paper, the quantitative status of employees in the Health and Social Care sector in the Czech Republic is assessed, and the future development of the sector is predicted both for the Czech Republic as a whole, and for individual regions according to the NUTS3 classification. At present, labor market prognoses are created using the ROA-CERGE model, which includes the main professions in the Health and Social Care sector. This article expands the predictions by adding the regional level and using extrapolation of time series, and it identifies the regions important for the given sector and the labor force. The position of the Czech Republic with regard to selected professions in comparison with other countries of the European Union, i.e., its qualitative status, is also assessed in the paper. The following professions are assessed: general nurses and midwives (both with and without a specialization), physicians, and professional assistants. Healthcare workers do not manifest geographical mobility between regions and work primarily in the region where they live. Since the Czech Republic’s accession to the EU, staff working in key professions have been able to work under comparable conditions in any of the member states. The workforce flow depends, among other things, on its qualitative representation in the given country.
    [Show full text]
  • An Investment Primer for Reforestation CARBON REMOVAL, ENVIRONMENTAL and SOCIAL IMPACTS, and FINANCIAL POTENTIAL
    1 An Investment Primer for Reforestation CARBON REMOVAL, ENVIRONMENTAL AND SOCIAL IMPACTS, AND FINANCIAL POTENTIAL JANUARY 2020 1 CONTENTS Contents About CREO 2 Terms 3 Executive Summary 4 Background Forestry for Climate 6 Reforestation Investment Potential 9 - Investment Avenues 9 - Costs and Returns 10 Carbon Markets Regulatory Compliance 14 Voluntary 15 Corporate Offsetting 15 Summary 16 Timber and Non-Timber Forest Products Timber 18 Agroforestry 19 Summary 20 Restoration and Conservation Initiatives Direct Revenue Creation 22 Blended Finance 23 Catalytic Capital 24 Summary 24 Moving Forward 25 Appendix A: CREO Modelling Assumptions 26 Appendix B: Carbon Markets 27 Citations 28 2 ABOUT CREO About CREO The CREO Syndicate (“CREO”) is a 501c3 public charity founded by wealth owners and family offices with a mission to address the most pressing environmental challenges of our time affecting communities across the globe—climate change and resource scarcity. By catalyzing private capital and scaling innovative solutions, CREO is contributing to protecting and preserving the environment and accelerating the transition to a sustainable economy for the benefit of the public. CREO works closely with a broad set of global stakeholders, including Members (wealth owners, family offices, and family-owned enterprises), Friends (aligned investors such as pension funds), and Partners (government, not-for-profit organizations and academia), who collaboratively develop and invest in solutions across sectors, asset classes and geographies. CREO’s primary activities include 1) knowledge building; 2) relationship building among like-minded, values-aligned, long-term investors; 3) conducting select research to support the advancement of its mission; and 4) deal origination. 3 TERMS Terms Afforestation (AF): Planting and/or deliberate seeding on land not forested over the last 50 years.
    [Show full text]
  • Saxon-Bohemian Switzerland Transparcnet Meeting Saxon-Bohemian Switzerland
    National Park Region Saxon-Bohemian Switzerland TransParcNet Meeting Saxon-Bohemian Switzerland: 7.6.2016 Four protected areas, two countries, NLP-Zentrum Bad Schandau one landscape Handrij Härtel & Jürgen Phoenix National Park Region Saxon-Bohemian Switzerland Saxon-Bohemian Switzerland: Discovery by Romantic painters Adrian Zingg (1734-1816) National Park Region Saxon-Bohemian Switzerland Saxon-Bohemian Switzerland Caspar David Friedrich (1774 Greifswald - 1840 Dresden) National Park Region Saxon-Bohemian Switzerland Saxon-Bohemian Switzerland Caspar David Friedrich (1774 Greifswald - 1840 Dresden) National Park Region Saxon-Bohemian Switzerland Saxon-Bohemian Switzerland: One of the oldest European tourist destinations Protected areas in sandstone rock regions across the world National Park Region Saxon-Bohemian Switzerland TransParcNet Meeting Saxon-Bohemian Switzerland: 7.6.2016 Singularity in European context: NLP-Zentrum Bad Schandau 3 sandstone rock national parks only National Park Region Saxon-Bohemian Switzerland TransParcNet Meeting Saxon-Bohemian Switzerland 7.6.2016 as part of larger geological unit NLP-Zentrum Bad Schandau Bohemian Cretaceous Basin PL D CZ Marine fossils from Cretaceous sandstones Inoceramus labiatus Natica bulbiformis Pecten Inoceramus lamarcky National Park Region Saxon-Bohemian Switzerland TransParcNet Meeting Saxon-Bohemian Switzerland: 7.6.2016 NLP-Zentrum High diversity of morphologic forms at different Bad Schandau spatial scales Saxon-Bohemian Switzerland: Terciary volcanism Růžovský vrch Zlatý vrch National Park Region Saxon-Bohemian Switzerland TransParcNet Meeting Saxon-Bohemian Switzerland: 7.6.2016 geodiversity-biodiversity relations NLP-Zentrum Bad Schandau Saxon-Bohemian Switzerland: role of microclimate Saxon-Bohemian Switzerland: vertebrates Grasshopper Troglophilus neglectus New for Central Europe (Chládek, Benda & Trýzna 2000) Charissa glaucinaria Extremely rare montane species, within CZ in Bohemian Switzerland only L – Phengaris nausithous R – Phengaris telejus Monitoring of the butterflies from the gen.
    [Show full text]
  • Creation of Sustainable Public Transport in the National Park Region Saxon-Bohemian Switzerland
    National Park Region Saxon-Bohemian Switzerland Creation of sustainable public transport in the National Park Region Saxon-Bohemian Switzerland Jürgen Phoenix, NPA Saxon Switzerland National Park Region Saxon-Bohemian Switzerland Saxon-Bohemian Switzerland: Protected Landscape Area (D): 287 km² Protected Landscape Area (CZ): 245 km² National Park (D): 93 km² National Park (CZ): 80 km² National Park Region Saxon-Bohemian Switzerland Situation analysis - tourism is the most important economic sector in the region, - but the large number of visitors causes risks for the protected areas, - one problem area is the private vehicle traffic of visitors (although the region is very well connected by public transport). keeping the situation in balance takes a lot of communication and cooperation between the different stakeholders. National Park Region Saxon-Bohemian Switzerland Traffic calming - a never-ending story? Traffic calming is a long-term task, don´t let any failures discourage you, after defeat get back on your feet again. National Park Region Saxon-Bohemian Switzerland Experiences from 25 years involvement in traffic calming Traffic regulation and public transport don´t fall within the jurisdiction of the National Park administration. Its possibilities are limited: - to chair processes, - to provide ideas, - to support projects and plannings with (limited) finances. Changes in the main points 1990 – 2000 the stakeholders gave a lukewarm reaction to the topic, the activities focused on the private vehicle traffic of the visitors. since
    [Show full text]
  • The Red Data List of Irish Plants
    The Red Data List of Irish Plants The risks that species face are each very different, however, as a guide to the susceptibility of a given species, an agreed set of categories has been established internationally, and these are used to determine the potential risk that a species could become extinct. These categories are:- CRITICALLY ENDANGERED or CR - Species that are declining at a fast rate, and face imminent risk of extinction. ENDANGERED or E - Species that are declining, or grow in habitats likely to be disturbed, 'developed' or facing an ongoing degradation. VULNERABLE or V - Species that are currently not endangered, but would be extremely vulnerable if their habitats are disturbed in the future. There are seven species of plant that require immediate intervention (CR) if we are to save them from joining the fate of 11 other species that are now known to be extinct in Ireland. A number of these are already extinct in the Republic, and are not therefore legally protected under the 1999 Flora Protection Act. In the list below, 188 species of plant are listed, of which 64 are flowering plants, 4 ferns, 14 mosses, 4 liverworts, 1 lichen and 2 algae. Protected=1999 Flora Protection Order; (protected)= formerly protected by 1987 Order; {protected}= formerly protected by 1980 Order; (NI)= protected in Northern Ireland only. EXTINCT (9) Pheasant's-eye Adonis annua -- Corncockle Agrostemma githago Cogal Corn Chamomile Anthemis arvensis Fíogadán goirt Purple Spurge Euphorbia peplis Spuirse dhearg Sea Stock Matthiola sinuata Tonóg chladaigh
    [Show full text]
  • Central Bohemia Region
    CENTRAL BOHEMIA CENTRAL BOHEMIA CZECH REPUBLIC / CENTRAL BOHEMIAN REGION Allow us to invite you to the largest region of the Czech Republic, enveloping the Czech capital, Prague. Visit our impressive sites, included on the UNESCO 1 World Heritage list, explore our majestic castles, unique natural scenery and rich cultural tradition. Central Bohemia is the perfect place for tourism, full of adventure and discovery. Our beautiful natural PRAGUE surroundings, with their rock formations and caves and large reservoirs on major rivers are just made for hiking, cycling and water sports. Devotees of golf or agrotourism are also very well provided for. 2 Come and sample the products of our local wineries and breweries, get to know authentic rural life as well as our glassmaking tradition. You don’t have to be a technology aficionado to enjoy our displays of mining, aerospace, railways and the automotive industry. Discover the beauty of Central Bohemia and enjoy a truly vibrant vacation! 1. Karlštejn castle 2. Český Šternberk 3. Mělník château 3 1 Immerse yourself in the endless beauty of untamed nature. Dense forests, rocky outcrops, steep peaks and deep valleys 2 – stunning natural scenery awaits you at every step. 1. Drábské světničky scenic rocks 2. Křivoklátsko district 3. Příhrazské skály scenic rocks 3 1 Go with the flow, or head upstream Several major rivers cross the region, which has given rise to impressive bodies of water, whether natural or man-made. 2 1. Vyhlídka Máj lookout point 2. The Slapy Dam 3. ‘America’ stone quarry gorge 3 1. Kačina stately home 2. Mnichovo Hradiště château 3.
    [Show full text]
  • 58 New Distributional Record of Daphnis Hypothous Crameri
    Vol. 24 (1) (March 2021) Insect Environment New distributional record of Daphnis hypothous crameri Eitschberger & Melichar, (Sphingidae: Lepidoptera) from Odisha, India Ashirwad Tripathy1 and Kishore Chandra Sahoo2 1Department of Silviculture and Agroforestry, Birsa Agricultural University, Kanke, Ranchi, Jharkhand- 834006 India 2Division of Entomology, ICAR- Indian Agricultural Research Institute, Pusa, New Delhi- 110012 India Corresponding author: [email protected] The Indian subcontinent is well known for its high biodiversity, varied environment and habitats, and interesting geological history. However, much work remains to document and catalogue the species of India and their geographic distribution, especially for invertebrate groups, in which Odisha still remain unexplored as per insect diversity is concerned. Moths and butterflies contribute to essential ecosystem processes such as herbivory, pollination and decomposition in many terrestrial biomes. They are strongly associated with vegetation structure and composition, which make them a suitable indicator taxon for various ecological studies (Lomov et al., 2006). As they are highly sensitive to environmental changes and proved to be powerful indicator of forest disturbance moth communities are receiving increasing conservation interest (Luff and Woiwod, 1995, Summerville et al., 2004, Scalericio et al., 2009). Documenting the faunal diversity of moth can get evolutionary insights and a first step in developing conservation goals for the Lepidoptera (Gadhikar et al., 2015). Species level inventories will provide baseline data on the geographic distribution of species which is a prerequisite for management and preservation of natural habitats whereas local level inventories provide information for economic and educational activities (Arandhara et al., 2017). There are around 1,42,000 moth species in the world.
    [Show full text]
  • Biodiversity of the Hercynian Mountains of Central Europe
    Pirineos, 151-152: 83 a 99, JACA; 1998 BIODIVERSITY OF THE HERCYNIAN MOUNTAINS OF CENTRAL EUROPE JAN JENÍK Faculty of Science, Charles University, Benátská 2, CZ-12801 Praha 2, Czech Republic SUMMARY.- The vegetation of temperate Central Europe north of the Alps is mainly of low diversity broadleaf and conifer forest. The occurrence of three azonal habitat types: mires with their numerous microhabitats, the georelief of the karst and its deeply-cut river valleys, and ecological islands with a distinct vegetation near the treeline of the middle-mountains causes local areas of high diversity. These high species diversity spots are the result of an interplay between physical, biotic and historical factors. A model of an anemo-orographic system with its underlying factors is described to explain the high plant and animal diversity in the corries (glacial cirques) of the Hercynian mountains. RÉSUMÉ.-La végétation de l'Europe Centrale tempérée au nord des Alpes nous montre surtout des forêts à de feuillues et de connifères à faible diversité. Cependant, la présence de trois types d'habitats azonaux peut produire une haute diversité au niveau local: zones humides avec leur nombreux microhabitats, reliefs karstiques et leur profonds défilés fluviaux, et enfin des îles écologiques avec une végétation par­ ticulière situées près de la limite supérieure des arbres (treeline). Ces secteurs riches en espèces peuvent s'expliquer par l'interaction des facteurs physiques, biotiques et historiques. Dans ce domaine nous proposons un système anémo-orographique avec ses facteurs inféodés qui pourrait expliquer la haute diversité animale et végétale dans les cirques glaciaires des montagnes hercyniennes.
    [Show full text]