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The Dusky Large Blue – Maculinea Nausithous Kijevensis (Sheljuzhko, 1928) in the Transylvanian Basin: New Data on Taxonomy and Ecology
Nota lepid. 33 (1): 16931 – – 37 175 31 The Dusky Large Blue – Maculinea nausithous kijevensis (Sheljuzhko, 1928) in the Transylvanian basin: New data on taxonomy and ecology LÁSZLÓ RÁKOSY 1, ANDRÁS TARTALLY 2, 3, MARIN GOIA 4, CIPRIAN MIHALI 1 & ZOLTÁN VARGA 2, 5 1 Department of Taxonomy and Ecology, Babes-Bolyai University, RO-3400, Str. Clinicilor 5 – 7, Cluj-Napoca, Romania 2 Department of Evolutionary Zoology, University of Debrecen, H-4010 Debrecen, Egyetem-tér 1. Hungary 3 Centre for Social Evolution, Department of Biology, University of Copenhagen, Universitetsparken 15, DK-2100, Copenhagen, Denmark; tartally@delÀ n.unideb.hu 4 Alea Azuga Nr9/32, RO-400451, Cluj-Napoca, Romania 5 Hungary; [email protected], corresponding author Abstract. Maculinea nausithous (Bergsträsser, 1779) was recently discovered in two parts of the Tran- sylvanian basin. External characters of these populations completely agree with the original description of Maculinea nausithous kijevensis (Sheljuzhko, 1928) and show some small but constant differences against the Central European nominotypic populations. Since the habitats and host ant selection of these popula- tions are also different from the Central European populations, we consider M. nausithous kijevensis stat. rev. as valid subspeciÀ c taxon. Specimens with the same external characters were also collected in north- eastern Romania, in Kazakhstan and in the western part of the Altai Mts. Therefore we believe that this subspecies has a wider Euro-Siberian distribution. Introduction The Dusky Large Blue, Maculinea nausithous (Bergsträsser, 1779) 1, has a Euro- Siberian distribution with a wide but sporadic range from Western and Central Europe to Kazakhstan, Southern Siberia and Mongolia (Lukhtanov & Lukhtanov 1994; Tuzov 1997; Wynhoff 1998; Munguira & Martín 1999). -
Intensive Mowing Effect of One Patch on the Metapopulations of Two Phengaris Species*
ENVIRONMENTAL SCIENCES INTENSIVE MOWING EFFECT OF ONE PATCH ON THE METAPOPULATIONS OF TWO PHENGARIS SPECIES* T. Bubová, M. Kulma, D. Koleška, V. Vrabec Czech University of Life Sciences Prague, Faculty of Agrobiology, Food and Natural Resources, Prague, Czech Republic In the second half of the 20th century, change of land use in the name of intensive agriculture was one of the most important factors caused significant loss of butterfly diversity in Europe. Phengaris nausithous and Phengaris teleius belong among the flagship species associated with wet meadows and are directly threatened by the intensive agriculture practises or management abandonment. Due to their very specific lifecycle, they are closely linked to their habitats and appropriate mowing manage- ment on their patches is thus crucial for their survival. Our research took place in Dolní Labe, Děčín, Czech Republic, on 16 patches and has been performed using Mark-Release-Recapture since 2009. This paper will illustrate how intensive mow- ing management, applied on only one of the patches, which forms only 9.4% of total locality size, can influence the entire local Phengaris metapopulation. The selected patch was intentionally mowed in the middle of flight season annually for four years. Even though, no significant effect was identified after the first year of study, after the second and third seasons, there was evidence of population decline of both studied species. Mark-Release-Recapture, land use management, Lepidoptera, conservation doi: 10.2478/sab-2018-0027 Received for publication on September 13, 2017 Accepted for publication on December 17, 2017 INTRODUCTION primarily due to patch destructions or other irrevers- ible changes performed on these meadows (S a l a et Cultural landscape and agricultural lands are histori- al., 2000; S u t c l i f f e et al., 2015). -
Effects of Timing and Frequency of Mowing on the Threatened Scarce
Agriculture, Ecosystems and Environment 196 (2014) 24–33 Contents lists available at ScienceDirect Agriculture, Ecosystems and Environment journa l homepage: www.elsevier.com/locate/agee Effects of timing and frequency of mowing on the threatened scarce large blue butterfly – A fine-scale experiment a,b, c d e f Ádám KÅrösi *, István Szentirmai , Péter Batáry , Szilvia Kövér , Noémi Örvössy , g László Peregovits a MTA–ELTE–MTM Ecology Research Group, Pázmány Péter s. 1/C, Budapest 1117, Hungary b Field Station Fabrikschleichach, Biocenter, University of Würzburg, Glasshüttenstr. 5, Rauhenebrach 96181, Germany c Ärség National Park Directorate, Siskaszer 26/A, Äriszentpéter 9941, Hungary d Agroecology, Georg-August University, Grisebachstr. 6, Göttingen 37077, Germany e Institute of Biology, Szent István University, Rottenbiller u. 50, Budapest 1077, Hungary f Institute of Ecology and Botany, MTA Centre for Ecological Research, Alkotmány u. 2-4, Vácrátót 2163, Hungary g Pars Limited, Rózsa u. 17, Nagykovácsi 2094 Hungary A R T I C L E I N F O A B S T R A C T Article history: As part of a major transformation of the EU agriculture in the last few decades, traditional land-use types Received 5 December 2013 disappeared due to either intensification or abandonment. Grasslands are highly affected in this process Received in revised form 18 June 2014 and are consequently among the most threatened semi-natural habitats in Europe. However, Accepted 23 June 2014 experimental evidence is scarce on the effects of management types on biodiversity. Moreover, Available online 5 July 2014 management types need to be feasible within the recently changed socio-economic circumstances in Hungary. -
The IUCN Red List of Threatened Species™ European Assessment Update – March 2010 © Tom Nygaard Kristensen Species Facts
The IUCN Red List of Threatened Species™ European Assessment Update – March 2010 © Tom Nygaard Kristensen Species Facts © Jean-Pierre Boudot What do butterflies, beetles and dragonflies have in common? Butterflies, beetles and dragonflies play an important role in contributing to Europe’s rich biodiversity. Through pollination, nutrient-cycling and pest control, respectively, they help to maintain vital balances within the ecosystems upon which we all depend. Unfortunately, according to the IUCN Red List of Threatened Species™ - the world’s most comprehensive information source on the global conservation status of animals and plants - all three taxonomic groups are considered to be in decline in Europe. Furthermore, recent analyses found that 9% of Europe’s butterflies, 11% of its saproxylic beetles and 14% of its dragonflies are threatened with extinction. There are 482 butterfly species in Europe, with the highest diversity being found in the mountainous areas of southern Europe, mainly the Pyrenees, the Alps and the Balkans. Butterflies go through three main stages of development – from caterpillar to chrysalis to adult – and have very different habitat requirements during each of these stages. Saproxylic beetles depend upon decaying wood, particularly in forests, for their survival. These beetles play an important role in the decomposition and nutrient- cycling processes which occur in natural ecosystems, and many are also involved in pollination. Dragonflies are relatively large insects, recognized for their striking colours and equilibristic flight. Most of them make their homes in freshwater environments, and thus serve as good indicators for environmental change both above and below the water’s surface. THE IUCN RED LIST OF THREATENED SPECIES™ What is the main threat? The main threat to all three groups of species is habitat loss, although climate change is set to become an increasing threat in the future. -
At Home on Foreign Meadows: the Reintroduction of Two Maculineae Butterfly Species
At Home onForeign Meadows: theReintroduction oftwo Maculinea ButterflySpecies CENTRALE LANDBOUWCATALOGUS 0000 0872 4219 Promotores: Prof. Dr. H.H.T.Prin s Hoogleraar in het Natuurbeheer ind eTrope ne n Ecologieva n Vertebraten Wageningen Universiteit Prof.Dr . P.M.Brakefiel d Hoogleraar Evolutiebiologie Universiteit Leiden Promotie commissie: Prof. Dr. L.E.M.Ve t Wageningen Universiteit Prof. Dr. J.M.va nGroenendae l Katholieke Universiteit Nijmegen Dr.J.A . Thomas NERC Centre of Ecology and Hydrology, England Dr. M.M. Kwak Rijksuniversiteit Groningen y; VX.JO27XV ,3o -> yAfHom e onForeign Meadows: theReintroduction oftwo Maculinea ButterflySpecies Irmgard Wynhoff Proefschrift ter verkrijging van degraa dva n doctor opgeza g van de rector magnificusva nWageninge n Universiteit Prof. Dr. Ir. L. Speelman, in hetopenbaa r te verdedigen opvrijda g 5oktobe r 2001 des namiddagst evie r uur ind eAul a Abstract Wynhoff, I.,2001 . At Home on Foreign Meadows:th e Reintroduction oftw o MaculineaButterfl y species. Doctoral Thesis. ISBN90-5808-461-2 . Wageningen Agricultural University, The Netherlands. Maculinea butterflies live asobligat e parasites of specific Myrmica hostant s in meadow and heathland habitat maintained by low intensity landuse.Change s in agriculture causedth edeclin e and extinction of many populations. InTh e Netherlands, Maculinea nausithousan d M.te/e/t/s disappeare d inth e 1970s.I n 1990,the ywer e reintroduced following the recommendations ofth e IUCN.Thi s study focuses onth eevaluatio n ofthi s reintroduction intoth e nature reserve Moerputten inth e province of Northern Brabant. Population establishment and dispersalwer e monitoredan daccompanie d by researcho nth e impact ofth e reintroduction onspecies-specifi c genetic composition and behaviour.Maculinea teleiusimmediatel y established itself onon e meadow, where the population still occurs today. -
Do Not Eat Too Much! the Key to Success – Suitable Land Use Systems Research for the Scarce Large Blue
Part ne r o f N a t u r e NR.8 The key to success – Suitable land use systems The habitats of M. teleius need to be kept open by regular mowing or in a few cases by grazing. If mowing takes place too often or too infrequent it can lead to adverse habitat conditions for the host plant or the host ants. Adverse mowing can seriously reduce the chance of finding the right host ant and being adopted successfully. Another risk is mowing too early, which can lead to the destruction of the young caterpillars, which still live in the buds of the host plants. The wrong frequency or date of mowing can cause the local extinction of M. teleius populations. Research for the Scarce Large Blue The multitude of questions about how to design suit- The Scarce Large Blue (Maculinea teleius) has light grey- able land use systems in the different habitat types called brown underwings with two rows of dark spots. The for detailed research. The Bavarian Academy for Nature marginal spots often appear diffused. The butterfly is an Conservation and Landscape management (ANL) con- indicator species for extensively used moist mesophile sequently started a research project about the impact of grasslands like litter meadows, tall herb communities, and land uses systems on M. teleius. Fortunately we had the wet meadows, all mostly poor in nutrients. The species has chance to integrate our investigations in the EU research suffered a strong decrease all over Europe and is listed in project “MacMan” (EVK2-CT-2001-00126) which brought Appendix II and IV of the EU Habitats Directive. -
Introduction
BULGARIA Nick Greatorex-Davies. European Butterflies Group Contact ([email protected]) Local Contact Prof. Stoyan Beshkov. ([email protected]) National Museum of Natural History (NMNH), Sofia, Butterfly Conservation Europe Partner Bulgarian Academy of Sciences Stanislav Abadjiev compiled and collated butterfly records for the whole of Bulgaria and published a Local Recording Scheme distribution atlas in 2001 (see below). Records are still being gathered and can be sent to Stoyan Beshkov at NMNH, Sofia. Butterfly List See Butterflies of Bulgaria website (Details below) Introduction Bulgaria is situated in eastern Europe with its eastern border running along the Black Sea coast. It is separated from Romania for much of its northern border by the River Danube. It shares its western border with Serbia and Macedonia, and its southern border with Greece and Turkey. Bulgaria has a land area of almost 111,000 sq km (smaller than England but bigger than Scotland) and a declining human population of 7.15 million (as of 2015), 1.5 million of which live in the capital city, Sofia. It is very varied in both climate, topography and habitats. Substantial parts of the country are mountainous, particularly in the west, south-west and central ‘spine’ of the country and has the highest mountain in the Balkan Mountains (Musala peak in the Rila Mountains, 2925m) (Map 1). Almost 70% of the land area is above 200m and over 27% above 600m. About 40% of the country is forested and this is likely to increase through natural regeneration due to the abandonment of agricultural land. Following nearly 500 years under the rule of the Ottoman Empire, Bulgaria was independent for just a few years from 1908 before coming under the domination of the soviet communist regime in 1946. -
Evaluation of Active Management Applied to Meadows with Phengaris Butterflies Occurrence*
ENVIRONMENTAL SCIENCES EVALUATION OF ACTIVE MANAGEMENT APPLIED to MEADOWS WITH PHENGARIS BUTTERFLIES OCCURRENCE* T. Bubová, M. Kulma, V. Vrabec Czech University of Life Sciences Prague, Faculty of Agrobiology, Food and Natural Resources, Prague, Czech Republic In recent decades, changes in meadows maintenance have reduced the populations of endangered butterfly species Phengaris nausithous (Bergsträsser, 1779) and P. teleius (Bergsträsser, 1779). Currently, meadows are either abandoned or intensively used. Unfortunately, both these managements are considered unfavourable for grassland butterfly species. In this study, the effect of suitable meadow management on population sizes of both the above mentioned Phengaris species was investigated. The experiment was performed at the locality Dolní Labe (Děčín, Czech Republic). The most suitable models, based on the lowest values of Akaike’s information criterion corrected for small sample sizes, were selected using MARK statistical soft- ware. The results were subsequently compared with data obtained from this locality prior to the management application. Un- expectedly, no significant positive effects were found. To reach the desirable status, suitable management practices should be applied for long-term. To verify the management effect on the population size, the meadows were divided into three groups: (i) application of favourable management, (ii) mowing in inappropriate term, (iii) without management. Based on the statisti- cal evaluation, the management application proved to be the most favourable option for both studied butterflies species. Phengaris teleius, Phengaris nausithous, Dolní Labe, active protection, mowing, succession doi: 10.1515/sab-2016-0024 Received for publication on October 6, 2015 Accepted for publication on August 30, 2016 INTRODUCTION 2007). On the other hand, the absence of agricultural interventions leads to the onset of succession (H u l a The majority of European butterfly species are vi- et al., 2004; S k ó r k a et al., 2007). -
Pattern of Genetic and Morphometric Differentiation in Maculinea Nausithous (Lepidoptera: Lycaenidae) in the Carpathian Basin
Acta Zoologica Academiae Scientiarum Hungaricae 58 (1), pp. 87–103, 2012 PATTERN OF GENETIC AND MORPHOMETRIC DIFFERENTIATION IN MACULINEA NAUSITHOUS (LEPIDOPTERA: LYCAENIDAE) IN THE CARPATHIAN BASIN HOLLÓS, A.1, PECSENYE, K.1, BERECZKI, J.1, BÁTORI, E.1, RÁKOSY, L.2 and VARGA, Z.1 1Department of Evolutionary Zoology and Human Biology, University of Debrecen H-4010, Egyetem tér 1, Debrecen, Hungary; e-mail: [email protected] 2Department of Taxonomy and Ecology, Babeş-Bolyai University RO-3400, Str. Clinicilor 5–7, Cluj-Napoca, Romania The level of variation and the pattern of differentiation were studied in two Western Hungarian (Transdanubia: Őrség region) and two Romanian (Transylvanian Basin) populations of Macu- linea nausithous (Dusky Large Blue). The aim was to provide evidence on the genetic differ- entiation of the Transylvanian populations, which were relegated as M. nausithous kijevensis by RÁKOSY et al. (2010). In order to analyse genetic variance enzyme polymorphism was studied at 17 loci. The structure of phenotypic variation was investigated by performing morphomet- ric analyses on 11 traits of the wings. Statistical procedures were chosen so, that the results ob- tained for morphological and genetic data could be compared. The results of all genetic surveys supported the differentiation of the Transylvanian popula- tions from the Western Transdanubian (Őrség) ones. Hence, genetic results supported the existence of differentiation at the subspecies level in M. nausithous. The results of the morphometric analyses, however, were not obvious. In some analyses (phenogram) no clear phenotypic differentiation was observed between the two regions. Nevertheless, the results of hierarchical analysis of variance and Multiple Discriminant Analysis indicated a significant separation of specimens from the two regions. -
TANAP Project's Executive Summary of ESIA and Supporting Environmental and Social Safeguard Documents
TANAP Project’s Executive Summary of ESIA and Supporting Environmental and Social Safeguard Documents 22 July 2016 TANAP DOĞALGAZ İLETİM A.Ş. TANAP Project’s Executive Summary of ESIA and Supporting Environmental and Social Safeguard Documents TABLE OF CONTENTS 1. BRIEF PROJECT DESCRIPTION .......................................................................................... 4 2. LEGAL REQUIREMENTS AND STANDARDS ...................................................................... 7 2.1. KEY LEGAL, POLITICAL AND INSTITUTIONAL FRAMEWORK FOR ESIA ...................... 7 2.2. POLICY AND LEGISLATIVE FRAMEWORK FOR LAND ACQUISITION ............................ 8 3. ENVIRONMENTAL AND SOCIAL RISK MANAGEMENT AND ESMS ............................... 11 3.1. DEVELOPMENT OF THE PROJECT, ROUTE SELECTION .............................................. 11 3.2. ENVIRONMENTAL AND SOCIAL IMPACT ASSESSMENT PROCESS ............................ 15 3.3. ENVIRONMENTAL AND SOCIAL MANAGEMENT SYSTEM (ESMS) ............................... 21 3.3.1. Environmental and Social Management Guidelines for Contractors ............................. 28 3.3.2. Alignment of Environmental and Social Management System Documentation with other Engineering documentation ................................................................................................. 30 4. ENVIRONMENTAL AND SOCIAL IMPACTS ...................................................................... 35 4.1. ENVIRONMENTAL AND SOCIAL IMPACT ASSESSMENT .............................................. -
EIG 8 Autumn 2010 (PDF, 4.0Mb)
NEWSLETTER Issue 8 October 2010 CONTENTS Page Chairman’s Introduction 2&3 Dates for your Diary / EIG Calendar/ Contact Details 4 European Butterflies – the taxonomy update 5&6 Agricultural Change and its implications for Butterflies In Eastern French Pyrenees 7,8,9&10 Monitoring the Sudeten Ringlet in Switzerland 11,12&13 Fundraising Tour to Slovenia (1) 14&15 Fundraising Trip to Slovenia & Orseg (2) 16 EIG Trip to Mt. Phalakron, Greece 17&18 At last, the Macedonian Grayling (Pseudochazara cingowskii) 19&20 Skiathos – Greece 21&22 Finding Apollo in the Julian Alps 23 In search of the Scarce Fritillary 24 Orseg National Park 25&26 The Butterfly Year – The late Butterfly season in Provence(Var) 26 Part 2 of Newsletter We are pleased to include an extract of Bernard Watts ‘European Butterflies a portrait in photographs’ on the Alcon Blue ( Phengaris = Maculinea alcon) This document will be sent as a pdf titled: Part II – Autumn 2010_alcon-brw.pdf 1 INTRODUCTION Editorial As I mentioned in the last newsletter Butterfly Conservation Europe (BCE) has now completed the Red List of European Butterflies using the new standardized IUCN 1 criteria. These are available on the IUCN website See http://ec.europa.eu/environment/nature/conservation/species/redlist or the link on EIG website: http://www.bc-eig.org.uk/Newsletters.html where you can download the Red List Report for free as a .pdf. This massive piece of work was led by Chris van Swaay and is a major achievement for BCE. It covers all butterflies in Europe either in the EU27 countries but also continental Europe which includes Turkey west of the Bosphorus and Russia up to the Urals. -
The Importance of Traditional Agricultural Landscapes for Preventing Species Extinctions
Biodiversity and Conservation (2021) 30:1341–1357 https://doi.org/10.1007/s10531-021-02145-3 ORIGINAL PAPER The importance of traditional agricultural landscapes for preventing species extinctions Ove Eriksson1 Received: 17 August 2020 / Revised: 15 February 2021 / Accepted: 16 February 2021 / Published online: 1 March 2021 © The Author(s) 2021 Abstract The main paradigm for protection of biodiversity, focusing on maintaining or restoring conditions where humans leave no or little impact, risks overlooking anthropogenic land- scapes harboring a rich native biodiversity. An example is northern European agricultural landscapes with traditionally managed semi-natural grasslands harboring an exceptional local richness of many taxa, such as plants, fungi and insects. During the last century these grasslands have declined by more than 95%, i.e. in the same magnitude as other, interna- tionally more recognized declines of natural habitats. In this study, data from the Swedish Red List was used to calculate tentative extinction rates for vascular plants, insects (Lepi- doptera, Coleoptera, Hymenoptera) and fungi, given a scenario where such landscapes would vanish. Conservative estimates suggest that abandonment of traditional management in these landscapes would result in elevated extinction rates in all these taxa, between two and three orders of magnitude higher than global background extinction rates. It is sug- gested that the species richness in these landscapes refects a species pool from Pleistocene herbivore-structured environments, which, after the extinction of the Pleistocene mega- fauna, was rescued by the introduction of pre-historic agriculture. Maintaining traditionally managed agricultural landscapes is of paramount importance to prevent species loss. There is no inherent confict between preservation of anthropogenic landscapes and remain- ing ‘wild’ areas, but valuating also anthropogenic landscapes is essential for biodiversity conservation.