Maintaining Standing Stones Benefits Biodiversity in Lowland Heathland

Total Page:16

File Type:pdf, Size:1020Kb

Maintaining Standing Stones Benefits Biodiversity in Lowland Heathland Open Research Online The Open University’s repository of research publications and other research outputs Maintaining standing stones benefits biodiversity in lowland heathland Journal Item How to cite: Shepheard-Walwyn, Emma and Bhagwat, Shonil A. (2018). Maintaining standing stones benefits biodiversity in lowland heathland. Oryx, 52(2) pp. 240–249. For guidance on citations see FAQs. c 2018 Fauna Flora International https://creativecommons.org/licenses/by-nc-nd/4.0/ Version: Version of Record Link(s) to article on publisher’s website: http://dx.doi.org/doi:10.1017/S0030605317001442 Copyright and Moral Rights for the articles on this site are retained by the individual authors and/or other copyright owners. For more information on Open Research Online’s data policy on reuse of materials please consult the policies page. oro.open.ac.uk Maintaining standing stones benefits biodiversity in lowland heathland E MMA S HEPHEARD-WALWYN and S HONIL A. BHAGWAT Abstract The exploitation of natural resources by people some cases anthropogenic influence can produce new habi- generally has detrimental effects on nature but in some tats and diversity within the landscape, resulting in a more cases anthropogenic activities can result in changes to the biodiverse environment (Jones, ; Bhagwat et al., ; natural environment that produce new habitats and increase Anthwal et al., ). Many ecosystems have been altered biodiversity. Understanding and supporting such cultural historically by human activities, and areas previously con- aspects of land use is an important part of effective conser- sidered to be pristine have been found to have been sites vation strategies. The UK has a range of cultural landscapes of historical large-scale anthropogenic changes (Moran, that contribute to the landscape matrix and are often im- ). Understanding and supporting the cultural aspects portant for biodiversity. However, little research has been of land use is therefore, in some cases, an important part conducted on the relationship between various types of cul- of an effective conservation strategy. tural landscapes or their effects on biodiversity. We exam- Anthropogenic activities in the natural environment re- ined the interaction between semi-natural sacred sites and sult in cultural landscapes (Jones, ; Agnoletti, ), lowland heathland in Cornwall, and the contribution these which can provide information about the way in which na- sites make to the overall biodiversity within the habitat. We ture responds to human influences, and how anthropogenic found that semi-natural sacred sites had significantly higher use can help to promote biodiversity (Agnoletti, ; Willis levels of biodiversity compared to surrounding heathland; et al., ; Anthwal et al., ). Globally there are exam- the existence and use of the sites created new and important ples of both positive and negative influences of people’s habitats for rare and threatened heathland species; and the actions on the natural environment; cultural landscapes, spiritual and cultural use of the sites aids the management of from single prayer trees to the extensive agricultural land- heathland. Promoting the use of semi-natural sacred sites scapes of Europe, are a product of such actions (Jones, could therefore contribute to biodiversity conservation. ; Moran, ; Bhagwat et al., ). Many cultural Furthermore, the cultural and spiritual importance of such landscapes help to contribute towards the heterogeneity of sites potentially increases the availability of volunteer re- the landscape matrix and provide unique opportunities for sources for their management. We highlight the importance biodiversity conservation (Agnoletti, ; Bhagwat et al., of an integrated management approach for achieving effect- ; Dudley et al., ). ive biodiversity conservation in areas containing multiple There have been studies of the contributions of various types of cultural landscapes. types of cultural landscapes in the landscape matrix (Bhagwat et al., ), and the importance of the variation Keywords Biodiversity, Biodiversity Action Plan habitats, of habitats within particular cultural landscapes (Kirby, Cornwall, cultural landscape, heathland, semi-natural ; Key, ; Price, ). However, there has been less sacred sites, standing stones, UK focus on habitat heterogeneity within cultural landscapes, Supplementary material for this article is available at and no previous research has investigated directly the effects https://doi.org/./S of sacred sites on biodiversity in lowland heathland. There is a variety of cultural landscapes in the UK, in- cluding agricultural landscapes, heathland and moorland, managed forests, urban green spaces, and sacred sites. Introduction Many sacred sites in the UK can be categorized as semi- natural sacred sites because of their presence in otherwise he detrimental effects of human activities on nature highly anthropogenic landscapes. Here we examine semi- Thave prompted many conservation practitioners to natural sacred sites in lowland heathland, and the contribu- attempt to keep nature separate from people. However, in tion these sites make to biodiversity within the heathland habitat. We address five questions: () What is the extent and spatial distribution of known semi-natural sacred sites EMMA SHEPHEARD-WALWYN (Corresponding author) The White House Cottage, within lowland heathland in Cornwall? () What are the dif- Stockland, Devon, EX14 9DS, UK. E-mail [email protected] ferences in community structure and composition between SHONIL A. BHAGWAT Department of Geography, Open Space Research Centre, The Open University, UK these sites and the surrounding heathland? ( ) How does the Received January . Revision requested May . use of semi-natural sacred sites affect the structure and com- Accepted September . First published online February . position of surrounding habitat, and what impact does this Oryx, 2018, 52(2), 240–249 © 2018 Fauna & Flora International doi:10.1017/S0030605317001442 Downloaded from https://www.cambridge.org/core. Open University Library, on 24 May 2018 at 11:45:43, subject to the Cambridge Core terms of use, available at https://www.cambridge.org/core/terms. https://doi.org/10.1017/S0030605317001442 Standing stones benefit biodiversity 241 have on biodiversity? () What are the differences in habitat significance, and are categorized as semi-natural sacred diversity between semi-natural sacred sites and heathland? sites. They harbour natural habitats that have been altered () What contribution do semi-natural sacred sites make through extensive human influence over time (Bhagwat & to the biodiversity of the heathland? Rutte, ; Anthwal et al., ; Shepheard-Walwyn, ), and they have been found to support biodiversity that differs from that of surrounding habitats (Bhagwat & Study area Rutte, ; Dudley et al., ). We focus on five types of This study was conducted in the region of Penwith, West stone monuments (standing stones, stone circles, cairns, Cornwall, in south-west England (Fig. ). The west of quoits and tumuli) regarded as sacred by Pagan worship- Penwith is an Environmentally Sensitive Area (Natural pers, and consider sites: semi-natural sacred sites England, ). (Table ) and (paired) non-sacred sites within lowland heathland. Lowland heathland The co-existence of Neolithic monuments with heathland Lowland heathland is an anthropogenic landscape that oc- curs up to m altitude. Most heathland requires active Lowland heathland in Western Europe is a highly managed management to prevent trees becoming dominant in the habitat, and without management it would return to forest landscape (Price, ; D. Allen, , pers. comm.). (Price, ). In Britain, Neolithic monuments and stone Twenty percent of all remaining lowland heathland is in structures are embedded within this habitat. Archaeological the UK, and the majority of this is in the south of evidence suggests that Neolithic cultures practised farming England (Price, ). Lowland heathlands are vital to and pastoralism, which are associated with widespread clear- many rare species, such as the smooth snake Coronella aus- ing of forest and expansion of farmland (Heil & Aerts, ; triaca, the nightjar Caprimulgus europaeus and the ladybird Gaillard et al., ). The sacredness of the stone structures spider Eresus sandaliatus (Forestry Commission, ), and therefore lies in the stones rather than in the land per se, so therefore the management of these lands is vital to the pro- management of heathland and maintenance of sacred stone tection of much of the UK’s biodiversity (Kirby, ;Key, structures would have coexisted in Neolithic times. ; Price, ). An important aspect of heathlands is the variation of structures and habitats within them (Kirby, Methods ;Key,; Price, ), including areas dominated by gorse Ulex and heather Calluna, areas of open grass We used a combination of fieldwork and a geographical and bare soil, and wet areas including boggy patches or information system to map semi-natural sacred sites in open water (Hantsweb, ). In addition, footpaths, bare lowland heathland and analyse their distribution in the ground, rocky structures, artificial features and ruins can landscape, and the differences in vegetation, habitat and all provide heterogeneity within the landscape matrix, biodiversity between paired sacred and non-sacred sites. which is essential for biodiversity (Kirby, ;Key,; Price, ). Selection of study sites Neolithic stone monuments To select the study sites we conducted analysis using ArcGIS v. , ArcMap v. and
Recommended publications
  • Trunk Road Estate Biodiversity Action Plan
    Home Welsh Assembly Government Trunk Road Estate Biodiversity Action Plan 2004-2014 If you have any comments on this document, its contents, or its links to other sites, please send them by post to: Environmental Science Advisor, Transport Directorate, Welsh Assembly Government, Cathays Park, Cardiff CF10 3NQ or by email to [email protected] The same contact point can be used to report sightings of wildlife relating to the Trunk Road and Motorway network. Prepared by on behalf of the Welsh Assembly Government ISBN 0 7504 3243 8 JANUARY 2004 ©Crown copyright 2004 Home Contents Foreword by Minister for Economic Development and Transport 4 Executive Summary 5 How to use this document 8 Introduction 9 Background to biodiversity in the UK 10 Background to biodiversity in Wales 12 The Trunk Road Estate 13 Existing guidance and advice 16 TREBAP development 19 Delivery 23 Links to other organisations 26 The Plans 27 Glossary 129 Bibliography and useful references 134 Other references 138 Acknowledgements 139 3 Contents Foreword FOREWORD BY THE MINISTER FOR ECONOMIC DEVELOPMENT AND TRANSPORT The publication of this Action Plan is both a recognition of the way the Assembly Government has been taking forward biodiversity and an opportunity for the Transport Directorate to continue to contribute to the wealth of biodiversity that occurs in Wales. Getting the right balance between the needs of our society for road-based transport, and the effects of the Assembly’s road network on our wildlife is a complex and often controversial issue. The Plan itself is designed to both challenge and inspire those who work with the Directorate on the National Assembly’s road network – and, as importantly, to challenge those of us who use the network to think more about the wildlife there.
    [Show full text]
  • BSBI SCOTTISH KEWSIETTER Lumber 2 Summer 1980
    B.S.B. I. SCOTTISH NEWSLETTER BSBI SCOTTISH KEWSIETTER lumber 2 Summer 1980 COOTEOTS Editorial 2 Woodsia ilvensis in the Itoffat area 2 Ulex gallii in the far north of Scotland - E.R.Bullard 5 Cirsium wankelii in Argyll, v.c.98 - A.G*Kenneth 6 Discovery of Schoenus ferrugineous as a native British plant - R.A.H. Smith 7 Rosa arvensis in Scotland - O.M. Stewart 7 The year of the Dandelion - G.H. Ballantyne 8 •The Flora of Kintyre1. Review - P. Macpherson 9 Liaison between the BSBI and Nature Conservancy Council 10 HCC Assistant Regional Officers 10 Calamagrostis - 0«M. Stewart 13 Spiraea salicifolia group - A.J, Silverside 13 % Chairman's Letter 14 Flora of Uig (Lewis) 15 Cover Illustration - Woodsia ilvensis by Olga M. Stewart 1 EDITORIAL staff, who is the author of a recent report on the subjecto * We hope that this, the second number of the newsletter, meets with the approval of our readers, but its success The report is divided into four parts - Geographical can only be judged by our receiving your comments and distribution? Ecological aspects? Past and Present Status constructive criticism, so please let us know what you in the Moffat Hills? and Conservation in Britain. The think of our efforts® world, European and British distribution is discussed in Our cover illustration, for which we are once again general terms, with appropriate maps. These show W. indebted to Mrs Olga Stewart, has been chosen as an ilvensis to be a fern of the i'orth Temperate zone, con­ fined to the Arctic and mountainous regions, extending as accompaniment to the item on Woodsia ilvensis.
    [Show full text]
  • A Literature Review of Urban Effects on Lowland Heaths and Their Wildlife
    Report Number 623 A literature review of urban effects on lowland heaths and their wildlife English Nature Research Reports working today for nature tomorrow English Nature Research Reports Number 623 A literature review of urban effects on lowland heaths and their wildlife J C Underhill-Day RSPB, Syldata Arne, Wareham Dorset BH20 5BJ Telephone: 01929 550969 email: [email protected] You may reproduce as many additional copies of this report as you like, provided such copies stipulate that copyright remains with English Nature, Northminster House, Peterborough PE1 1UA ISSN 0967-876X © Copyright English Nature 2005 Executive summary Introduction Heather clad lowland heath developed on light, freely draining, acid soils following prehistoric woodland clearance, and down the centuries, has been kept open by grazing, burning and cutting. As the economic value of these uses declined, considerable areas of heath were lost to agriculture, forestry, housing, roads, mineral working and other uses, and today, much of what is left is adjacent to built up areas, especially in Dorset. These lowland heathland fragments can be found across much of southern England on suitable soils. Much of the research on heathlands over the last twenty years has concentrated on the Dorset heaths, which are now almost all SSSIs and mostly within the Dorset Heathland SPA. While this report reflects the bias in the literature towards work in Dorset, the results have wide applicability to urban heathlands that are accessed by the surrounding urban populations for amenity and recreation whether in Dorset or elsewhere. This urban public access places considerable pressures on the heaths, for example through disturbance, wild fires, trampling, predation by domestic pets, pollution and enrichment.
    [Show full text]
  • Oberholzeria (Fabaceae Subfam. Faboideae), a New Monotypic Legume Genus from Namibia
    RESEARCH ARTICLE Oberholzeria (Fabaceae subfam. Faboideae), a New Monotypic Legume Genus from Namibia Wessel Swanepoel1,2*, M. Marianne le Roux3¤, Martin F. Wojciechowski4, Abraham E. van Wyk2 1 Independent Researcher, Windhoek, Namibia, 2 H. G. W. J. Schweickerdt Herbarium, Department of Plant Science, University of Pretoria, Pretoria, South Africa, 3 Department of Botany and Plant Biotechnology, University of Johannesburg, Johannesburg, South Africa, 4 School of Life Sciences, Arizona a11111 State University, Tempe, Arizona, United States of America ¤ Current address: South African National Biodiversity Institute, Pretoria, South Africa * [email protected] Abstract OPEN ACCESS Oberholzeria etendekaensis, a succulent biennial or short-lived perennial shrublet is de- Citation: Swanepoel W, le Roux MM, Wojciechowski scribed as a new species, and a new monotypic genus. Discovered in 2012, it is a rare spe- MF, van Wyk AE (2015) Oberholzeria (Fabaceae subfam. Faboideae), a New Monotypic Legume cies known only from a single locality in the Kaokoveld Centre of Plant Endemism, north- Genus from Namibia. PLoS ONE 10(3): e0122080. western Namibia. Phylogenetic analyses of molecular sequence data from the plastid matK doi:10.1371/journal.pone.0122080 gene resolves Oberholzeria as the sister group to the Genisteae clade while data from the Academic Editor: Maharaj K Pandit, University of nuclear rDNA ITS region showed that it is sister to a clade comprising both the Crotalarieae Delhi, INDIA and Genisteae clades. Morphological characters diagnostic of the new genus include: 1) Received: October 3, 2014 succulent stems with woody remains; 2) pinnately trifoliolate, fleshy leaves; 3) monadel- Accepted: February 2, 2015 phous stamens in a sheath that is fused above; 4) dimorphic anthers with five long, basifixed anthers alternating with five short, dorsifixed anthers, and 5) pendent, membranous, one- Published: March 27, 2015 seeded, laterally flattened, slightly inflated but indehiscent fruits.
    [Show full text]
  • 0376761 STC Biodiversity Action Plan
    Shwe Taung Cement Co., Ltd. Cement and Coal Mine Concessions Biodiversity Action Plan October 2018 V.1.5 www.erm.com The business of sustainability FINAL REPORT Shwe Taung Cement Co., Ltd. Cement and Coal Mine Concessions Biodiversity Action Plan October 2018 Reference: DRAFT STC BAP.docx v.1.5 Environmental Resources Management Siam Co. Ltd 179 Bangkok City Tower 24th Floor, South Sathorn Road Thungmahamek, Sathorn Bangkok 10120 Thailand www.erm.com Review Log Date Rev. Description Prepared Checked Approved (dd/mm/yyyy) 1.1 14/09/2017 Response to IFC comments on draft SMC/DN DN PT 1.2 06/11/2017 Response to STC comments on draft DN DN PT 1.3 22/12/2017 Response to consultation comments DN DN PT Response to consultation comments on 1.4 01/03/2018 DN DN PT draft 1.5 10/10/2018 Response to comments from FFI DN DN PT Revision Log Date Revised Detail Rev. (dd/mm/yyyy) Item Page Article Description Contents INTRODUCTION 5 STRUCTURE OF THIS BAP 5 RELEVANT ESAP ACTIONS 5 CONSULTATION 6 INSTITUTIONAL FRAMEWORK 7 RELEVANT INTERNATIONAL POLICY FRAMEWORKS 8 RELEVANT INTERNATIONAL AGREEMENTS/COMMITMENTS 8 RELEVANT LAWS IN MYANMAR 9 STC BIODIVERSITY AND ECOSYSTEM SERVICES POLICY 14 SCOPE OF POLICY 14 POLICY REQUIREMENTS 15 LEGAL AND OTHER REQUIREMENTS 15 OBJECTIVES AND TARGETS 15 OPERATIONAL CONTROL 16 MONITORING AND EVALUATION 17 STC ZERO TOLERANCE POLICY ON POSSESSION OF WILDLIFE AND FOREST RESOURCES 18 POLICY REQUIREMENTS 18 OPERATIONAL CONTROL 18 STC ANTI-ILLEGAL LOGGING POLICY 20 POLICY REQUIREMENTS 20 OPERATIONAL CONTROL 20 BIODIVERSITY OFFSET
    [Show full text]
  • Sheep and Goat Grazing Effects on Three Atlantic Heathland Types Berta M
    Rangeland Ecol Manage 62:119–126 | March 2009 Sheep and Goat Grazing Effects on Three Atlantic Heathland Types Berta M. Ja´uregui,1 Urcesino Garcı´a,2 Koldo Osoro,3 and Rafael Celaya1 Authors are 1Research Associates, 2Experimental Farm Manager, and 3Research Head, Animal Production Systems Department, Servicio Regional de Investigacio´n y Desarrollo Agroalimentario, Apdo. 13, 33300 Villaviciosa, Asturias, Spain Abstract Heathlands in the northwest of Spain have been traditionally used by domestic herbivores as a food resource. However, their abandonment in the past decades has promoted a high incidence of wildfires, threatening biodiversity. Sheep and goats exhibit different grazing behavior, affecting rangelands dynamics in a different way, but the botanical and structural composition may also affect such dynamics. The aim of this article was to compare the grazing effects of sheep and goats on three different heathland types: previously burned grass- or gorse (Ulex gallii Planchon)-dominated and unburned heather (Erica spp.)- dominated shrublands. Two grazing treatments (sheep or goats) were applied in each vegetation type in a factorial design with two replicates (12 experimental plots). A small fenced area was excluded from grazing in each plot (control treatment). The experiment was carried out from 2003 to 2006, and the grazing season extended from May to October–November. Plant cover, canopy height, and phytomass amount and composition were assessed in each plot. Results showed that goats controlled shrub encroachment, phytomass accumulation, and canopy height more than sheep in either burned grass– and gorse– and unburned heather–dominated shrublands. It was accompanied by a higher increase of herbaceous species under goat grazing.
    [Show full text]
  • 2017 City of York Biodiversity Action Plan
    CITY OF YORK Local Biodiversity Action Plan 2017 City of York Local Biodiversity Action Plan - Executive Summary What is biodiversity and why is it important? Biodiversity is the variety of all species of plant and animal life on earth, and the places in which they live. Biodiversity has its own intrinsic value but is also provides us with a wide range of essential goods and services such as such as food, fresh water and clean air, natural flood and climate regulation and pollination of crops, but also less obvious services such as benefits to our health and wellbeing and providing a sense of place. We are experiencing global declines in biodiversity, and the goods and services which it provides are consistently undervalued. Efforts to protect and enhance biodiversity need to be significantly increased. The Biodiversity of the City of York The City of York area is a special place not only for its history, buildings and archaeology but also for its wildlife. York Minister is an 800 year old jewel in the historical crown of the city, but we also have our natural gems as well. York supports species and habitats which are of national, regional and local conservation importance including the endangered Tansy Beetle which until 2014 was known only to occur along stretches of the River Ouse around York and Selby; ancient flood meadows of which c.9-10% of the national resource occurs in York; populations of Otters and Water Voles on the River Ouse, River Foss and their tributaries; the country’s most northerly example of extensive lowland heath at Strensall Common; and internationally important populations of wetland birds in the Lower Derwent Valley.
    [Show full text]
  • Guidelines for Appropriate Uses of Iucn Red List Data
    GUIDELINES FOR APPROPRIATE USES OF IUCN RED LIST DATA Incorporating, as Annexes, the 1) Guidelines for Reporting on Proportion Threatened (ver. 1.1); 2) Guidelines on Scientific Collecting of Threatened Species (ver. 1.0); and 3) Guidelines for the Appropriate Use of the IUCN Red List by Business (ver. 1.0) Version 3.0 (October 2016) Citation: IUCN. 2016. Guidelines for appropriate uses of IUCN Red List Data. Incorporating, as Annexes, the 1) Guidelines for Reporting on Proportion Threatened (ver. 1.1); 2) Guidelines on Scientific Collecting of Threatened Species (ver. 1.0); and 3) Guidelines for the Appropriate Use of the IUCN Red List by Business (ver. 1.0). Version 3.0. Adopted by the IUCN Red List Committee. THE IUCN RED LIST OF THREATENED SPECIES™ GUIDELINES FOR APPROPRIATE USES OF RED LIST DATA The IUCN Red List of Threatened Species™ is the world’s most comprehensive data resource on the status of species, containing information and status assessments on over 80,000 species of animals, plants and fungi. As well as measuring the extinction risk faced by each species, the IUCN Red List includes detailed species-specific information on distribution, threats, conservation measures, and other relevant factors. The IUCN Red List of Threatened Species™ is increasingly used by scientists, governments, NGOs, businesses, and civil society for a wide variety of purposes. These Guidelines are designed to encourage and facilitate the use of IUCN Red List data and information to tackle a broad range of important conservation issues. These Guidelines give a brief introduction to The IUCN Red List of Threatened Species™ (hereafter called the IUCN Red List), the Red List Categories and Criteria, and the Red List Assessment process, followed by some key facts that all Red List users need to know to maximally take advantage of this resource.
    [Show full text]
  • Invitation to Join the Biodiversity Disclosure Project
    INVITATION TO JOIN THE BIODIVERSITY DISCLOSURE PROJECT A STUDY OF THE BIODIVERSITY PERFORMANCE OF SOUTH AFRICAN COMPANIES ENDANGERED ENDANGERED WILDLIFE TRUST WILDLIFE TRUST Protecting forever, together. Protecting forever, together. STRATEGIC PARTNERSHIP 1 BIODIVERSITY MATTERS TO BUSINESS What is biodiversity? The international Convention on Biological Diversity (CBD) defines “biodiversity” as the variability among living organisms from all sources including, inter alia, terrestrial, marine and other aquatic ecosystems and the ecological complexes of which they are part. This includes diversity within species, between species and of ecosystems. Biodiversity produces a wide variety of services on which businesses depend. Examples include crop pollination, water filtration, flood attenuation, erosion control and many others. Business- es are critically dependent on these ecosystem services to produce their goods and services and would not be able to operate without them. However, biodiversity is under severe threat globally and the private sector is one of the primary drivers of its degradation and loss. Increasingly, biodiversity is being recognised internationally and nationally as a key part of the sustainable development agenda. The Sustainable Development Goals (SDGs) prioritise the connection between environment and development by integrating sustainability in all 17 of the Global Goals. More specifically, SDG 14 “life below water” and SDG 15 “life on land” make bio- diversity a top priority on the international development agenda. Healthy ecosystems are rec- ognised as being at the foundation of poverty reduction and sustainable development. In addition, governments around the world have adopted the Strategic Plan for Biodiversity 2011–2020. This plan and its 20 Aichi Biodiversity Targets represent a roadmap towards a sus- tainable future and are aligned with the Sustainable Development Goals.
    [Show full text]
  • Ulex-Europaeus EN Icon.Pdf
    Appendix A Harmonia+PL – procedure for negative impact risk assessment for invasive alien species and potentially invasive alien species in Poland QUESTIONNAIRE A0 | Context Questions from this module identify the assessor and the biological, geographical & social context of the assessment. a01. Name(s) of the assessor(s): first name and family name 1. Agnieszka Popiela 2. Zbigniew Sobisz 3. Teresa Nowak acomm01. Comments: degree affiliation assessment date (1) prof. dr hab. Department of Botany and Nature Conservation, 14-01-2018 Faculty of Biology, University of Szczecin (2) dr hab. Department of Botany and Nature Protection, Institute 21-01-2018 of Biology and Environmental Protection, Pomeranian University, Słupsk, Poland (3) dr Faculty of Biology and Environmental Protection, 27-01-2018 University of Silesia in Katowice a02. Name(s) of the species under assessment: Polish name: Kolcolist zachodni Latin name: Ulex europaeus L. English name: Common gorse acomm02. Comments: Latin names are reported on the basis of The Plant List database (2013 – B). The Polish name is quoted according to a local report concerning the nomenclature of Polish flora (Mirek et al. 2002 – P), and the English common names – according to the Invasive Species Compendium database (CABI 2017 – B). There are many more synonyms for the Latin names than reported below (The Plant List 2013 – B): Ulex floridus Salisb., Ulex hibernicus G.Don, Ulex major Thore, Ulex opistholepis Webb, Ulex strictus J.Mackay, Ulex vernalis Thore. 13 species of the Ulex genus, native for southern Europe and northern Africa are known, however the taxonomy of the genus has not been sufficiently known yet (CABI 2017 – B).
    [Show full text]
  • Plant List for VC54, North Lincolnshire
    Plant List for Vice-county 54, North Lincolnshire 3 Vc61 SE TA 2 Vc63 1 SE TA SK NORTH LINCOLNSHIRE TF 9 8 Vc54 Vc56 7 6 5 Vc53 4 3 SK TF 6 7 8 9 1 2 3 4 5 6 Paul Kirby, 31/01/2017 Plant list for Vice-county 54, North Lincolnshire CONTENTS Introduction Page 1 - 50 Main Table 51 - 64 Summary Tables Red Listed taxa recorded between 2000 & 2017 51 Table 2 Threatened: Critically Endangered & Endangered 52 Table 3 Threatened: Vulnerable 53 Table 4 Near Threatened Nationally Rare & Scarce taxa recorded between 2000 & 2017 54 Table 5 Rare 55 - 56 Table 6 Scarce Vc54 Rare & Scarce taxa recorded between 2000 & 2017 57 - 59 Table 7 Rare 60 - 61 Table 8 Scarce Natives & Archaeophytes extinct & thought to be extinct in Vc54 62 - 64 Table 9 Extinct Plant list for Vice-county 54, North Lincolnshire The main table details all the Vascular Plant & Stonewort taxa with records on the MapMate botanical database for Vc54 at the end of January 2017. The table comprises: Column 1 Taxon and Authority 2 Common Name 3 Total number of records for the taxon on the database at 31/01/2017 4 Year of first record 5 Year of latest record 6 Number of hectads with records before 1/01/2000 7 Number of hectads with records between 1/01/2000 & 31/01/2017 8 Number of tetrads with records between 1/01/2000 & 31/01/2017 9 Comment & Conservation status of the taxon in Vc54 10 Conservation status of the taxon in the UK A hectad is a 10km.
    [Show full text]
  • EU BIODIVERSITY ACTION PLAN: 2010 Assessment
    EU BIODIVERSITY ACTION PLAN: 2010 Assessment Biodiversity Action Plan: 2010 Assessment 1 Europe Direct is a service to help you find answers to your questions about the European Union Freephone number (*): 00 800 6 7 8 9 10 11 (*) Certain mobile telephone operators do not allow access to 00 800 numbers or these calls may be billed More information on the European Union is available on the Internet (http://europa.eu) Cataloguing data can be found at the end of this publication Luxembourg: Publications Office of the European Union, 2010 ISBN 978-92-79-16248-0 doi : 10.2779/42306 © European Union, 2010 Reproduction is authorised provided the source is acknowledged Printed in Belgium Printed on recycled paper that has been awarded the eu eco-label for graphic paper (http://ec.europa.eu/ecolabel) 2 Biodiversity Action Plan: 2010 Assessment Contents Introduction ..................................................................................................................................................... 5 Why is biodiversity important? ..................................................................................................................... 7 The state of biodiversity in the EU ................................................................................................................ 9 The 2010 Assessment of the EU Biodiversity Action Plan ......................................................................... 13 Objective 1: To safeguard the EU’s most important habitats and species ................................................................
    [Show full text]