Eurasian Beaver (Castor Fiber) Former and Proposed Reintroductions in Romania a Comparative Attitudinal Study

Total Page:16

File Type:pdf, Size:1020Kb

Eurasian Beaver (Castor Fiber) Former and Proposed Reintroductions in Romania a Comparative Attitudinal Study Eurasian Beaver (Castor fiber) Former and Proposed Reintroductions in Romania A Comparative Attitudinal Study Alexandra Cristiana Panait MSc. in Conservation Science 4th of September 2012 A thesis submitted in partial fulfilment of the requirements for the degree of Master of Science and Diploma of Imperial College THE SIGNED DECLARATION OF OWN WORK I declare that this thesis 'European Beaver (Castor fiber) Former and Proposed Reintroductions in Romania - A Comparative Attitudinal Study' is entirely my own work and that where material could be construed as the work of others, it is fully cited and referenced, and/or with appropriate acknowledgement given. Signature ………………………… Alexandra Cristiana Panait Name of Supervisors: Professor John Fa & Professor Stephen Redpath 2 CONTENTS THE SIGNED DECLARATION OF OWN WORK ______________________________________________________________ 1 CONTENTS ______________________________________________________________________________________________________ 3 LIST OF FIGURES _______________________________________________________________________________________________ 5 LIST OF TABLES ________________________________________________________________________________________________ 6 ACRONYMS ______________________________________________________________________________________________________ 6 ABSTRACT ______________________________________________________________________________________________________ 7 WORD COUNT __________________________________________________________________________________________________ 7 ACKNOWLEDGMENTS _________________________________________________________________________________________ 8 1 INTRODUCTION _________________________________________________________________________________________ 9 1.1 THE CONTEXT _________________________________________________________________________________________ 9 1.2 FRAMING THE ISSUE – POLICY TERMS ____________________________________________________________ 10 1.3 SCARCITY OF DATA _________________________________________________________________________________ 12 1.4 AIMS, OBJECTIVES AND HYPOTHESIS _____________________________________________________________ 13 1.5 OVERVIEW OF THE THESIS STRUCTURE __________________________________________________________ 14 2 BACKGROUND _________________________________________________________________________________________ 16 2.1 ATTITUDES TOWARDS THE ENVIRONMENT AND ITS CURRENT STATE - A POLITICAL REGIME PERSPECTIVE ____________________________________________________________________________________ 16 2.1.1 A world defined by a dichotomy ______________________________________________________________ 16 2.1.2 Communist transformation and degraded environments? __________________________________ 17 2.1.3 Democratic restoration and restored habitats? ______________________________________________ 17 2.1.4 What was left behind and what can be done? The Danube Delta case study ______________ 18 2.1.4.1 Economically-politically driven ecosystem engineering _______________________________________ 18 2.1.4.2 Present ecosystem state: water, soil pollution levels and biodiversity _______________________ 19 2.1.4.3 The theory and practice of implementing conservation _______________________________________ 20 2.2 INTERVENTION AGAIN? WETLAND RESTORATION______________________________________________ 21 2.2.1 The relationship between restoration and reintroduction __________________________________ 21 2.2.2 Reintroduction in the historic ranges: Covasna and self introduction on the Danube River and Delta ________________________________________________________________________________________________ 22 2.2.3 Beaver’s work in progress _____________________________________________________________________ 24 2.3 PERCEPTIONS TOWARDS BEAVERS THROUGH TIME: FROM ECONOMICAL DRIVE ALMOST EXTINCTION TO ECO (-NOMICAL/ -LOGICAL) DRIVEN SUSTAINABILITY ____________________________ 26 2.3.1 Dress to kill: the fur industry __________________________________________________________________ 26 2.3.2 Fashionable changes: first shifts in attitudes, behaviour and protection laws _____________ 26 2.3.3 Is it possible to wear two hats in 21th century: participatory management in ecosystem restoration? _____________________________________________________________________________________________ 27 2.3.3.1 Restoration - beaver ecosystem services relationship _________________________________________ 27 2.3.3.2 Attitudes measurement as predictors for success or failure __________________________________ 27 3 METHODS _______________________________________________________________________________________________ 30 3.1 RESEARCH APPROACH______________________________________________________________________________ 30 3.1.1 The Ethics Behind the Scientific Methodology _______________________________________________ 30 3.1.2 Objectives reflection in the research approach ______________________________________________ 31 3.2 THE RESEARCH METHODS SUITED FOR THE RESEARCH APPROACH _____________________________ 31 3.2.1 An Overview____________________________________________________________________________________ 31 3.2.2 The Questionnaires ____________________________________________________________________________ 32 3.2.2.1 Questionnaire choice of method _________________________________________________________________ 32 3.2.2.2 Questionnaire structure design __________________________________________________________________ 32 3.2.2.3 Questionnaire Data Collection __________________________________________________________________ 35 3.2.3 The Focus Group _______________________________________________________________________________ 37 3.2.3.1 Choice of method _________________________________________________________________________________ 37 3.2.3.2 Structure design __________________________________________________________________________________ 37 3.2.3.3 Data collection ____________________________________________________________________________________ 38 3 3.3 DATA PROCESSING AND ANALYSIS _________________________________________________________________39 3.3.1 The Questionnaires: Statistical Analysis ______________________________________________________ 39 3.3.1.1 Setting up the data for the analysis: Coding and Code Books __________________________________ 39 3.3.1.2 Constructing scores for measuring knowledge _________________________________________________ 39 3.3.1.3 Statistical tests ____________________________________________________________________________________ 39 3.3.2 The Focus Group: Conversation Analysis ______________________________________________________ 40 4 RESULTS ________________________________________________________________________________________________ 41 4.1 GENERAL DESCRIPTION AND TOTAL NUMBER OF COLLECTED QUESTIONNAIRES ___________41 4.2 COMPARATIVE SOCIO-DEMOGRAPHICS RESULTS ________________________________________________41 4.3 BEAVER’S BEHAVIOUR GENERAL KNOWLEDGE SCORES _________________________________________42 4.4 BEAVER’S CONSERVATION STATUS & LEGISLATION KNOWLEDGE SCORES ___________________44 4.5 REPORTED DAMAGES CAUSED BY WILD ANIMALS _______________________________________________46 4.6 ACTIVITIES RELATED TO THE NATURAL ENVIRONMENT _______________________________________48 4.6.1 Outdoor activities ______________________________________________________________________________ 48 4.6.2 Environment related activities ________________________________________________________________ 48 4.7 THE ATTITUDES ______________________________________________________________________________________49 4.7.1 Constructing scales for attitudinal variables _________________________________________________ 51 4.7.2 Factors correlated with the attitudes scores __________________________________________________ 53 4.7.3 Factors significantly associated with attitudes scores ________________________________________ 55 4.7.3.1 The analysis for Covasna county sample ________________________________________________________ 55 4.7.3.2 The analysis for Sfantu Gheorghe village sample _______________________________________________ 57 5 DISCUSSION ____________________________________________________________________________________________ 60 5.1 THE TYPOLOGY OF BASIC WILDLIFE VALUES SHOW MIXED ATTITUDES TOWARDS BEAVER REINTRODUCTIONS 60 5.1.1 Certain demographics descriptors are relevant for describing attitudes ____________________ 60 5.1.2 Objective 1: There is no difference between the levels of Beaver species knowledge in the study areas and they moderately relate to attitudes ___________________________________________________ 62 5.1.3 Objective 2: There is a significant difference between the levels of knowledge about the Beaver species conservation status and the legislation protecting the species in the study areas. __ 63 5.1.4 Objective 3: Human-wildlife conflict levels differ significantly between the two Romanian areas 63 5.1.5 Objective 4: Civic implications, voluntary work and outdoor activities levels of each sample and comparison between them __________________________________________________________________________ 64 5.2 LIMITATIONS OF THE STUDY _____________________________________________________________________________65 5.3 RESEARCH LESSONS LEARNT AND SUGGESTED RECOMMENDATIONS AS DERIVED FROM THE STUDIED ATTITUDES FROM COVASNA COUNTY _______________________________________________________________________________________66 REFERENCES _________________________________________________________________________________________________
Recommended publications
  • Beavers and Fish
    Beavers and Fish A: Introduction Land and freshwater fishery managers have become increasingly concerned following the announcement of a licensed trial to introduce European Beavers to Knapdale in Argyll. Their concern arises around the widespread interpretation by those who campaign for Beaver introductions to Britain that this licence heralds the return of Beavers to the British countryside; alongside which there have been repeated and consistent claims that Beavers will only be good, especially for biodiversity, and that there will be no adverse effects. This is despite the acknowledged fact that Beavers make profound changes to the ecosystems in which they live by making dams in watercourses; indeed this is a much cited benefit. The simplistic arguments that are presented to support the introduction of Beavers ignore widespread evidence that Beavers cause considerable damage both to the rivers and streams that they dam and also to the surrounding land. Much of this evidence is anecdotal but more is recorded in the scientific literature. Normally, when any major change to the English, Welsh or Scottish countryside is proposed, government agencies and others rightly demand appropriate assessments of the likely effects with particular reference to the literature, particularly where rivers or land under conservation designations such as SSSI (Site of Special Scientific Interest) or SAC (Special Area of Conservation) are involved. With Beaver introduction this process has been ignored; either no appropriate assessment has been made or none has been made public. This leaves a suspicion to many that the evidence may in fact be disadvantageous to the proposed introductions and that it is being suppressed.
    [Show full text]
  • Population Dynamics of Eurasian Beaver After Reintroduction
    ISSN 2075-1117, Russian Journal of Biological Invasions, 2016, Vol. 7, No. 4, pp. 355–373. © Pleiades Publishing, Ltd., 2016. Original Russian Text © V.G. Petrosyan, V.V. Golubkov, N.A. Zavyalov, Z.I. Goryainova, N.N. Dergunova, A.V. Omelchenko, S.A. Bessonov, S.A. Albov, N.F. Marchenko, L.A. Khlyap, 2016, published in Rossiiskii Zhurnal Biologicheskikh Invazii, 2016, No. 3, pp. 66–89. Patterns of Population Dynamics of Eurasian Beaver (Castor fiber L.) after Reintroduction into Nature Reserves of the European Part of Russia V. G. Petrosyana, *, V. V. Golubkovb, N. A. Zavyalovc, **, Z. I. Goryainovaa, N. N. Dergunovaa, A. V. Omelchenkoa, S. A. Bessonova, S. A. Albovd, N. F. Marchenkoe, and L. A. Khlyapa, *** aSevertsov Institute of Ecology and Evolution, Russian Academy of Sciences, pr. Leninskii 33, Moscow, 119071 Russia bFederal Research Centre “Information and Management”, Russian Academy of Sciences, ul. Vavilova 44, Moscow, 119333 Russia cRdeysky Nature Reserve, ul. Chelpanova 27, Kholm, Novgorod oblast, 175271 Russia dPrioksko-Terrasnyi Nature Biosphere Reserve, Serphukov District, Danki, Moscow oblast, 142200 Russia eKhopersky Nature Reserve, Varvarino, NovoKhopersky District, Voronezh oblast, 397418 Russia *e-mail: [email protected] **e-mail: [email protected] ***e-mail: [email protected] Received May 12, 2016 Abstract⎯This paper presents the results of analysis of the population dynamics of Eurasian beaver after its reintroduction into the Lapland, Darvinsky, Central-Forest, Prioksko-Terrasnyi, Oksky, and Khopersky nat- ural reserves that are located in European Russia in the northern, southern and central parts of the beaver range. The paper analyzes the effectiveness of a discrete time model that includes a feedback between animals and their food resources for the quantitative description of the population dynamics in the optimal, suboptimal, and pessimal habitats.
    [Show full text]
  • North American Beaver (Castor Canadensis)
    Utah Division of Wildlife Resources Wildlife Notebook Series No. 24 North American Beaver (Castor canadensis) Beaver are thought to have once numbered 60-400 million throughout North America before European settlement. Prior to 1825, explorers in Utah noted beaver in abundance throughout the state. Highly prized for their lustrous pelts, beaver populations were decimated by fur trapping during the 1700s and 1800s to supply a worldwide demand for warm and fashionable accessories. By the end of the decade they were considered rare and in Utah, their harvest was closed in 1899. Beaver have since recolonized a large portion of their former range, however loss of habitat due largely to competing land uses, has severely limited populations in many areas through- out Utah. DESCRIPTION Beaver are the largest rodents in North America. Their soft pelts range in color from nearly black, brown, reddish brown to blonde. Adults can grow to over four feet in length and up to 60 pounds or more in weight. They can live to be 20 years old. The most distinctive feature of beaver is their broad paddle-like tail, which they use like a rudder to navigate their watery environment and to balance upon as they stand on their hind legs gnawing on trees and various woody plants they harvest and use for food. While generally clumsy on land, beaver are incredibly grace- ful in the water, where they use their webbed rear feet to propel them and their tail to steer. This large tail is also used as a defense mechanism. When beaver are threatened, they will slap their tail on the surface of the water to alert family members of potential danger and to startle potential preda- tors such as bears, bobcats or otters.
    [Show full text]
  • Population and Distribution of Eurasian Beaver (Castor Fiber)
    BALTIC FORESTRY POPULATION AND DISTRIBUTION OF EURASIAN BEAVER ( CASTOR FIBER ) H. HALLEY ET AL. Population and Distribution of Eurasian Beaver ( Castor fiber ) 1 2 3 DUNCAN HALLEY , FRANK ROSELL AND ALEXANDER SAVELJEV 1 Norwegian Institute for Nature Research, Tungasletta 2, N-7485 Trondheim, Norway, e-mail: [email protected] 2 Telemark University College, N-3800 B¸ i Telemark, Norway 3 Russian Research Institute of Game Management and Fur Farming (VNIIOZ) of RAAS, 610000 Kirov, Russia Corresponding author: Duncan Halley Halley, D., Rosell, F. and Saveljev, A. 2012. Population and Distribution of Eurasian Beaver ( Castor fiber ). Baltic Forestry 18(1): 168175. Abstract After being reduced to about 1,200 animals in eight isolated populations by the beginning of the 20th century, Eurasian beavers ( Castor fiber ) have powerfully recovered in range and population, through widespread reintroductions, relaxation of persecution, and natural spread. Populations are now (2010) established in all countries within their former natural range in Europe except for Portugal, Italy, and the south Balkans (Greece, Albania, Bulgaria, Macedonia, Kosovo, Montenegro). In Asia, there are significant populations in West and Central Siberia; and small relict populations elsewhere in west and south Siberia, and in Xinjiang (China)/western Mongolia. The current minimum world population estimate for Eurasian beavers is 1.04 million, though this figure includes some populations of introduced North American beavers ( C. canadensis ) in the NW and Far Eastern Russian Federation, where the ranges of the two species occur in close proximity and to some extent overlap. Both populations and range are in rapid expansion, and in 2008 the species was reclassified by IUCN as Least Concern , though some subspecies remain threatened.
    [Show full text]
  • Use of Anal Gland Secretion to Distinguish the Two Beaver Species Castor Canadensis and C
    Central Washington University ScholarWorks@CWU Biology Faculty Scholarship College of the Sciences 6-1999 Use of anal gland secretion to distinguish the two beaver species Castor canadensis and C. fiber Frank Rosell Telemark College Lixing Sun Central Washington University, [email protected] Follow this and additional works at: https://digitalcommons.cwu.edu/biology Part of the Biology Commons Recommended Citation Rosell, F. & Sun, L. (1999). Use of anal gland secretion to distinguish the two beaver species Castor canadensis and C. fiber. Wildlife Biology, 5(2), 119-123. This Article is brought to you for free and open access by the College of the Sciences at ScholarWorks@CWU. It has been accepted for inclusion in Biology Faculty Scholarship by an authorized administrator of ScholarWorks@CWU. For more information, please contact [email protected]. SHORT Short communication articles are short scientific entities often dealing with methodological problems or with byproducts of larger research COMMUNICATION projects. The style should be the same as in original articles Use of anal gland secretion to distinguish the two beaver species Castor canadensis and C. fiber Frank Rosell & Lixing Sun Rosell, F. & Sun, L. 1999: Use of anal gland secretion to distinguish the two beaver species Castor canadensis and C. fiber. - Wildl. Biol. 5: 119-123. Introduced North American beavers Castor canadensis pose a potential threat to the continuing recovery of Eurasian beaver C. fiber populations in several European countries. For management purposes, it is necessary to be able to identify and distinguish the two species. This, however, is difficult because the two species are morphologically, ecologically and behavioural- ly similar.
    [Show full text]
  • Beavers in Scotland a Report to the Scottish Government Beavers in Scotland: a Report to the Scottish Government
    Beavers in Scotland A Report to the Scottish Government Beavers in Scotland: A report to the Scottish Government Edited by: Martin Gaywood SNH authors (in report section order): Martin Gaywood, Andrew Stringer, Duncan Blake, Jeanette Hall, Mary Hennessy, Angus Tree, David Genney, Iain Macdonald, Athayde Tonhasca, Colin Bean, John McKinnell, Simon Cohen, Robert Raynor, Paul Watkinson, David Bale, Karen Taylor, James Scott, Sally Blyth Scottish Natural Heritage, Inverness. June 2015 ISBN 978-1-78391-363-3 Please see the acknowledgements section for details of other contributors. For more information go to www.snh.gov.uk/beavers-in-scotland or contact [email protected] Beavers in Scotland A Report to the Scottish Government Foreword Beavers in Scotland I am delighted to present this report to Scottish Ministers. It is the culmination of many years of dedicated research, investigation and discussion. The report draws on 20 years of work on beavers in Scotland, as well as experience from elsewhere in Europe and North America. It provides a comprehensive summary of existing knowledge and offers four future scenarios for beavers in Scotland for Ministers to consider. It covers a wide range of topics from beaver ecology and genetics, to beaver interactions with farming, forestry, and fisheries. The reintroduction of a species, absent for many centuries, is a very significant decision for any Government to take. To support the decision- making process we have produced this comprehensive report providing one of the most thorough assessments ever done for a species reintroduction proposal. Ian Ross Chair Scottish Natural Heritage June 2015 Commission from Scottish Ministers to SNH, January 2014 Advice on the future of beavers in Scotland SNH should deliver a report to Scottish Ministers by the end of May 2015 summarising our current knowledge about beavers and setting out a series of scenarios for the future of beavers in Scotland.
    [Show full text]
  • Permanenţă Şi Continuitate Românească În Depresiunea Târgu
    The Annals of Valahia University of Târgovişte, Geographical Series, Tome 11 / 2011 __________________________________________________________________________________________________ ROMANIAN PERMANENCY AND CONTINUITY IN THE DEPRESSION TÂRGU SECUIESC Claudia CĂPĂŢÎNĂ1 1National Institute of Statistics Abstract: The establishment of the adequate framework for the living and the solidity of the human settlements in the Depression Târgu Secuiesc, according to historical realities and with the various writings of the times, proving the ancient, permanency and continuity of the Romanians in this area have concerned over time the Romanians and the Hungarians in the same time. Compelling testimonies highlighted by numerous archaeological discoveries are dating from the Paleolithic, Neolithic, Bronze Age and Iron and Feudalism, showing continuous occupation of this territory since ancient times and the absence of a population vacuum, even temporarily, at the coming migrants Hungarian, Szeklers (Székely) or other migratory. The Romanism aspect of the area is and was subject to controversy created especially by the Roesler's theory that the vacuum ethnic to the coming of Hungarians, theory "removed" not only by Romanian, but also by the representatives of the ethnic groups inhabiting, even by Hungarian ethnicity. Keywords: ancient, permanency, continuity, archaeological discoveries, autochthonous 1. Location and limits of the Depression Secuiesc Through the politico-administrative perspective, the Depression Târgu Secuiesc is part of Covasna County, occupying the north-eastern marginal part of Covasna County, being crossed by the Râul Negru (Black River) and its tributaries and surrounded on three sides by mountains. It presents a significant height, in the north part having 600 m, 530-550 m in the southern part, being stretched from north to south on about 35 km and from east to west on about 15-20 km.
    [Show full text]
  • Species Conservation Translocations: Update and Opportunities 2019
    SAC/2019/03/03 SCOTTISH NATURAL HERITAGE SCIENTIFIC ADVISORY COMMITTEE Species conservation translocations: Update and opportunities 2019. Summary 1. This paper provides an update on issues relating to species reintroductions and other types of conservation translocations, the work of the National Species Reintroduction Forum, and some future opportunities. Action 2. SAC members are invited to note the recent work on conservation translocations, and to comment on the scientific issues and potential opportunities presented in sections 27-35. Preparation of Paper 3. This paper has been prepared by Martin Gaywood, and is sponsored by Eileen Stuart. Background 4. Conservation translocations refer to the intentional movement and release of living organisms where the primary goal is a conservation benefit. They may include reintroductions, reinforcements and assisted colonisations. More background, including definitions of terms, the work of the National Species Reintroduction Forum (NSRF), and a description of the Scottish Code for Conservation Translocations (which are based on the IUCN Guidelines for Reintroductions and Other Conservation Translocations), can be found in paper SAC/2016/03/08 produced in March 2016. 5. Scotland remains a leader in conservation translocation work. It is a topic that can generate substantial public, media and political interest. The use of conservation translocations (especially reintroductions) has increased dramatically in recent years. The following sections provide an update of relevant activities that have taken place since the 2016 paper, and sets out some possible future opportunities. Update since March 2016 6. The Terms of Reference for the National Species Reintroduction Forum (NSRF) were revised and updated in December 2017. This clarified that its remit covers all conservation translocations, and not just reintroductions.
    [Show full text]
  • Eurasian Beaver (Castor Fiber) – Germany
    Eurasian Beaver (Castor fiber) – Germany Conservation DE (ATL): FV status Protection HD: Annex II & IV, Annex V for Swedish status and Finnish populations Bern Convention: Annex III Population EU27: > 356,000 – 568,000 individuals DE (CON): 5,000 – 50,000 individuals MS with AT (ALP), BE (ATL), DE (ATL), DE (CON), genuine LU improvement Other MS AT (CON), BE (CON), CZ, DE (ALP), DK, EE, ES, FI, FR, HU, LT, LV, NL,.PL, RO, SE, SI, SK Photograph: Martina Lion (2011), https://www.panoramio.com/photo/63040408 Summary: The Eurasian Beaver has undergone a history of decline and more recent recovery across Europe, with the species, assessed by the IUCN as near threatened in the mid-nineties as a result of extensive hunting and wetland loss since the beginning of the 20th century, and as ‘least concern’ only fifteen years later. Conservation measures implemented through national and sub-national conservation programmes are the main driver of the species’ recovery in Europe, in effect securing the beaver’s favourable status as long as these mechanisms are in place. Successful conservation measures in Europe contributing to the species' recovery included reintroductions and translocations, hunting restrictions, and habitat protection. Background Status and EU occurrence Whilst the Eurasian Beaver (Castor fiber)1 was once widespread in Europe and Asia, over-hunting drastically reduced the species’ range and population size from the early 20th century (Batbold et al. 2016). As a result, it was eradicated in all but a few sites across Europe: parts of the Rhone (France) and Elbe (Germany), southern Norway, the Neman River and Dnepr Basin (Belarus) and Voronezh (Russia).
    [Show full text]
  • Modelling Eurasian Beaver Foraging Habitat and Dam Suitability, for Predicting the Location and Number of Dams Throughout Catchments in Great Britain
    European Journal of Wildlife Research (2020) 66:42 https://doi.org/10.1007/s10344-020-01379-w ORIGINAL ARTICLE Modelling Eurasian beaver foraging habitat and dam suitability, for predicting the location and number of dams throughout catchments in Great Britain Hugh A. Graham1 & Alan Puttock1 & William W. Macfarlane2 & Joseph M. Wheaton2 & Jordan T. Gilbert2 & Róisín Campbell-Palmer3 & Mark Elliott4 & Martin J. Gaywood5 & Karen Anderson6 & Richard E. Brazier1 Received: 9 October 2019 /Revised: 25 March 2020 /Accepted: 2 April 2020 # The Author(s) 2020 Abstract Eurasian beaver (Castor fiber) populations are expanding across Europe. Depending on location, beaver dams bring multiple benefits and/or require management. Using nationally available data, we developed: a Beaver Forage Index (BFI), identifying beaver foraging habitat, and a Beaver Dam Capacity (BDC) model, classifying suitability of river reaches for dam construction, to estimate location and number of dams at catchment scales. Models were executed across three catchments, in Great Britain (GB), containing beaver. An area of 6747 km2 was analysed for BFI and 16,739 km of stream for BDC. Field surveys identified 258 km of channel containing beaver activity and 89 dams, providing data to test predictions. Models were evaluated using a categorical binomial Bayesian framework to calculate probability of foraging and dam construction. BFI and BDC models successfully categorised the use of reaches for foraging and damming, with higher scoring reaches being preferred. Highest scoring categories were ca. 31 and 79 times more likely to be used than the lowest for foraging and damming respectively. Zero- inflated negative binomial regression showed that modelled dam capacity was significantly related (p = 0.01) to observed damming and was used to predict numbers of dams that may occur.
    [Show full text]
  • (Castor Fiber) Reintroduction in the River Otter Beaver Trial
    See discussions, stats, and author profiles for this publication at: https://www.researchgate.net/publication/347424506 Alternative perspectives of the angling community on Eurasian beaver (Castor fiber) reintroduction in the River Otter Beaver Trial Article in Journal of Environmental Planning and Management · December 2020 DOI: 10.1080/09640568.2020.1816933 CITATIONS READS 0 4 3 authors, including: Roger Auster University of Exeter 5 PUBLICATIONS 6 CITATIONS SEE PROFILE All content following this page was uploaded by Roger Auster on 17 December 2020. The user has requested enhancement of the downloaded file. Journal of Environmental Planning and Management ISSN: (Print) (Online) Journal homepage: https://www.tandfonline.com/loi/cjep20 Alternative perspectives of the angling community on Eurasian beaver (Castor fiber) reintroduction in the River Otter Beaver Trial Roger Edward Auster , Stewart Barr & Richard Brazier To cite this article: Roger Edward Auster , Stewart Barr & Richard Brazier (2020): Alternative perspectives of the angling community on Eurasian beaver (Castorfiber) reintroduction in the River Otter Beaver Trial, Journal of Environmental Planning and Management To link to this article: https://doi.org/10.1080/09640568.2020.1816933 © 2020 The Author(s). Published by Informa UK Limited, trading as Taylor & Francis Group. View supplementary material Published online: 16 Dec 2020. Submit your article to this journal View related articles View Crossmark data Full Terms & Conditions of access and use can be found at https://www.tandfonline.com/action/journalInformation?journalCode=cjep20
    [Show full text]
  • Școala Gimnazială "Mihai Eminescu" Valea Mare
    ŞCOALA GIMNAZIALĂ „MIHAI EMINESCU” VALEA MARE, Jud. COVASNA CUI 13646683 Nr. 283/14.09.2016 PROIECT DE DEZVOLTARE INSTITUŢIONALĂ 2014-2018 ARGUMENT: Planul de dezvoltare pe termen mediu a unităţii şcolare trebuie să reflecte strategia educaţională pe termen mediu (4 – 5 ani), ţinând cont de strategia educaţională la nivel naţional, local, de evoluţie economică a zonei în care se află situată şcoala, de mobilitatea şi cerinţele profesionale ale pieţei muncii. Şcoala funcţionează şi se dezvoltă prin efortul combinat al conducerii, al personalului şcolii,al elevilor şi părinţilor, împreună alcătuind comunitatea educaţională. Planul de dezvoltare ne arată direcţiile majore de progres, iar modul de întocmire a permite consultarea părţilor interesate şi implicarea în asumarea scopurilor, obiectivelor şi acţiunilor propuse. La nivelul fiecărei unităţi şcolare proiectul de dezvoltare instituţională are o importanţă deosebită deoarece concentrează atenţia asupra finalităţilor educaţiei (dobândirea de abilităţi, aptitudini, competenţe), asigurând concentrarea tuturor domeniilor funcţionale ale managementului (curriculum, resurse umane, material financiare, relaţii sistemice şi comunitare) şi asigură coerenţa strategiei pe termen lung a şcolii. În contextul unei mondializări a economiei, a globalizării mondiale, a creşterii concurenţei internaţionale, ca urmare a aderării şi integrării în Uniunea Europeană, a impactului de noi tehnologii asupra societăţii, precum şi a pregătirii educabililor pentru a face faţă unei evoluţii în carieră într-o lume
    [Show full text]