Mapping and assessment of ecosystems and their services, [1st report], An analytical framework for ecosystem assessments under Action 5 of the EU Biodiversity Strategy to 2020: discussion paper
In: Technical report 2013-067
48 Ergebnisse
Sortierung:
In: Technical report 2013-067
In: Ecology and society: E&S ; a journal of integrative science for resilience and sustainability, Band 17, Heft 2
ISSN: 1708-3087
Green infrastructure (GI), a network of nature, semi-natural areas and green space, delivers essential ecosystem services which underpin human well-being and quality of life. Maintaining ecosystem services through the development of GI is therefore increasingly recognized by policies as a strategy to cope with potentially changing conditions in the future. This paper assessed how current trends of land-use change have an impact on the aggregated provision of eight ecosystem services at the regional scale of the European Union, measured by the Total Ecosystem Services Index (TESI8). Moreover, the paper reports how further implementation of GI across Europe can help maintain ecosystem services at baseline levels. Current demographic, economic and agricultural trends, which affect land use, were derived from the so called Reference Scenario. This scenario is established by the European Commission to assess the impact of energy and climate policy up to 2050. Under the Reference Scenario, economic growth, coupled with the total population, stimulates increasing urban and industrial expansion. TESI8 is expected to decrease across Europe between 0 and 5 % by 2020 and between 10 and 15 % by 2050 relative to the base year 2010. Based on regression analysis, we estimated that every additional percent increase of the proportion of artificial land needs to be compensated with an increase of 2.2 % of land that qualifies as green infrastructure in order to maintain ecosystem services at 2010 levels.
BASE
In: Technical report 2016-099
Insect pollinators are a key component of biodiversity; they also play a major role in the reproduction of many species of wild plants and crops. It is widely acknowledged that insect pollinators are threatened by many environmental pressures, mostly of anthropogenic nature. Their decline is a global phenomenon. A better understanding of their distribution can help their monitoring and ultimately facilitate conservation actions. Since we only have partial knowledge of where pollinator species occur, the possibility to predict suitable environmental conditions from scattered species records can facilitate not only species monitoring, but also the identification of areas potentially vulnerable to pollinators decline. This data paper contains the predicted distribution of 47 species of bumblebees across the 28 Member States of the European Union (EU-28). Amongst the wild pollinators, bumblebees are one of the major groups contributing to the production of many crop species, hence their decline in Europe, North America and Asia can potentially threaten food security. Predictions were derived from distribution models, using species records with a spatial resolution of 10 km accessed from a central repository. Predictions were based on records from 1991 to 2012 and on a series of spatial environmental predictors from three main thematic areas: land use and land cover, climate and topography. These distributions were used to estimate the value of pollination as an ecosystem service. In light of the recent European Pollinators Initiative, this paper provides valuable information for a better understanding of where wild pollinators occur and it should be extended to other pollinator species.
BASE
In: Technical report 2014-080
QC 20191128 ; EU Horizon 2020 ESMERALDA Project, Grant agreement No. 642007
BASE
In: Van Herzele , A , Coninx , I , Mortelmans , D , Young , J , Bela , G , Heink , U , Carmen , E , Blicharska , M , Hendriks , K , Bogers , M , Jokinen , P , Geamana , N , Bucur , M , Cosor , G , Maes , J , Müller , A , Fabok , V , Kopperoinen , L , Primmer , E & Bugter , R 2014 , Final report synthesising the analysis of argumentation in multi-level governance interactions in case studies : Deliverable No: 3.1 . Rapport niet door INBO uitgegeven .
This report provides a synthesis of argumentation analysis in real-world cases in "multi-level biodiversity governance", investigated within the BESAFE project. The following broad research questions guided the synthesis of argumentation analysis in the case studies: • Which (different types of) arguments can be identified at different levels and units of biodiversity governance? • How are these arguments exchanged and put to work in multi-level and networked interactions (i.e. within and across different levels and units of biodiversity governance)? • How are these arguments rooted in and how do they feed into different perspectives, worldviews and functioning of social groups or institutions at the different levels and units of biodiversity governance? The study's approach to answering these questions is guided by a three layer analytical framework. This framework comprises three different perspectives to argument-making practice. Together these enable a comprehensive understanding of the role of argumentation in multi-level biodiversity governance. The first layer takes the perspective that arguments are "products" of communication. The analysis focuses on the verbal content of arguments, i.e. what these arguments "say". By comparing argument contents between global, European, national, regional and local governance levels, it was revealed that at both global and regional level, social arguments were most dominant, while at the European level economic arguments were more prominent. Comparison between European and national governance levels revealed little differences. Comparison between types of actors showed some differences of emphasis. Whereas most actors use the argument that biodiversity should be protected because of its inherent value, regional authorities more often referred to social wellbeing and national authorities to legal obligation. The analysis also considered variety of arguments. In general, variety was very limited. Politicians used the smallest variety of arguments, while the largest variety was found in the science actors. Furthermore, variety depended on communication channels (e.g. internet forums showed much variety). Lastly, arguments do change over time. Arguments on ecosystem services, for instance, became prominent at both global and European levels, but they often do not reach or persist at local levels of governance. The second layer of the framework uses the perspective of arguments being transactions between arguers and audiences. The focus here is on what actors "do" D3.1 Final report synthesising the analysis of argumentation in multi-level governance interactions in case studies with arguments, that is, what they aim to achieve with the arguments and what strategies they use. Plenty of strategies were identified, such as particularisation (e.g. stressing the uniqueness of a natural area to increase policy attention), upscaling (e.g. situating a biodiversity problem at a higher level of space or time to make it more important), dichotomisation (e.g. polarising between two alternatives to exclude the possibility of an intermediate solution) and aligning arguments to the goals and interests of others to affect policy outcomes in a way that suits own interests. Finally, actors used various channels to transmit argument. Main examples were local politicians, NGOs and mass media. The third layer takes the perspective of arguments as being conditioned by the social-institutional networks in which they are transmitted. The analysis focuses on how the arguments and the reasoning they communicate "fit" into the different perspectives, worldviews and functioning of social groups and institutions. It was shown that argumentation was highly conditioned by law and regulations, institutional roles and established practices. International obligation, in particular, empowered member states to implement biodiversity policy and to finish disputes. But legislation (and uncertainty about it) also hampered conservation efforts. Furthermore, established criteria used in conservation practice (e.g. rarity, threat and species richness) supported justification of the need for implementing biodiversity conservation measures. Finally, what actors considered as their interests and what they valued as a legitimate policy process (democratic, science-based and sufficient societal support) conditioned the argumentation.
BASE
In: EUR 30599
In: Technical report 2016-102
In: ARPHA Preprints
In this report, we present the analysis of the different available biodiversity data streams at the EU and national level, both baseline biodiversity data and monitoring data. We assess how these biodiversity data inform and trigger policy action and identify the related challenges the different European countries and relevant EU agencies face and the solutions to overcome them. To do this, we consulted with more than 350 expert stakeholders from policy, research and practice. The assessment identified a fragmented biodiversity data landscape that cannot currently easily answer all relevant policy questions. Quantity and quality of biodiversity baseline datasets differ for the different countries, ranging from non-existent biodiversity monitoring due to capacity issues, to regular monitoring of ecosystem processes and state. By engaging stakeholders and experts in both member states and non-member states and from several EU bodies, we identified key challenges and ways to address these with targeted solutions towards building a joint European Biodiversity Monitoring Network. Solutions include focussing on cooperation and coordination, enhanced data standardisation and sharing, as well as the use of models and new technologies. These solutions can however only be realised with dedicated funding and capacity building, in coordination with all stakeholders in partnership.
BASE
In the EU, the mapping and assessment of ecosystems and their services, abbreviated to MAES, is seen as a key action for the advancement of biodiversity objectives, and also to inform the development and implementation of related policies on water, climate, agriculture, forest, marine and regional planning. In this study, we present the development of an analytical framework which ensures that consistent approaches are used throughout the EU. It is framed by a broad set of key policy questions and structured around a conceptual framework that links human societies and their well-being with the environment. Next, this framework is tested through four thematic pilot studies, including stakeholders and experts working at different scales and governance levels, which contributed indicators to assess the state of ecosystem services. Indicators were scored according to different criteria and assorted per ecosystem type and ecosystem services using the common international classification of ecosystem services (CICES) as typology. We concluded that there is potential to develop a first EU wide ecosystem assessment on the basis of existing data if they are combined in a creative way. However, substantial data gaps remain to be filled before a fully integrated and complete ecosystem assessment can be carried out.
BASE
In: Maes , J , Hauck , J , Paracchini, M L , Ratamäki, O , Termansen , M , Perez-Soba , M , Kopperoinen , L , Rankinen , K , Schägner , J P , Henrys , P , Cisowska , I , Zandersen , M , Jax , K , La Notte , A , Leikola, N , Pouta , E , Smart , S , Hasler , B , Lankia , T , Andersen , H E , Lavalle , C , Vermaas , T , Alemu , M H , Scholefield , P , Batista , F , Pywell , R , Hutchins , M , Blemmer , M , Fonnesbech-Wulff , A , Vanbergen , A , Münier , B , Baranzelli , C , Roy , D , Thieu , V , Zulian , G , Kuussaari , M , Thodsen , H , Alanen , E-L , Egoh , B , Sørensen , P B , Braat , L & Bidoglio , G 2012 , A spatial assessment of ecosystem services in Europe - Phase II : Methods, case studies and policy analysis & Synthesis Report . PEER Report , no. 4 , European Commission, Joint Research Centre . https://doi.org/10.2788/4198 , https://doi.org/10.2788/41831
Mainstreaming ecosystem services in EU decision making processes requires a solid conceptual and methodological framework for mapping and assessing ecosystem services that serve the multiple objectives addressed by policies. The PRESS-2 study (PEER Research on Ecosystem Service – Phase 2) provides such an analytical framework which enables the operationalization of the present scientific knowledge base of environmental data and models for application by the EU and Member States for mapping and assessment of ecosystem services. This study was structured along three strands of work: policy and scenario analysis, mapping and valuation. Linking the maps of ecosystem service supply to monetary valuation allowed an analysis of the expected impact of policy measures on benefits derived from ecosystem services. The recreation case, which Marianne participated in, presents evidence that millions of people visited forests several times per year and they expressed their willingness to pay to continue doing so. The visitor statistics that were used in this study confirmed the usefulness of the ROS approach (Recreation Opportunity Spectrum) to identify areas in terms of their accessibility and potential to provide recreation services. In addition, PRESS-2 presents a spatial analysis of city population density and green urban areas.
BASE
The European Union (EU) Horizon 2020 Coordination and Support Action ESMERALDA aimed at developing guidance and a flexible methodology for Mapping and Assessment of Ecosystems and their Services (MAES) to support the EU member states in the implementation of the EU Biodiversity Strategy's Target 2 Action 5. ESMERALDA's key tasks included network creation, stakeholder engagement, enhancing ecosystem services mapping and assessment methods across various spatial scales and value domains, work in case studies and support of EU member states in MAES implementation. Thus ESMERALDA aimed at integrating various project outcomes around four major strands: i) Networking, ii) Policy, iii) Research and iv) Application. The objective was to provide guidance for integrated ecosystem service mapping and assessment that can be used for sustainable decision-making in policy, business, society, practice and science at EU, national and regional levels. This article presents the overall ESMERALDA approach of integrating the above-mentioned project components and outcomes and provides an overview of how the enhanced methods were applied and how they can be used to support MAES implementation in the EU member states. Experiences with implementing such a large pan-European Coordination and Support Action in the context of EU policy are discussed and recommendations for future actions are given.
BASE
The European Union (EU) Horizon 2020 Coordination and Support Action ESMERALDA aimed at developing guidance and a flexible methodology for Mapping and Assessment of Ecosystems and their Services (MAES) to support the EU member states in the implementation of the EU Biodiversity Strategy's Target 2 Action 5. ESMERALDA's key tasks included network creation, stakeholder engagement, enhancing ecosystem services mapping and assessment methods across various spatial scales and value domains, work in case studies and support of EU member states in MAES implementation. Thus ESMERALDA aimed at integrating various project outcomes around four major strands: i) Networking, ii) Policy, iii) Research and iv) Application. The objective was to provide guidance for integrated ecosystem service mapping and assessment that can be used for sustainable decision-making in policy, business, society, practice and science at EU, national and regional levels. This article presents the overall ESMERALDA approach of integrating the above-mentioned project components and outcomes and provides an overview of how the enhanced methods were applied and how they can be used to support MAES implementation in the EU member states. Experiences with implementing such a large pan-European Coordination and Support Action in the context of EU policy are discussed and recommendations for future actions are given. ; QC 20191008
BASE