Many Mediterranean coastal areas encounter similar problems and gaps between science, governance, and implementation of sustainable management at local-regional scales. There is often a lack of coordination between management of inland and coastal areas, and a lack of integrated land-sea data and knowledge exchange to support transitions towards sustainable development and synergies between rural and coastal areas. In this paper, we illustrate the main challenges to reach a sustainable development of coastal-rural areas related to data availability, knowledge exchange and governance, which could be tackled by coupling regional and international research infrastructures (RIs) with scientific and stakeholder collaboration networks to facilitate knowledge exchange and co-creation of solutions.Wefirst identified the main challenges in sustainable development of coastal-rural areas followed by a review of major existing RIs, scientific knowledge and collaboration networks that can help support integrated management of Mediterranean coastal zones. Based on this, we developed recommendations for a better integration of RIs and collaboration networks in the management of coastal-rural areas, including (1) the creation of local networks to facilitate periodical meetings between all sectors involved and to connect science and policy actors and (2) setting up local RIs that support the data processing and the use of regional and international RIs by scientists and policy stakeholders. ; This article has received funding from the European Union's H2020 research and innovation programme under grant agreement No 773782 'COASTAL: Collaborative Land Sea inTegration Platform' and Horizon 2020 Grant Number 654131 'COOP+: Cooperation of research infrastructures to address global challenges in the environmental field'. R B was partly funded by the Spanish Ministry of Science, Innovation and Universities (Programa Juan de la Cierva 2017, FJCI-2017-31781).
Large river-floodplain systems are hotspots of biodiversity and ecosystem services but are also used formultiple human activities, making them one of the most threatened ecosystems worldwide. There is wide evidence that reconnecting river channels with their floodplains is an effective measure to increase their multi-functionality, i.e., ecological integrity, habitats for multiple species and the multiple functions and services of river-floodplain systems, although, the selection of promising sites for restoration projects can be a demanding task. In the case of the Danube River in Europe, planning and implementation of restoration projects is substantially hampered by the complexity and heterogeneity of the environmental problems, lack of data and strong differences in socio-economic conditions aswell as inconsistencies in legislation related to river management.We take a quantitative approach based on best-available data to assess biodiversity using selected species and three ecosystem services (flood regulation, crop pollination, and recreation), focused on the navigable main stem of the Danube River and its floodplains. We spatially prioritize river-floodplain segments for conservation and restoration based on (1) multi-functionality related to biodiversity and ecosystem services, (2) availability of remaining semi-natural areas and (3) reversibility as it relates to multiple human activities (e.g. flood protection, hydropower and navigation). Our approach can thus serve as a strategic planning tool for the Danube and provide a method for similar analyses in other large river-floodplain systems.
The Digital Observatory for Protected Areas (DOPA) has been developed to support the European Union's efforts in strengthening our capacity to mobilize and use biodiversity data, information and forecasts so that they are readily accessible to policymakers, managers, experts and other users. Conceived as a set of web based services [1,2], DOPA provides a broad set of free and open source tools to assess, monitor and even forecast the state of and pressure on protected areas at local, regional and global scale. Recognized by the UN Convention on Biological Diversity (CBD) as a reference information system, DOPA Explorer is a web based interface of the DOPA providing simple means to rank protected areas at the country and ecoregion levels. It further provides users with the information at the site level species, important ecosystems and the pressures they are exposed to because of human activities. First launched in 2015, and recently updated in 2018, the DOPA Explorer 2.0 currently documents all protected areas in the world at least as large as 50 km2, around 23 000 of them covering in total more than 95% of the global protected surface. Distinguishing between terrestrial, marine and mixed protected areas, DOPA Explorer can help end users, for example, to identify those exposed to highest pressure and at the same time hosting unique threatened biodiversity. The DOPA provides a broad range of consistent and comparable indicators, based on global reference datasets, on protected area coverage, connectivity, species, ecosystems, ecosystem services and pressures at multiple (country, ecoregion and protected area) scales. These indicators are derived from more than 400 metrics and include new indicators on the connectivity of protected area systems as well as new indicators derived from Copernicus services that highlight changes in the land cover, surface water and built-up areas in protected areas. These indicators are particularly relevant for Aichi Biodiversity Target 11 (Protected Areas) of the Convention on Biological Diversity, and the UN Sustainable Development Goals 14 (Life below Water) and 15 (Life on Land), and can be used to support spatial planning, conservation and international reporting. It is the purpose of this presentation to introduce the audience with this new DOPA Explorer 2.0 tool as released in February 2018. The above work has been made with the kind collaboration of the UN Environment World Conservation Monitoring Centre (UNEP-WCMC), the International Union for Conservation of Nature (IUCN) and BirdLife International. References 1. Dubois et al. 2016. Integrating multiple spatial datasets to assess protected areas: Lessons learnt from the DOPA. International Journal of Geo-Information ISPRS 5(12), 242; doi:10.3390/ijgi5120242 2. Bastin et al. 2017. Processing conservation indicators with Open Source tools: lessons learned from the DOPA. Proceedings of the FOSS4G Conference 2017", Boston, USA, 14 -19 August 2017. ; peerReviewed
The Digital Observatory for Protected Areas (DOPA) has been developed to support the European Union's efforts in strengthening our capacity to mobilize and use biodiversity data so that they are readily accessible to policymakers, managers, researchers and other users. Assessing protected areas for biodiversity conservation at national, regional and international scales implies that methods and tools are in place to evaluate characteristics such as the protected areas' connectivity, their species assemblages (including the presence of threatened species), the uniqueness of their ecosystems, and the threats these areas are exposed to. Typical requirements for such analyses are data on protected areas, information on species distributions and threat status, and information on ecosystem distributions. By integrating all these global data consistently in metrics and indicators, the DOPA provides the means to allow end-users to evaluate protected areas individually but also to compare protected areas at the country and ecoregion level to, for example, identify potential priorities for further conservation research, action and funding. Since the metrics and indicators are available through web services, the DOPA further allows end-users to develop their own applications without requiring management of large databases and processing capacities. In addition to examples illustrating how the DOPA can be used as an aid to decision making, we discuss the lessons learnt in the development of this global biodiversity information system, and outline planned future developments for further supporting conservation strategies
To reach the global aspiration of 17 ambitious SDGs, local realities must be integrated. Often, models are developed based on quantitative statistical data sources from databases on environmental indicators or economics to assess how a given SDG can be achieved. This process however removes the local realities from the equation. How can you best include stakeholders in this mathematical modelling processes distanced from their local realities, though, and ensure higher probability of future compliance with top-down global decisions that may have local consequences once implemented? When researching stakeholder involvement and their ability to form public policy, their opinions often get reported as a single assessment, like counting the fish in the ocean once and stating that as a permanent result. Too seldom do stakeholders get invited back and given the opportunity to validate results and allow researchers to adjust their models based on on-the-ground validation or change requests. We tested the full integration of stakeholders in the modelling process of environmental topics in six different case areas across Europe, with each area holding six sectoral and one inter-sectoral workshops. In these workshops, the scope of the issues relevant to the stakeholders was driven by first the sectoral priorities of the given sector, followed by a merging of issues. In this process, we were able to identify what the commonalities between different sectors were and where synergies lay in terms of governance paths. These results were then returned to the stakeholders in a mixed session where they were able to come with feedback and advice on the results researchers presented, so that the models reflected more closely the perceptions of the regional actors. We present these methods and reflect on the challenges and opportunities of using this deep-integration method to integrate qualitative data from stakeholder inclusion in a quantitative model ; The authors would like to acknowledge funding from the European Union's ...
To reach the global aspiration of 17 ambitious SDGs, local realities must be integrated. Often, models are developed based on quantitative statistical data sources from databases on environmental indicators or economics to assess how a given SDG can be achieved. This process however removes the local realities from the equation. How can you best include stakeholders in this mathematical modelling processes distanced from their local realities, though, and ensure higher probability of future compliance with top-down global decisions that may have local consequences once implemented? When researching stakeholder involvement and their ability to form public policy, their opinions often get reported as a single assessment, like counting the fish in the ocean once and stating that as a permanent result. Too seldom do stakeholders get invited back and given the opportunity to validate results and allow researchers to adjust their models based on on-the-ground validation or change requests. We tested the full integration of stakeholders in the modelling process of environmental topics in six different case areas across Europe, with each area holding six sectoral and one inter-sectoral workshops. In these workshops, the scope of the issues relevant to the stakeholders was driven by first the sectoral priorities of the given sector, followed by a merging of issues. In this process, we were able to identify what the commonalities between different sectors were and where synergies lay in terms of governance paths. These results were then returned to the stakeholders in a mixed session where they were able to come with feedback and advice on the results researchers presented, so that the models reflected more closely the perceptions of the regional actors. We present these methods and reflect on the challenges and opportunities of using this deep-integration method to integrate qualitative data from stakeholder inclusion in a quantitative model. ; publishedVersion
In: Kleemann , J , Schröter , M , Bagstad , K J , Kuhlicke , C , Kastner , T , Fridman , D , Schulp , C J E , Wolff , S , Martínez-López , J , Koellner , T , Arnhold , S , Martín-López , B , Marques , A , Lopez-Hoffman , L , Liu , J , Kissinger , M , Guerra , C A & Bonn , A 2020 , ' Quantifying interregional flows of multiple ecosystem services – A case study for Germany ' , Global Environmental Change , vol. 61 , 102051 , pp. 1-26 . https://doi.org/10.1016/j.gloenvcha.2020.102051
Despite a growing number of national-scale ecosystem service (ES) assessments, few studies consider the impacts of ES use and consumption beyond national or regional boundaries. Interregional ES flows – ecosystem services "imported" from and "exported" to other countries – are rarely analyzed and their importance for global sustainability is little known. Here, we provide a first multi-ES quantification of a nation's use of ES from abroad. We focus on ES flows that benefit the population in Germany but are supplied outside German territory. We employ a conceptual framework recently developed to systematically quantify interregional ES flows. We address four types of interregional ES flows with: (i) biophysical flows of traded goods: cocoa import for consumption; (ii) flows mediated by migratory species: migration of birds providing pest control; (iii) passive biophysical flows: flood control along transboundary watersheds; and (iv) information flows: China's giant panda loan to the Berlin Zoo. We determined that: (i) Ivory Coast and Ghana alone supply around 53% of Germany's cocoa while major negative consequences for biodiversity occurred in Cameroon and Ecuador; (ii) Africa´s humid and sub-humid climate zones are important habitats for the majority of migratory bird species that provide natural pest control services in agricultural areas in Germany; (iii) Upstream watersheds outside the country add an additional 64% flood regulation services nationally, while Germany exports 40% of flood regulation services in neighboring, downstream countries; (iv) Information flows transported by the pandas were mainly related to political aspects and - contrary to our expectations - considerably less on biological and natural aspects. We discuss the implications of these results for international resource management policy and governance.
Faced with environmental degradation, governments worldwide are developing policies to safeguard ecosystem services (ES). Many ES models exist to support these policies, but they are generally poorly validated, especially at large scales, which undermines their credibility. To address this gap, we describe a study of multiple models of five ES, which we validate at an unprecedented scale against 1675 data points across sub-Saharan Africa. We find that potential ES (biophysical supply of carbon and water) are reasonably well predicted by the existing models. These potential ES models can also be used as inputs to new models for realised ES (use of charcoal, firewood, grazing resources and water), by adding information on human population density. We find that increasing model complexity can improve estimates of both potential and realised ES, suggesting that developing more detailed models of ES will be beneficial. Furthermore, in 85% of cases, human population density alone was as good or a better predictor of realised ES than ES models, suggesting that it is demand, rather than supply that is predominantly determining current patterns of ES use. Our study demonstrates the feasibility of ES model validation, even in data-deficient locations such as sub-Saharan Africa. Our work also shows the clear need for more work on the demand side of ES models, and the importance of model validation in providing a stronger base to support policies which seek to achieve sustainable development in support of human well-being.
The EU Water Framework Directive aims to ensure restoration of Europe's water bodies to "good ecological status" by 2027. Many Member States will struggle to meet this target, with around half of EU river catchments currently reporting below standard water quality. Diffuse pollution from agriculture represents a major pressure, affecting over 90% of river basins. Accumulating evidence shows that recent improvements to agricultural practices are benefiting water quality but in many cases will be insufficient to achieve WFD objectives. There is growing support for land use change to help bridge the gap, with a particular focus on targeted tree planting to intercept and reduce the delivery of diffuse pollutants to water. This form of integrated catchment management offers multiple benefits to society but a significant cost to landowners and managers. New economic instruments, in combination with spatial targeting, need to be developed to ensure cost effective solutions – including tree planting for water benefits - are realised. Payments for Ecosystem Services (PES) are flexible, incentive-based mechanisms that could play an important role in promoting land use change to deliver water quality targets. The PESFOR-W COST Action will consolidate learning from existing woodlands for water PES schemes in Europe and help standardize approaches to evaluating the environmental effectiveness and cost-effectiveness of woodland measures. It will also create a European network through which PES schemes can be facilitated, extended and improved, for example by incorporating other ecosystem services linking with aims of the wider forests-carbon policy nexus.
In: Valatin , G , Abildtrup , J , Accastello , C , Said Al-Tawaha , A R M , Andreucci , M-B , Atanasova , S , Avdibegović , M , Baksic , N , Banasik , K , Barquin , J , Barstad , J , Bastakova , V , Becirovic , D , Begueria , S , Bethers , U , Bihunova , M , Blagojevic , B , Bösch , M , Bournaris , T , Cao , Y , Carvalho-Santos , C , Chikalanov , A , A. Cunha e Sá , M , Czyżyk , K , Daly , H , Davies , H , Del Campo , A , de Groot , R , De Vreese , R , Dostál , T , El Mokaddem , A , Finér , L , Evans , R , Fiquepron , J , Frac , M , Futter , M , Garcia , S , Gatto , P , Geneletti , D , Gezik , V , Giupponi , C , González-Sanchís , M , Gordillo , F , Gorriz , E , Grigorova , Y , Heinsoo , K , Hochbichler , E , Högbom , L , Image , M , Jacobsen , J B , Japelj , A , Jelic , S , Junk , J , Juhasz , C , Kagalou , I , Kelly-Quinn , M , Klamerus-Iwan , A , Kluvankova , T , Koeck , R , Konovska , I , Krajter Ostoic , S , Krc , J , Lavnyy , V , Leonardi , A , Libiete , Z , Little , D , Lo Porto , A , Loukas , A , Lyubenova , M I , Maric , B , Martínez-López , J , Martinez , I , Maxim , A , Metslaid , M , Melvin , A , Costică , M , Mincev , I , Morkvenas , Z , Nevenic , R , Nisbet , T , O'hUallachain , D , Olschewski , R , Östberg , J , Oszust , K , Ovando , P , Paletto , A , Parpan , T , Pettenella , D , Pezdevšek Malovrh , Š , Planinšek , Š , Podlipná , R , Posavec , S , Potočki , K , Prokofieva , I , Quinteiro , P , Radocz , L , Ristic , R , Robert , N , Rugani , B , Sabanovic , J , Sarvasova , Z , Savoska , S , Schleppi , P , Schueler , G , Shannon , M , Silgram , M , Srdjevic , B , Stefan , G , Stijovic , A , Strange , N , Tattari , S , Teofilovski , A , Termansen , M , Thorsen , B J , Toth , A , Trebs , I , Tmušić , N , Vasiliades , L , Vedel , S E , Ventrubová , K , Vuletic , D , Winkel , G , Yao , R , Young , S , Yousefpour , R , Zahvoyska , L , Zhang , D , Zhou , J & Žižková , E 2017 , ' PESFOR-W : improving the design and environmental effectiveness of woodlands for water payments for ecosystem services ' , Research Ideas and Outcomes , vol. 3 , e13828 . https://doi.org/10.3897/rio.3.e13828
The EU Water Framework Directive aims to ensure restoration of Europe's water bodies to "good ecological status" by 2027. Many Member States will struggle to meet this target, with around half of EU river catchments currently reporting below standard water quality. Diffuse pollution from agriculture represents a major pressure, affecting over 90% of river basins. Accumulating evidence shows that recent improvements to agricultural practices are benefiting water quality but in many cases will be insufficient to achieve WFD objectives. There is growing support for land use change to help bridge the gap, with a particular focus on targeted tree planting to intercept and reduce the delivery of diffuse pollutants to water. This form of integrated catchment management offers multiple benefits to society but a significant cost to landowners and managers. New economic instruments, in combination with spatial targeting, need to be developed to ensure cost effective solutions – including tree planting for water benefits - are realised. Payments for Ecosystem Services (PES) are flexible, incentive-based mechanisms that could play an important role in promoting land use change to deliver water quality targets. The PESFOR-W COST Action will consolidate learning from existing woodlands for water PES schemes in Europe and help standardize approaches to evaluating the environmental effectiveness and cost-effectiveness of woodland measures. It will also create a European network through which PES schemes can be facilitated, extended and improved, for example by incorporating other ecosystem services linking with aims of the wider forests-carbon policy nexus. ; The EU Water Framework Directive aims to ensure restoration of Europe's water bodies to "good ecological status" by 2027. Many Member States will struggle to meet this target, with around half of EU river catchments currently reporting below standard water quality. Diffuse pollution from agriculture represents a major pressure, affecting over 90% of river basins. Accumulating evidence shows that recent improvements to agricultural practices are benefiting water quality but in many cases will be insufficient to achieve WFD objectives. There is growing support for land use change to help bridge the gap, with a particular focus on targeted tree planting to intercept and reduce the delivery of diffuse pollutants to water. This form of integrated catchment management offers multiple benefits to society but a significant cost to landowners and managers. New economic instruments, in combination with spatial targeting, need to be developed to ensure cost effective solutions – including tree planting for water benefits - are realised. Payments for Ecosystem Services (PES) are flexible, incentive-based mechanisms that could play an important role in promoting land use change to deliver water quality targets. The PESFOR-W COST Action will consolidate learning from existing woodlands for water PES schemes in Europe and help standardize approaches to evaluating the environmental effectiveness and cost-effectiveness of woodland measures. It will also create a European network through which PES schemes can be facilitated, extended and improved, for example by incorporating other ecosystem services linking with aims of the wider forests-carbon policy nexus.