The ecosystem service assessment challenge: Reflections from Flanders-REA
Introduction
The field of ecosystem services continues a long-standing tradition in economic science and revolves around the sustainable and equitable use of natural resources. After the somewhat polemic promotion of the concept in the 1990s (see Baveye et al., 2013), ecosystem services and especially their valuation recently regained wider attention of high-level policy institutions and the nature conservation research community (for a critical review of the concept's history see Baveye et al., 2013, Gómez-Baggethun et al., 2010). This resulted in a broader mainstreaming of the concept and its percolation into various policy documents during the last decade.
The Aichi Targets, adopted by the convention on biological diversity (CBD), explicitly put forward a rationale on ecosystem service provision, aiming at sustainability and equity in ecosystem service delivery.1 The achievement of these targets is envisioned by 2020. In line with this ambition, the European Commission developed a biodiversity strategy for Europe.2 The strategy is similarly divided in targets and actions and emphasizes the (strict) economic notion more strongly. There are six main targets and 20 actions to help Europe reach its goal. Target two, action five is directly linked to ecosystem services: ‘member states, with the assistance of the Commission, will map and assess the state of ecosystems and their services in their national territory by 2014, assess the economic value of such services, and promote the integration of these values into accounting and reporting systems at EU and national level by 2020’. The assistance of the European Commission is embodied in the working group MAES (mapping and assessment of ecosystem services), which to date has provided two guidance documents (Maes et al., 2013a, Maes et al., 2013b).
Up till now, most member states have not reached the 2014 goal yet, and demand for assistance and inter-state exchange is increasing. The current evolutions and several assessments on EU scale are tracked by the MAES working group.3 Adding to available frameworks (MEA, 2005; TEEB, 2009; Jacobs et al., 2013, Maes et al., 2013a), specific lessons were drawn from the United Kingdom National Ecosystem Assessment (UK-NEA, 2011), the Japan Satoyama Satoumi Assessment (JSSA, 2010), and active exchanges with Dutch colleagues.4
Flanders, the northern region of the Belgian federal state, has seen a surge in ecosystem services projects and networks during the last 6 years (Segers et al., 2013). Following this build-up of critical mass and scientific capacity, the Research Institute for Nature and Forest (INBO) decided to focus its statutory nature reporting task on supporting Target 2, Action 5 of the EU Biodiversity Strategy. Reporting on the ‘state of nature’ is a legal obligation: ‘to report on the state of nature in Flanders, the expected evolutions under alternative policy scenarios, and the evaluation of past policy’.5 Taking the EU-targets into account, the biennial reporting process was extended to an ‘assessment of the state and trends of ecosystems and their services in Flanders (2014), the development of policy tools and procedures with regard to ecosystem services (2016), and the analysis of alternative scenarios for Flanders (2018)’. The first reporting phase, the state and trends assessment, was finished in 2014 and presented to policy makers in February 2015 (Stevens et al., 2015). This paper mainly focusses on organizational and methodological aspects of the assessment, in order to address common challenges of regional assessments toward reaching European and global policy targets. Results on state and trends of ecosystem services are presented and discussed in brief, as for the detailed assessment results; technical methods and discussion, the 1500 page technical assessment report, its synthesis and the online ecosystem service maps6 can be consulted.
Section snippets
Methods
The first section explains the general organization of the assessment, focusing on inclusion of relevant experts, decision makers and non-governmental organizations. Then, the methodology for evaluation of ecosystem service state and trends on a regional aggregated level is discussed in detail. This includes the analysis of supply, demand and use of ecosystem services as well as interactions among ecosystem services, based on a scientific meta-review and synthesis method. A third section
Results
The results section presents results on state and trends of ecosystem services, and exemplifies some of the assessment's mapping results. In the third section participation and mainstreaming results are briefly described.
Discussion of assessment concept, methodology and organization
The discussion section outlines the conceptual and methodological lessons of the Flanders REA which can particularly be of interest to regional and national assessments. The local, European and global policy context is discussed by focusing on local implementation, EU guidance needs and global sustainability goals.
Conclusions
Assessments on biodiversity and ecosystem services operate in a very complex context, coping with large unknowns, combinations of different disciplines and data types, and responding to multiple demands at different scales. This entails a significant personal and professional challenge for assessment teams, transforming traditional scientific work in several ways. Local, regional or national assessments and larger-scale assessments such as the IPBES regional assessments should share
Acknowledgements
First of all, the authors wish to acknowledge the many authors and reviewers of the Flanders REA reports for their valuable time, high-quality work, constructive discussions and for putting up with us during two years. Critical insights and ideas never come alone, they result from many discussions and conversations with colleagues and friends in the Belgium Ecosystem Services Community (www.beescommunity.be), the IWT-ECOPLAN project, the value integration working group of the ecosystem service
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2020, Science of the Total EnvironmentNature affinity and willingness to pay for urban green spaces in a developing country
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2019, Science of the Total EnvironmentCitation Excerpt :Ecosystem services analyses followed the work of Hartel et al. (2014) and resulted in a list of actual and ES demand and supply and a rating score for each ES in the area. Using (a) the available data from various literature sources for the study area (Kalliris, 1993; Papastergiadou et al., 2007; Piraeus Bank, 2014, 2018; MEEN, 2016; NCMA, 2016; Vlami et al., 2017), (b) the outcomes of the questionnaire survey of this study and (c) the authors' expert judgment, we assigned each service to the relevant ecosystem type by using spatial analysis techniques (“matrix” based approach) (Burkhard et al., 2009, 2012; Jacobs et al., 2016; Burkhard and Maes, 2017). Rating of the importance of each ES, as previously described, was also incorporated in the analysis.
Navigating pluralism: Understanding perceptions of the ecosystem services concept
2019, Ecosystem ServicesCitation Excerpt :Increased collaboration, both between academic disciplines and between academia and wider society, was identified as a key area for the development of ecosystem services research and practice. The expansion of inter- and transdisciplinary work was a clear desire of the respondents (Cross-cutting theme 4) and matches aspirations in the literature (Carmen et al., 2018; Jacobs et al., 2015). The inclusion of more social scientists within ecosystem services assessments was particularly stressed as a necessary step to increase the integration of social and cultural values (Cross-cutting theme 5).