Lillebø, Ana I.Ana I.LillebøSomma, FrancescaFrancescaSommaNorén, KatjaKatjaNorénGonçalves, JorgeJorgeGonçalvesAlves, M. FátimaM. FátimaAlvesBallarini, ElisabettaElisabettaBallariniBentes, LuisLuisBentesBielecka, MalgorzataMalgorzataBieleckaChubarenko, Boris V.Boris V.ChubarenkoHeise, SusanneSusanneHeiseKhokhlov, ValeriyValeriyKhokhlovKlaoudatos, DimitrisDimitrisKlaoudatosLloret, JavierJavierLloretMargonski, PiotrPiotrMargonskiMarín, AtuchaAtuchaMarínMatczak, MagdalenaMagdalenaMatczakOen, Amy M.Amy M.OenPalmieri, Maria G.Maria G.PalmieriPrzedrzymirska, JoannaJoannaPrzedrzymirskaRóżyński, GrzegorzGrzegorzRóżyńskiSousa, Ana I.Ana I.SousaSousa, Lisa P.Lisa P.SousaTuchkovenko, YuriiYuriiTuchkovenkoZaucha, JacekJacekZaucha2020-04-202020-04-202016-10-01Integrated environmental assessment and management 4 (12): 726-734 (2016-10-01)http://hdl.handle.net/11420/5778This article shares the experiences, observations, and discussions that occurred during the completing of an ecosystem services (ES) indicator framework to be used at European Union (EU) and Member States' level. The experience base was drawn from 3 European research projects and 14 associated case study sites that include 13 transitional-water bodies (specifically 8 coastal lagoons, 4 riverine estuaries, and 1 fjord) and 1 coastal-water ecosystem. The ES pertinent to each case study site were identified along with indicators of these ES and data sources that could be used for mapping. During the process, several questions and uncertainties arose, followed by discussion, leading to these main lessons learned: 1) ES identification: Some ES that do not seem important at the European scale emerge as relevant at regional or local scales; 2) ES indicators: When direct indicators are not available, proxies for indicators (indirect indicators) might be used, including combined data on monitoring requirements imposed by EU legislation and international agreements; 3) ES mapping: Boundaries and appropriate data spatial resolution must be established because ES can be mapped at different temporal and spatial scales. We also acknowledge that mapping and assessment of ES supports the dialogue between human well-being and ecological status. From an evidence-based marine planning-process point of view, mapping and assessment of marine ES are of paramount importance to sustainable use of marine natural capital and to halt the loss of marine biodiversity. Integr Environ Assess Manag 2016;12:726-734. © 2016 SETAC.en1551-377720164726734Biodiversity strategyCommon International Classification for Ecosystem Services (CICES)Ecosystem-based managementSpatial planningTransitional watersTechnikJournal Article10.1002/ieam.1782Other