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Ocean Sci., 12, 953–976, 2016 www.-sci.net/12/953/2016/ doi:10.5194/os-12-953-2016 © Author(s) 2016. CC Attribution 3.0 License.

Developing European operational for Blue Growth, climate change adaptation and mitigation, and ecosystem-based management

Jun She1, Icarus Allen2, Erik Buch3, Alessandro Crise4, Johnny A. Johannessen5, Pierre-Yves Le Traon6, Urmas Lips7, Glenn Nolan4, Nadia Pinardi8, Jan H. Reißmann9, John Siddorn10, Emil Stanev11, and Henning Wehde12 1Department of Research, Danish Meteorological Institute, Copenhagen, Denmark 2Plymouth Marine Laboratory, Plymouth, UK 3EuroGOOS AISBL, Brussels, Belgium 4Istituto Nazionale di Oceanografia e di Geofisica Sperimentale, Trieste, Italy 5Nansen Environmental and Remote Sensing Center, Bergen, Norway 6Mercator Ocean and Ifremer, Ramonville St. Agne, France 7Marine Institute, Tallinn University of Technology, Tallinn, Estonia 8Department of Physics and Astronomy, Alma Mater Studiorum University of Bologna, Italy 9Bundesamt für Seeschifffahrt und Hydrographie, Hamburg, Germany 10Met Office, Exeter, UK 11Department of Data Analysis and Data Assimilation, Helmholtz-Zentrum Geesthacht, Hamburg, Germany 12Institute of Marine Research, Bergen, Norway

Correspondence to: Jun She ([email protected])

Received: 26 October 2015 – Published in Ocean Sci. Discuss.: 21 January 2016 Revised: 13 June 2016 – Accepted: 14 June 2016 – Published: 26 July 2016

Abstract. Operational approaches have been more and more Oceanography” and “Operational Ecology” aim at develop- widely developed and used for providing marine data and ing new operational approaches for the corresponding knowl- information services for different socio-economic sectors of edge areas. the Blue Growth and to advance knowledge about the marine environment. The objective of operational oceanographic re- search is to develop and improve the efficiency, timeliness, robustness and product quality of this approach. This white 1 Introduction paper aims to address key scientific challenges and research priorities for the development of operational oceanography Operational oceanography, including ocean monitoring, in Europe for the next 5–10 years. Knowledge gaps and analysis, reanalysis, forecasting and service provision is a deficiencies are identified in relation to common scientific branch of science that requires continuous implementation challenges in four EuroGOOS knowledge areas: European of the most advanced research findings to comply with ocean , Modelling and Forecasting Technology, user needs. Inherent to operational oceanography is also the Coastal Operational Oceanography and Operational Ecol- sustained production, timely delivery, automated qualifica- ogy. The areas “European Ocean Observations” and “Mod- tion and free access to observations in near real time. More- elling and Forecasting Technology” focus on the further ad- over, operational oceanography delivers products and infor- vancement of the basic instruments and capacities for Euro- mation that are crucial for the research community to gain pean operational oceanography, while “Coastal Operational major understanding and advance knowledge and technology in the marine sector.

Published by Copernicus Publications on behalf of the European Geosciences Union. 954 J. She et al.: Developing European operational oceanography for Blue Growth

In the past decades, due to a growing blue economy and relatively lower levels of maturity and integration than the challenges for adaption and mitigation to climate change as physical part of the CMEMS . well as the improved capacities on operational marine ser- In recent years, user requirements for operational marine vice, operational approaches have been developed for a va- data and information have largely increased due to the grow- riety of socio-economic sectors, ranging from public ser- ing blue economy (e.g. , maritime transport, vice for coastal in the beginning to emerging areas coastal and offshore , and marine bio-resources), such as marine ecosystem and maritime services and inte- implementation of European polices in marine-related Di- grated coastal zone management services. Such operational rectives and regional marine environmental conventions (e.g. approaches share common features in their value-chain, i.e. ecosystem-based management), adaptation to and mitigation user- and science-driven, knowledge- and technology-based, of climate change as well as public services (e.g. disaster operation-practiced and service-oriented (She, 2015). The ar- warning and protections). Although European operational eas of interests for future research are determined by both oceanography has made significant advancements in the last user needs and the state of the scientific frontier. New 2 decades, great challenges still exist in view of serving fast- knowledge and technologies, generated from the research, growing user needs. A large part of them can be summarized will then be incorporated into operational oceanography sys- in four key knowledge areas: (i) European Ocean Observa- tems that provide the users with data and information prod- tions; (ii) Modelling and Forecasting Technology; (iii) Oper- ucts. ational oceanography in the coastal ; and (iv) opera- Operational oceanography in Europe was mainly initiated tional ecology (OE) (She, 2015). and sustained at national level before the 1990s. Aiming at This paper describes the objectives, challenges, and re- integrating the operational oceanography development on re- search priorities in the above four areas, both in the short gional and European scales, EuroGOOS from its very be- to mid-term (1–5 years) and long term (5–10 years and ginning established the Regional Operational Oceanography more). Among the four areas, (i) and (ii) focus on the fur- Systems (ROOSes), such as for the Arctic Ocean, Baltic , ther advancement and integration of existing operational Northwest Shelf Sea, Ireland–Biscay–Iberia , and the oceanography areas. The two areas are closely integrated Mediterranean Sea. EuroGOOS and its ROOSes have played and provide a basis for building up European operational an active role in data exchange, sharing the best practice and oceanography, which will be described in the Sects. 2 and knowledge, harmonizing monitoring networks and forecast- 3. (iii) and (iv) are identified as two of the major emerg- ing systems, and stimulating joint research activities. Since ing operational oceanography areas where the operational Framework programme IV, the European Commission (EC) approaches based on the scientific state-of-the-art are still has continuously supported research on integration and de- under development and which have to increase the signifi- velopment of European operational oceanography monitor- cance in supporting sustained socio-economic development. ing and forecasting systems, especially through Operational Such an operational approach will provide a sustained devel- Forecasting Cluster projects (Cieslikiewicz et al., 2004), opment and service platform and significantly improve ef- MERSEA (Marine Environment and Security for the Euro- ficiency, quality and timeliness of the current services sup- pean Area, Johannessen et al., 2006) and the GMES (Global porting Blue Growth, especially for the implementation of Monitoring for Environment and Security, currently referred integrated coastal zone management and ecosystem-based to as Copernicus) Marine Service programme (Bahurel et al., management. The research in (iii) and (iv) can benefit from 2010). The development in the last 20 years has helped ad- (i) and (ii), but also develop in their own directions as emerg- vance the existing national services and establish new ones ing research areas. Details can be found in Sects. 4 and 5. It in many of the European countries. At the European level, an is notified that the areas (iii) and (iv) are partly overlapping integrated capacity – the MyOcean operational monitoring with (i) and (ii) but with different focuses and ambitions. A and forecasting systems for global, Arctic and European re- summary and discussion is given in Sect. 6, to provide a har- gional seas – has been established, which is now transformed monized overview and address some missing issues of the into the Copernicus Marine Environmental Monitoring Ser- paper. vice (CMEMS, http://marine.copernicus.eu/) programme in the period 2015–2020. Thanks to these national- and EU-funded programmes 2 European ocean observations we have seen major scientific achievements in the develop- ment of Earth Observation (EO) data management, short- Since the establishment of EuroGOOS, it has been a central term forecasting systems (including data assimilation) and focal issue of EuroGOOS research to sustain, enhance, and reconstruction of a long-term historical database through re- optimize the European ocean observing systems (Prandle et analysis and reprocessing. Long-term prediction, ecosystem al., 2003; Nittis et al., 2014). With dual roles in ocean mon- prediction, coastal services and optimization of European itoring, i.e. both as observation providers and users, Euro- marine monitoring systems have also been improved but with GOOS members have different concerns. As a data provider, one needs to maximize the value of end-to-end data delivery

Ocean Sci., 12, 953–976, 2016 www.ocean-sci.net/12/953/2016/ J. She et al.: Developing European operational oceanography for Blue Growth 955 and improve the cost-efficiency for making observations; as human activities, both online and offline. All these initiatives a user, one requires easy, fast, and open access to a maximum are and should be further coordinated. EuroGOOS members of available qualified observations for operational oceanog- are directly involved in EMODnet and the CMEMS In-situ raphy applications. TAC, and this ensures that these two major initiatives con- Maximizing the value delivery: as monitoring agencies, tribute to the overarching goal of facilitating the access to EuroGOOS members are responsible for delivering observa- ocean data for operational oceanography. EuroGOOS also tions with maximized benefits to users for supporting Euro- has a vision on observing systems for a close dialogue with pean Blue Growth and public affairs: major users (e.g. COPERNICUS Marine Services) in order to align efforts to their requirements (and take advantages of – Values from data to product: improving observational feedbacks) and at same time to influence/harmonize the de- data use for core marine products through (i) the timely velopment of the national components. delivery of available observations for operational use; Operational monitoring and data handling in emerging ar- (ii) the maximum use of observations in analysis, fore- eas: our knowledge on marine ecosystems is evolving in the cast, reanalysis and reprocessing; (iii) improved under- process of serving the growing blue economy and ecosystem- standing of product skill through improved use of ob- based management, and new challenges are also identified servations in validation and verification activities. for data and information needs in emerging areas. Such – Values from data to knowledge: new knowledge gener- emerging areas include, but are not limited to, bottom sedi- ation by using observations together with models to un- mentation and resuspension, ocean acidification, marine pol- derstand physical and ecosystem processes and improve lution related to noise and marine litter, especially plastic, model parameterizations/forecasts. paraffin, etc. These areas are normally beyond the exist- ing scope of operational oceanography; hence, new monitor- – Values from data to socio-economic benefit: exploiting ing and modelling technology should be developed. Further- societal value of marine observations through innova- more, it becomes increasingly important to integrate “non- tive fit-for-purpose socio-economic applications in a va- operational” observations, e.g. from tagged marine mam- riety of social benefit areas by using observations to- mals, offshore commercial platforms, and research observa- gether with models and sectorial data. tories, as well as sectorial information, e.g. ship data from the Improving the cost-efficiency: EuroGOOS members need Automatic Identification System, into an operational moni- to undertake cost-efficient monitoring activities. This re- toring and data management framework. quires research and development on the assessment and de- Research on European ocean observations will aim at de- sign of cost-effective ocean observing networks through op- livering the above objectives. The basic aspect of this re- timization of sampling strategy, integration and coordina- search is to integrate existing observational infrastructure in tion of observational infrastructure and efficient data man- operational oceanography. As emphasized in the EuroGOOS agement. Strategy Plan (2014–2020), (Nittis et al., 2014), EuroGOOS Data access and harvesting for operational oceanogra- will promote the need for the development of an integrated phy applications: EuroGOOS needs to quantify the needs European Ocean Observing System (EOOS) during the com- of ocean observations for operational oceanography appli- ing years in partnership with the EuroGOOS ROOSes. The cations, including parameters, data quality, sampling density proposed system will be based to a large extent on past and and delivery time window. This analysis is instrumental to planned investments: national systems, regional collabora- produce a coherent vision on future development of the ob- tive observing programmes such as FerryBox and voluntary servational component and its research and innovation prior- observing ships, European programmes, and research infras- ities. In addition, timely access to the observations, both in tructures such as Euro-, JERICO-NEXT, FixO3, EGO, online and offline modes, must be ensured. This requires Eu- and HF radars. However, following a system approach im- roGOOS to work closely with other European ocean moni- plies an additional level of operational networking and a gov- toring and data providers and management centres. Among ernance scheme that will allow common programming and the former are the environmental monitoring agencies co- joint investments. ordinated under regional conventions (Helsinki Convention, EuroGOOS is taking the initiative in leading and coordi- Oslo and Paris Convention, and Barcelona Convention) and nating activities within the various observation platforms by EEA, fishery monitoring community and research and com- enhancing the ROOS cooperation and establishing a num- mercial monitoring communities. Data management centres ber of ocean observing Task Teams such as HF radar, glider, include ICES for handling marine and ecosystem data from FerryBox and gauges, and with strong links to Euro- the Baltic and North Sea, SeaDataNet for managing the of- Argo and its European legal entity Euro-Argo ERIC (Euro- fline physical and biogeochemical data, the CMEMS In-situ pean Research Infrastructure Consortium). The purpose is to Thematic Assembly Centre (TAC) for real-time and delayed get these groups well organized, creating synergy within the mode data required by the CMEMS and EMODnet for man- Task Teams themselves and across the Task Teams. This ef- aging all types of marine data ranging from physical data to fort will be carried out in collaboration with the European www.ocean-sci.net/12/953/2016/ Ocean Sci., 12, 953–976, 2016 956 J. She et al.: Developing European operational oceanography for Blue Growth

Marine Board and other initiatives such as JPI-Oceans (the improve the sustainability; (iv) deliver new observations for Joint Programming Initiative Healthy and Productive Seas operational oceanography; and (v) improve the efficiency of and Oceans). managing and using big data. To reach these goals, the fol- Besides the progress made in in situ marine observing, lowing challenges have been identified. satellite oceanography has also been significantly advanced in the last 2 decades and become a major component of 2.1.1 Short- to mid-term objectives operational oceanography, as documented by Le Traon et al. (2015). Satellites provide real-time and regular, global, – Reducing the observation gaps: integrating existing high spatial and temporal resolution observation of key ocean non-operational, multi-source observations at regional variables that are essential to constrain ocean models through level to ensure more timely access, delivery, and us- data assimilation and/or to serve downstream applications. age of observations for analysis/forecasting and regu- Future research on European ocean observations will lar ocean state estimation; identify critical “data de- evolve with advances in the observation capacities, such as livery time windows” for operational forecasting and the variety of Argo profiling floats (e.g. Bio-Argo, shallow- harmonize the data format, metadata, and quality stan- water Argo, abyssal Argo, and under-ice Argo), innovative dard; integrating new observations into the existing op- in situ monitoring (e.g. ITP – the Ice Tethered Profiler, ice erational data flow, promoting the historical data gath- mass balance buoys, FerryBox, and gliders), cabled obser- ering in coordination with EMODnet (in particular for vatories, and ocean acoustics. Moreover, integration with biogeochemical variables); widening the usage of inno- satellite-based observations, both polar-orbiting and geosta- vative cost-effective monitoring technology, e.g. Ferry- tionary satellites, is highly important. The outlook on future Box, HF radar and Bio-Argo, in operational monitoring. missions within the next decade is promising. The satellite – Ensuring open availability of innovative multi-sensor constellation should be improved and new missions with a satellite observation retrieval algorithms for essential potentially large impact for operational oceanography (such ocean and ice variables with higher quality: using in situ as the Sentinel missions) should be demonstrated. Interna- measurements and multi-variate met-ocean data to cal- tional collaboration will be crucial to optimize and make best ibrate, validate, and improve the relevant remote sens- use of the satellite observations (e.g. sensor synergy, cali- ing data and products, including possible new products bration, and validation) from the growing number of space derived from space infrastructures both in Europe and agencies. Moreover, more efforts will also be required to en- other countries such as the USA, China, Japan, and In- sure homogenized and inter-calibrated data sets from multi- dia. ple missions for all essential ocean variables. The on-going and forthcoming EC Horizon 2020 sup- – Coordinated use of marine infrastructures at regional ported projects such as AtlantOS for the Atlantic Ocean and level: for instance, in multi-lateral coordination of re- JERICO-NEXT for coastal observatories, and the calls on the search vessel-based monitoring, mobilization of ad- Integrated Arctic Observing System and the Mediterranean ditional relocatable observational infrastructure (e.g. Observing System with submission in February 2016, will AUVs, gliders, and drifters) with coordinated sam- strengthen the integration of European ocean observing sys- pling schemes. Although difficult, coordinated monitor- tems. ing planning such as on-ship time, sampling locations, In the long run, it is foreseen that European ocean observa- and mobilization of the observational infrastructure can tions will become more integrated, coordinated, and efficient. make significant improvements in terms of the cost and The related activities will be described below in two cate- benefit. gories: development and integration of ocean observing sys- – Testing the effectiveness of existing (semi)automated tems and assessment and optimization of observational net- sensors for chemical and biological observations. works. The former is dedicated to maximum value delivery of observations, ad hoc optimization of monitoring networks, – Data processing: further development of real-time qual- and data harvesting for operational oceanography, with the ity control protocols; development of advanced data latter to improve the cost-effectiveness of the EOOS through products (value-added) merging different types of ob- quantitative impact and design studies. servations, especially those including new satellite and in situ observations; establishing a systematic and con- 2.1 Development and integration of ocean observing sistent observation-based analysis framework as sug- systems gested by Chapron et al. (2010). 2.1.2 Longer-term objectives The goals of the integration of the ocean observing systems are to (i) maximize the number of timely and quality assured – New observations: filling the monitoring gaps in key observations for operational oceanography; (ii) improve the locations by deploying innovative multi-platform sen- cost-effectiveness of current monitoring components; (iii) sors; promoting the development of a deep-sea network

Ocean Sci., 12, 953–976, 2016 www.ocean-sci.net/12/953/2016/ J. She et al.: Developing European operational oceanography for Blue Growth 957

of gauges (needed also for calibration of satel- to the GEOSS philosophy (compliant where necessary lite sea-level products); developing a limited number of with ISO (International Organization for Standardiza- supersites located in critical areas (in particular in the tion) standards) based on interoperable web services. open sea) with a multi-platform approach; developing marine mammal tagged observations; and developing 2.2 Assessment and optimal design of ocean observing operational monitoring instruments and data handling networks tools for underwater noise and marine litter. The goal of the marine monitoring network assessment and – Integration of observations from the research commu- optimal design research is to identify the gaps in existing nity and private sectors: with the progress of engaging observing systems and to optimize their cost-effectiveness. research community (e.g. promoting the use of data doi) The EC has continuously supported this research area since and private sectors in operational oceanography, the ob- early 2000. The assessment and design studies can be divided servations made by them should be collected and shared into ad hoc studies and quantitative studies. The ad hoc stud- for operational oceanography research and other sec- ies have been carried out in many EC-funded observing sys- ondary uses. tem projects such as EDIOS, SeaDataNet, and recent fit-for- – Coordinated and cost-effective deployment of multi- purpose assessment by DG-MARE (the Directorate-General platform infrastructure at regional level, e.g. high- for Maritime Affairs and Fisheries) Sea Basin Checkpoint quality ship-board and bottom-mounted ADCP moni- projects for European seas. The ad hoc assessment work has toring, FerryBox, HF radar, moorings, cabled stations, led to the establishment of the meta-database and identi- and innovative use of lighthouses and other offshore fication of data availability and accessibility. On the other platforms. hand, a variety of quantitative assessment and optimal de- sign research have also been carried out in EC projects – Transferring, expanding, and integrating mature, cost- ODON, ECOOP, JERICO and OPEC, and are now contin- effective monitoring technology, e.g. HF radar for gen- uing in JERICO-NEXT and AtlantOS. Both statistical as- eral operational use. sessment and optimal design methods as well as assimilative model-based method – OSE (Observing System Experiment) – New technology for operational monitoring: developing and OSSE (Observing System Simulation Experiment), have cost-effective multi-sensors and robust calibration pro- been developed and applied in these projects. Large parts tocols, especially for biogeochemical measurements, of the physical and biological operational monitoring net- sediment, underwater noises, and marine pollutants. work (SST, T /S, nutrients, , and Chl a) in European seas have been assessed in terms of effective coverages and – Exploring the operational potential of present and inno- explained variance (She et al., 2007; Fu et al., 2011). The vative initiatives in the field of citizen observations (sea OSEs and OSSEs have also been applied in assessing and state observation, marine litter, ocean colour, jellyfish, optimizing physical monitoring networks, e.g. in FP5 project etc.). ODON and FP7 project JERICO. The strengths of OSEs and – Efficient big data management: it has been a chal- OSSEs are that impacts of a given sampling scheme can be lenge to quickly access and extract increasing amounts quantitatively assessed in terms of improvements of forecasts of Earth Observation (EO) data, which can be on the (Oke and Sakov, 2012; Turpin et al., 2016). The weakness order of peta- to exa-byte scales. The Earth System is that the results are model dependent and it can only ad- Grid Framework has been developed to facilitate data dress one sampling scheme per simulation. The statistical extraction from multiple data centres. However, bot- method has the strength of being a quick assessment and can tlenecks exist inside each data centre for online ac- be easily applied to find one optimal sampling scheme among cess to medium amounts of data (102–103Tb). An ef- many given candidates. A potential integration of the two ap- ficient data management framework should be devel- proaches is expected to combine the relative strong points. oped for online access, downloading, viewing and anal- ysis of data from a distributed multi-server local net- 2.2.1 Short- to mid-term objectives work. Novel technologies will be foreseen to move to- ward an open source array-oriented database manage- – Quantitative assessment of gaps and redundancy for ment system. Further development of data mining and operational forecasting: assessing representativeness, image processing techniques is needed to facilitate the sampling error, and impacts of European marine mon- automatic extraction and analysis of patterns from big itoring in situ components (including non-operational data sets. components) on operational analysis and forecasting to identify critical gaps and redundancy areas, while in- – Interoperability: identifying a strategy to move from the cluding existing satellite data, modelling, and assimila- NetCDF, file transfer-based, data exchange technology tion techniques. www.ocean-sci.net/12/953/2016/ Ocean Sci., 12, 953–976, 2016 958 J. She et al.: Developing European operational oceanography for Blue Growth

– Development of automatic observation network evalua- tion tools which can provide estimates of quality param- eters of the network, such as effective coverage, sam- pling error, explained variance, reconstruction error, and forecasting error, for sampling schemes defined by the users.

– Impact study method development: development of more robust methodologies (i.e. to ensure results as in- dependent as possible of model and error assumptions) to conduct impact studies.

2.2.2 Longer-term objectives

– Optimal design: identification of critical observation gaps and redundancy in parameters, space, and time; providing quantitative optimal designs of new cost- effective components of EOOS as well as guidance to the in situ observing communities on how to opti- Figure 1. Schematic of grand challenges from the “Earth System mize observing strategies (e.g. sampling scheme, tech- Science for Global Sustainability”. Source: ICSU (2010). nology) and the complementarity with Sentinel mis- sions; adopting an integrated, user-driven and science- and technology-based design approach by combining 3 Operational modelling and forecasting technology the relevant scientific, technological, and management resources. Modern ocean and ecosystem prediction and state estimation is built upon a combination of ocean models and observa- – Improvement of monitoring schemes at regional level: tions. The advanced science and technology in forecasts is based on impact and/or design study, identifying moni- at the centre of Earth system science challenges, as shown toring cases with significant cost-effectiveness improve- in Fig. 1, together with innovating, observing, responding to ment in the integration of existing systems, ship time and confining the impacts (ICSU, 2010). The accuracy of the planning, integrated and/or mobilized use of obser- ocean prediction relies on the model quality both in dynam- vational infrastructures, etc.; implementing the cases ics and numerical solver, model set-up, quality and amount by integrating monitoring technology (in situ and re- of forcing data and observation data, and the quality of pre- mote sensing), sampling schemes, monitoring objec- processing, assimilation, and post-processing technology. In tives, modelling capacity, user needs, and investment as this section we divided the modelling-related research areas a whole. Detailed knowledge should be developed on into model development and forecasting technology, e.g. data how different monitoring platforms, assimilation, and assimilation, nowcasting, and probabilistic forecast. understanding of dynamic processes can benefit each other to reach a cost-effective design of the system. De- 3.1 Model development livery time vs. user needs should also be mapped and evaluated for both physical and biogeochemical vari- In recent years seamless modelling and forecasting system ables. development has become a major focus to develop a unified framework for modelling and forecasting on both weather – Promote, design and carry out large-scale, integrated and climate scales (Shukla, 2009). Recently the WMO pub- field experiments: in order to make breakthroughs in lished the scientific report, “Seamless prediction of the earth new areas of operational oceanography, such as for system: from minutes to months”, which announces a new coastal shallow waters and operational ecology, dedi- era of development of our forecasting capacity into Unified cated large-scale field experiments are needed with an Earth System Models – UEM (WMO, 2015). Some coun- integrated monitoring–modelling approach. The knowl- tries, such as the United Kingdom and the USA, have worked edge and technological gaps should be identified, filled on a seamless approach to weather and climate prediction and transformed into the corresponding monitoring and by developing common modelling tools for weather and cli- forecasting systems. Examples with more details can be mate for years. For the ocean–sea ice–wave–ecosystem pre- found in Sects. 4 and 5 – Coastal Operational Oceanog- diction, existing boundaries of prediction between different raphy Experiment and Operational Ecology European timescales were mainly delimited due to computational and Experiment. model complexity considerations. Current CMEMS opera-

Ocean Sci., 12, 953–976, 2016 www.ocean-sci.net/12/953/2016/ J. She et al.: Developing European operational oceanography for Blue Growth 959 tional models such as NEMO, HYCOM, and HBM have also plications, there still exist significant challenges in improving been used in the long-term simulations such as hindcast, re- the computing efficiency and energy and mass conservation analysis, and climate projections. It is timely to build the features of the operational models. The benchmark test of the next-generation European operational ocean–sea ice–wave– climate UOM should be made for above two issues. ecosystem models in the framework of the Unified Ocean The computational aspect of the UOM concerns both com- system Model (UOM). putation speed and total consumption of electricity. Compu- The UOM means that the ocean subsystem models (i.e. tational efficiency is the key both to enhance the speed and ocean, sea ice, waves, sediment transport, marine ecosys- reduce the total energy consumption. Forecasting and climate tems) are able to serve the purpose of applications on all modelling for the entire coupled ocean system in a proba- timescales, ranging from nowcasting to climate projections. bilistic framework are extremely computational demanding. This requires that the model (i) has a high coding standard, For future seamless modelling, the minimum requirement is flexible grid and efficient numerical schemes to meet com- that the UOM should fulfil computational limits for both op- putational needs for both operational forecast and climate erational and climate modelling, e.g. delivering a 5–10 day modelling; (ii) is able to properly resolve small-scale features forecast daily within 2 h and a hundred year run within a few and extreme events as well as other features needed for op- months. In addition, the model code should be optimized in erational services; and (iii) meets the energy and mass con- order to minimize the total electricity consumption, which servation requirements for long-term simulations. The UOM needs close cooperation between model developers, HPC ex- should also be fully coupled between the subsystem models perts, and hardware producers. and the Unified Atmospheric Model (UAM). In order to use the operational UOM for climate applica- Operational ocean modelling has been significantly ad- tions, the model should be able to generate a stable vanced in the last 20 years in Europe. A great number of (with no significant trend) by running for several hundreds physical ocean–ice models have been developed and used of years without including anthropogenic effects. This serves in operational forecasting, such as NEMO, HBM, HYCOM, as a basic requirement (of energy and mass conservation) for ROMS, and MITGCM. In recent years a very strong move- climate modelling. The development of UOM is a long-term ment in the physical ocean modelling community is the goal which may be reached in 10 years or even longer, while NEMO model development, with supports from both the na- the short- to mid-term model development will be mainly tional and European levels. More and more countries are driven by large-scale operational oceanography projects such starting to use NEMO as their operational model. On the as CMEMS and those in Horizon 2020 calls which mainly fo- other hand, using different models in Europe for opera- cus on developing the existing modelling framework at basin tional forecasting is also necessary, as no single model can and global scales. The ideal situation is that the short- to mid- solve all problems. Quite a few ecological models have also term European ocean model development can be effectively been developed for operational forecasting, such as ERSEM, integrated into the UOM framework. ERGOM, BFM, ECO3M, BIMS_ECO, NORWECOM, and In the short to mid-term, the objective of the model de- ECOSMO. High trophic models have also been developed velopment work is to develop a European UOM framework for the forecasting purpose, e.g. in the OPEC project. The and continuous improvement of the deterministic prediction state-of-the-art European wave models and ocean–wave cou- models with a forecast range of 10 days or longer. The re- pling have been further advanced for operational forecasting search should focus on (i) designing the UOM concept and in the MyWave project, which is an important step towards framework and developing a road map towards the UOM; Copernicus wave service. (ii) improving description of model processes so that each There will probably be in the future several prototype Eu- UOM sub-model can effectively model major features in ropean UOMs, depending on further development of the ex- the subsystem; (iii) improving high-performance computing isting state-of-the-art and available resources (both funding through code modernization; (iv) improving the UOM sub- and modelling expertise) in Europe. Some UOMs may have system coupling and UOM-UAM coupling; and (v) develop- a capacity to covers a wide range of spatial scales ranging ing high-resolution models with flexible grids and interfaces from coastal to global ocean. Others may only cover multi- with basin- and global-scale models, and resolving coastal basin, basin and coastal oceans. processes for downstream applications. Some of the above The operational ocean models for the European seas pro- research topics, such as increased resolution, improved pa- vide nowcasting and forecasting ranging from hours to days, rameterizations, and atmosphere–ocean–sea ice–wave cou- which have to resolve mesoscale and smaller scales, high- pling, have been addressed in the research priorities of the frequency phenomena, and extreme events. The models have CMEMS Service Evolution strategy (CMEMS STAC, 2015). to be calibrated to reach certain quality standards to meet Modelling framework development: in the European the user needs, and are regularly verified against observa- ocean modelling community, a road map towards the UOM tions. These models have also been used for generating hind- is needed, which shall cover but not be limited to coding stan- cast, reanalysis, and climate projections. However, in order dards, code adaptation to many-core computer architectures, to use the existing operational models for climate-scale ap- coupling frameworks, new model components, e.g. sediment www.ocean-sci.net/12/953/2016/ Ocean Sci., 12, 953–976, 2016 960 J. She et al.: Developing European operational oceanography for Blue Growth transport and high trophic level models, and sharing of best Emerging modelling areas: in order to develop future practices of the model development. Detailed analysis of UOM, integration and extensions of current European capac- user and computational needs on the future UOMs should be ity in spatial–temporal scales and parameter dimensions are made. The best practices from both ocean and atmospheric needed. The existing basin-scale operational models (ocean– model development should be used to develop such a road sea ice–wave–biogeochemistry) can be evolved to resolve es- map. tuary and straits, while existing estuary–coastal sea models Integration of best practice into the UOM framework: due can be extended to cover multi-basins. New emerging mod- to the lack of resources at national level for ocean model de- els such as sediment transport and high trophic level models, velopment it is very important to share best practice in oper- models for downstream services such as coastal inundation ational modelling. One way to share best practice is through models, and unstructured grid models need to be further ma- community model development such as NEMO. There are tured and integrated with existing operational systems. In ad- also a few initiatives started recently to develop a Research dition to the model development, comprehensive verification to Operations (R2O) strategy meeting the needs for modern- studies should be made especially for the ecological models ization of numerical models to support the forecasting pro- and models in the Arctic in order to understand their draw- cess. One of such interesting platforms is the hurricane R2O backs. For the ice model, mesoscale sea ice rheology will be developmental testbed (Bernardet et al., 2015), an initiative needed to describe lead dynamics of the ice. More discus- hinging on three activities: establishing a solid code manage- sions on the development of marine ecosystem models can ment practice, supporting the research community in using be found in Sect. 5 – Operational Ecology. the operational model and inserting innovations and conduct- The above short- and mid-term research will significantly ing model testing and evaluation in a well-established and improve the efficiency and accuracy of the model perfor- harmonized framework. Such ideas, though applied in mete- mance at synoptic scales, which will provide a basis for orology, can also be useful in the establishment of the UOM building up European UOMs. In the long term, it is important framework. Concerted action among the European modelling to reach breakthroughs in seasonal forecasting for the Euro- groups is also important for integrating the progress in the pean earth system and to improve the quality and efficiency different modelling groups into the future UOM framework. of the UOMs in generating climate simulations. The re- EuroGOOS has initiated a Coastal and Shelf model Working search here focuses on probabilistic forecast, coupled UAM- Group (COSMO) to promote the model knowledge exchange UOM models with multi-grids and medium–high resolution, and best-practice sharing. and efficient high-performance computing for global, multi- Improving deterministic models: although operational basin, and coastal scales. The research is a further exten- physical ocean models are much more mature than the eco- sion and integration of the existing deterministic UAM-UOM logical models, there still exist well-known challenges such modelling framework which has been developed in the short- as unrealistic diapycnal mixing, resolving bottom layers and and mid-term research. sharp pycnoclines, flow over steep topography, water ex- In the long term, UOMs for solving problems at pan- change through narrow straits, configuration of surface fluxes European seas and the Arctic–North Atlantic scale should in a coupled framework, vertical transport of substances, sub- be developed. Since European regional seas are connected grid parameterization, binary identical code, and the capac- by straits (some with widths of a few hundred metres to ity for using new high-performance computing architectures. kilometres), the UOMs for climate-scale applications have Progress in the above areas will directly improve the model to resolve such scales in order to model correctly the inter- quality. basin transport. Besides, implementation of European poli- Development of coupled systems: research in the devel- cies, such as the Climate Directive, Common Fishery Pol- opment of the coupled system and predictability study will icy and Marine Strategy Framework Directive, needs a har- evolve in the Horizon 2020 programme and the Coperni- monized European seas database to support the decision- cus Service, especially CMEMS systems. While coupled making. A UOM at pan-European scale will fit this purpose. atmosphere–ocean–ice–wave models have been developed at The model system should be able to resolve and/or permit a global level for climate research and seasonal forecast- mesoscale eddies and resolve narrow straits. The current op- ing, regional coupled systems for synoptic-scale prediction erational models, such as the UOM developed for determinis- remain to be developed. Proper implementation of the air– tic prediction, can be further developed for this purpose with sea–ice interaction and data assimilation for the coupled sys- two-way nesting. Other alternatives include unstructured grid tem are essential for correctly resolving corresponding diur- models. nal variability. Predictability is expected to be prolonged in a For the seasonal and longer scales, it has been found coupled forecasting system, which should be explored. The that the Arctic condition has great impacts on the Euro- future development will also contribute and draw momentum pean weather and climate. An Arctic–North Atlantic cou- from the on-going GODAE-OceanView (Brassington et al., pled atmosphere–ocean–ice–wave component should be de- 2015). veloped as a key part of the future European Earth Sys- tem Model. The advantage of the regional coupled Arctic

Ocean Sci., 12, 953–976, 2016 www.ocean-sci.net/12/953/2016/ J. She et al.: Developing European operational oceanography for Blue Growth 961 system is that high resolution can be used and research ef- open oceans, satellite measurements such as sea surface tem- forts can be focused on the Arctic-related processes such as perature, sea ice and sea surface height and in atmosphere–ocean–ice coupling and sea ice dynamics. A few situ observations of SST and T /S profiles have been assimi- regional coupled atmosphere–ocean–ice systems, e.g. RASM lated in global and regional forecasting systems for the North (Maslowski et al., 2012) and national systems in Sweden, Atlantic, Arctic, and Mediterranean seas, such as in CMEMS Norway, and Denmark, have already been tested for Arc- marine forecasting centres. For coastal and shelf sea assim- tic climate research. The development of the future Arctic– ilation, there have been a number of successful stories, e.g. North Atlantic coupled model should also take the advantage sea-level assimilation in North Sea storm surge forecast (Zijl of the Horizon 2020 Blue Growth Calls on Arctic: BG9 – et al., 2013), SST assimilation in CMEMS NW shelf MFC, Integrated Arctic Observing System and BG10 – Impact of and assimilation of SST, sea ice concentration, and T /S pro- Arctic on weather and climate in the Northern Hemisphere files in the Baltic Sea. and Europe, as well as the Year of Polar Prediction (YOPP). Major challenges in operational assimilation remain in As mentioned before, it is essential that the Climate UOM the coastal and shelf waters for assimilating both should be adapted to the multi-core and many-core super- from satellite and in situ tidal gauges, surface currents computing processors with efficient and balanced hybrid par- from HF radar, ice thickness and ice drift, as well as for allel computing. The current model code may have to be assimilating biogeochemical parameters. In this area, tra- modernized, as reported recently in the high-performance ditional Gaussian-distribution-based assimilation methods computing workshops organized by ECMWF and NCAR such as 3DVAR or Kalman filter-based methods have shown (National Center for Atmospheric Research). improvements and potential for operational applications, For example, a stricter coding standard should be applied such as in assimilating blended satellite in situ sea-level to ensure the run-to-run reproducibility. A more efficient cod- data in the Baltic–North Sea in the eSurge project, satel- ing principle such as PSyKAl (Parallel System, Kernel and lite Chl a assimilation in the OPEC project (http://www. Algorithm), taken in the GungHo Project which is develop- marine-opec.eu/documents/deliverables/D2.6.pdf), and Fer- ing a new dynamical core suitable for the weather and cli- ryBox SST/SSS/HF radar surface current assimilation in the mate simulations, may benefit the UOM development; up- German COSYNA project (Stanev et al., 2013, 2015). How- grading the code with the SIMD (single instruction multiple ever, technical difficulties remain, especially in cases with data, Poulsen et al., 2014) feature has proven the benefit for large spatial and temporal variations and high non-linearity, the model by using new vectorization and efficient hybrid relatively large model uncertainties, and insufficient real- threading for multi-core and many-core architectures. time observations. All these factors, especially when added together, may often lead to non-Gaussian model error statis- 3.2 Forecasting technology tics which cannot be solved properly by traditional assimi- lation methods based on non-biased Gaussian distribution of Advanced model code does not necessarily mean a good error statistics. Severe model instability or unrealistic correc- forecast. Initial and forcing errors are two major additional tion of the model initial fields may be generated. factors limiting the forecast quality. There are normally two New, innovative assimilation methods such as stochastic ways to deal with the initial error: one is assimilating obser- assimilation methods and a common data assimilation frame- vations to obtain a more realistic initial field; the other is to work such as PDAF (Parallel Data Assimilation Framework) perturb the initial field to generate ensembles which will be have been developed in the FP7 SANGOMA project. Inde- used to make a probabilistic forecast. The benefit of the en- pendently of SANGOMA, other efforts on modular software semble forecast is that (at least) the white noise of the fore- development have also been initiated at other European insti- cast can be largely removed by using the ensemble mean, tutions, such as the OOPS project at ECMWF. The following and the probabilistic forecast gives a valuable estimation of research and development activities on data assimilation are forecast uncertainties; furthermore, the method enables pos- required. sibilities for . In this section we focus on the future research on ocean data assimilation and ensemble In the short to mid-term forecasting technology. – Common assimilation framework developments: devel- 3.2.1 Data assimilation opment of community tools and diagnostics in observa- tion space, sharing of assimilation tools with the ocean The reduction of the product uncertainties is a central chal- modelling community and observational experts; verifi- lenge for operational modelling and services, which requires cation methods and inter-comparison protocols suitable continuous innovations in data assimilation. Present-day as- to probabilistic assimilation systems. similation approaches encompass a hierarchy of methods of increasing complexity, ranging from optimal interpolation to – Transferring existing best practices into operational sys- non-linear stochastic methods (CMEMS STAC, 2015). For tems: calibrating and operationalizing mature assimi- www.ocean-sci.net/12/953/2016/ Ocean Sci., 12, 953–976, 2016 962 J. She et al.: Developing European operational oceanography for Blue Growth

lation schemes for observations from research vessel, developing these methods for marine short-term forecasting buoys, FerryBox, HF radar, altimetry, and tidal gauges (Counillon and Bertino, 2009). for coastal and shelf seas. Probabilistic forecast for waves and physical ocean condi- tions has been developed and used in European operational – Development of new assimilation methods: stochas- oceanography in the last decade, both with ensemble and tic assimilation methods, hybrid assimilation methods (multi-model) super-ensemble forecast. ECMWF has oper- and assimilation methods addressing non-Gaussian er- ated global ocean wave ensemble forecasting for some years. ror statistics. A regional Baltic–North Sea wave ensemble forecast was – Development of assimilation of new and novel ob- put into operation in 2014 in the MONALISA2 project. In- servations: ice thickness, currents, nutrient profiles creasing use of the ensemble data assimilation method also and plankton; new data assimilation methods de- provides a natural platform for making 3-D ocean ensem- signed to handle strongly nonlinear dynamics and semi- ble forecasts. For the European seas, multi-model water-level qualitative information from satellites. prediction has been developed for European seas in ROOSes and in the ECOOP project, and used for national storm surge In the longer term forecasts since the early 2000s (Perez et al., 2012). Further development of multi-model ocean forecasting systems has – Further development of innovative assimilation meth- been an active part of MyOcean and CMEMS (Golbeck et ods: improving atmospheric forcing using available ob- al., 2015). servations via the ensemble Kalman filter and smoother; However, essential challenges in the ocean non-Gaussian extensions for non-linear transformations ensemble/super-ensemble forecast remain: due to the of probability distributions to reduce data assimilation insufficient coverage of all kinds of uncertainties when gen- biases by more realistic stochastic models; development erating the forecast ensembles, the ensembles often partly of hybrid data assimilation method; developing and im- contain the truth and cannot form an ergodic set; inefficient plementing advanced techniques to assimilate data into generation of the ensembles often leads to convergence of coupled ocean-ice-wave-atmosphere model systems. the ensembles, which makes this issue worse. Multi-model ensemble in a certain sense effectively increases the number – More details on the above research priorities can be of independent ensembles and has shown very good results found in the CMEMS Scientific Strategy (CMEMS in ensemble forecasts. Furthermore, the ensembles may not STAC, 2015). be Gaussian distributed and non-biased. In order to get a 3.2.2 Probabilistic forecasts and forecast uncertainty proper estimation of forecast uncertainty, a probability dis- quantification tribution function (pdf) based and bias-corrected uncertainty estimation should be developed and applied. and management has been set as a standard In the short to mid-term, research is needed for establish- requirement for many sea-going operations and policy mak- ing a framework for ocean model probabilistic forecast vali- ing, which raises needs for probabilistic forecasts and esti- dation; building up probabilistic forecasts through advancing mation of the forecast uncertainties. Due to the lack of ocean ensemble-based assimilation; improvement of ocean model observations, it is not easy to quantify the forecast uncer- ensemble generation with more effective perturbation of ini- tainties by comparing the model data with observations. One tial states, forcing, lateral boundary conditions, and model way to estimate the model product uncertainties is to use sin- shortfalls to get close to an ergodic set of ensembles; and fur- gle model ensembles or multi-model (super-ensemble) fore- ther development of multi-model ensemble forecasting and casts. Through perturbing the initial state, the lateral and ver- transferring to operations and advancing the ensemble/super- tical boundary condition errors and/or the model shortfalls ensemble forecast by including real-time observations and in a sufficiently large range, it is expected that an ergodic model output statistics (MOS) for forecast corrections. set of the forecast ensembles can be generated which con- It is obvious that seamless forecasting has to be treated in tains the true solution (the truth) as a subset. In this case, a probabilistic way for a fully coupled system. In the long a probabilistic forecast can be estimated from the ensem- term, efficient methods should be developed for estimating ble and/or super-ensemble products according to different the forecast uncertainty, including bias correction and non- user requirements, e.g. the probability of the significant wave Gaussian distribution of the ensembles. With the Unified height being higher than 5 m within the next 24 h. The best Earth System Models developed for the pan-European sea estimate of the forecast and its spread can also be derived. and the Arctic–North Atlantic scale, a probabilistic frame- With a Gaussian-distribution assumption, the spread can be work should be developed for seasonal forecasting and cli- used as an estimation of the forecast uncertainty. A frame- mate projections. The predictability study is needed to un- work of probabilistic forecast production, validation and ap- derstand and assess the predictability of the ocean circula- plication has been well established in meteorology but much tion, biogeochemistry and marine ecosystems at global, basin less in oceanography. Operational oceanography is presently scale or regional scale, and to identify spatial and temporal

Ocean Sci., 12, 953–976, 2016 www.ocean-sci.net/12/953/2016/ J. She et al.: Developing European operational oceanography for Blue Growth 963 scales with the strongest predictable signals in model system pean structural funds). Monitoring for commercial purposes dynamic processes, initial states and forcing. For the histori- also represents a significant data source. However, the value cal data, the probabilistic framework and metrics are needed of existing observations in the coastal waters has far from for the ocean reanalysis using ensemble techniques. Meth- been fully exploited, especially for operational oceanogra- ods should be developed to ensure quality, homogeneity, and phy. First, project-oriented observations have been poorly in- robust uncertainty measures in the long-term time series re- tegrated into operational data flow for forecasting; second, constructed from data or model reanalyses. new knowledge generated from the high-resolution observa- tions in the coastal waters is still limited; third, the coastal observations have rarely been assimilated into operational 4 Operational oceanography in the coastal ocean models in near-real-time mode. In the next few years, a large number of high-resolution The coastal oceans, including coastal zones and offshore and satellite observations will be available, including the ocean open coastal waters, are important economic zones and key colour (Sentinel 3), sediment (FCI from Meteosat Third Gen- areas of European Blue Growth. One-third of the EU pop- eration), and coastal altimetry (Sentinels). In the long run it is ulation lives within 50 km of the coast. The GDP generated expected that SWOT will provide altimetry sea level in swath by this population amounts to more than 30 % of the total and hydrological monitoring of big rivers. This will provide EU GDP. The economic value of coastal areas within 500 m a sustainable monitoring base for operational oceanography of the European shores has a total between C 0.5 and 1 tril- in coastal waters. lion per annum (European Commission, http://ec.europa.eu/ Vertical stratification in coastal areas, especially in the environment/iczm/state_coast.htm). river mouths, estuaries, and (semi-)enclosed basins, largely The coastal environment is experiencing its fastest influences the vertical transport of substances as well as changes ever recorded instrumentally – sea-level rise, coastal their transformation in the pycnoclines, redoxcline, and at erosion, increasing water and changing riverine the water–sediment interface. Thus, high-resolution observa- inputs, water mass properties, and mixing features. The most tions through the entire to resolve relevant fea- vulnerable parts of the coastal ocean are the coastal shallow tures and processes in stratified regions have to be applied. waters (CSW) with a depth of a few tens of metres. This zone The challenge here is to achieve the proper resolution both in is subject to most dynamic changes made by winds, waves, time and in space. , sediment transport, riverine inputs, and human activi- ties. They are also the hottest spots in marine spatial plan- Modelling and forecasting ning, maritime safety, protection, disaster prevention, offshore wind energy, climate change adaptation There have been two major issues in focus in the past and mitigation, ICZM (integrated coastal zone management), decade: one is to develop forecasting models and systems the WFD (Water Framework Directive), and the MSFD (Ma- for new operational coastal services, e.g. agitation forecast, rine Strategy Framework Directive), especially on habitat, inundation forecast, estuary/fjord flooding forecast, and dif- eutrophication, and hydrographic condition descriptors. ferent types of drift forecasts; the other is how to bridge and couple the global- and basin-scale forecasting systems 4.1 Operational oceanography in coastal waters with coastal modelling applications and to integrate the frag- 4.1.1 State-of-the-art mented coastal modelling systems at the European scale (She and Buch, 2003). Monitoring For the first issue, the new operational services are mainly developed by national operational agencies. The horizon- Monitoring in the coastal waters has been particularly active tal resolution has been refined to 100−2 m. This part of the in the past decade through both in situ and remote sensing. coastal operational oceanography (OO) is expected to be ex- Comprehensive coastal observatories have been established panded due to the increasing user needs, improved monitor- and maintained in the UK, Germany, and some other coun- ing and forecasting capacities. Private companies have also tries. Integrated monitoring using HF radar, FerryBox, moor- played a major role in coastal services which are mostly case ing buoys, shallow water Argo floats, gliders, integrated sen- by case services. Significantly advanced coastal modelling sors, and satellites have provided huge amounts of obser- systems have been developed and applied in the coastal ser- vations in the coastal waters. An important feature is that vices. Some of these systems have been used for operational many of these data sets have high spatial or temporal res- forecasting. It is expected that some of the commercial ser- olution, which reveals mesoscale and sub-mesoscale fea- vice areas will be transformed into an operational approach, tures in coastal waters and processes of estuary–coast–sea either through cooperation with operational agencies or run interaction. The EC has also strongly supported the coastal the service by themselves. The European research commu- monitoring infrastructure, e.g. through projects JERICO, nity has also contributed significantly to the coastal mod- JERICO-NEXT, and other funding instruments (e.g. Euro- elling systems, by developing a variety of coastal , www.ocean-sci.net/12/953/2016/ Ocean Sci., 12, 953–976, 2016 964 J. She et al.: Developing European operational oceanography for Blue Growth e.g. two-way nesting, unstructured grid, coupled systems and port at the European scale. Support from the EC with large- data assimilation. scale projects is essential to ensure the necessary funding for However, the existing coastal operational modelling, fore- both integration activities and research on new knowledge casting and services are fragmented. The coordination only generation and transformation into operational systems. happens at a limited level, mainly done by ROOSes. A sig- The short- to mid-term objective is to build up operational nificant effort made for integrating existing coastal monitor- monitoring and forecasting systems in the CSW. Engaging ing and forecasting capacities is the EC funded FP6 project existing monitoring into an operational framework, harvest- ECOOP, aiming at consolidating, integrating and further de- ing new knowledge and developing CSW modelling and veloping existing European coastal and regional seas opera- forecasting technology are the three major pillars to reach tional observing and forecasting systems into an integrated the objective. pan-European system targeted at detecting environmental Monitoring and data management research: in addition to and climate changes, predicting their evolution, producing research recommended in Sect. 2, specific R&D activities are timely and quality assured forecasts, and providing marine needed: enhancing monitoring coordination on cross-board information services (including data, information products, and regional scales; expanding existing HF radar observing knowledge and scientific advices). Unfortunately the inte- systems to cover European coastal seas; engaging research grated approach in ECOOP did not continue. In Copernicus and commercial monitoring activities to be part of the op- service, the coastal service has been regarded as a down- erational dataflow; and ensuring delivery of new in situ and stream activity and therefore has not been part of CMEMS. satellite observations for operational usage. Such objectives and tasks should be further addressed, ex- New knowledge generation for improving CSW mod- tended to resolve the estuary–coast–sea interaction and de- els: new knowledge on key dynamic processes, such as veloped into an operational framework through integration hydrodynamic–sediment–optics–biological interactions, 3-D into basin-scale operational systems. Recently the research current–sea level–wave interaction, vertical flux exchange in this area has been identified as a CMEMS research prior- between the atmosphere, water and sea floor, sub-mesoscale ity – seamless interactions between basin and coastal systems phenomena and interaction between sea and river waters, can (CMEMS STAC, 2015). be obtained by using high-resolution in situ and remote sens- However, many key dynamic processes in the CSW have ing data together with modelling tools. The new knowledge not been well resolved by the existing forecasting systems harvesting shall aim at improving coastal ocean models. developed in ECOOP and CMEMS. This includes coupling Modelling and forecasting technology: developing coastal between sediment, optics, physical and ecosystem; verti- ocean models for the CSW to resolve key dynamic cal exchange between atmosphere, water, and the bottom, processes in CSW by transferring new knowledge ob- change, interaction between river and sea wa- tained into models, including hydrodynamic–sediment– ters, small-scale features such as sub-mesoscale eddies, river optics–biological coupling, ocean–wave–ice coupling, im- plumes, etc. Sediment transport and coastal morphology proved description of vertical exchange and sub-mesoscale models have not been included as part of the forecasting sys- parameterization; developing sub-kilometric-resolution estu- tem. ary models; coupling between storm surge, wave and in- Alternatively, the coupled hydrodynamic–wave–sediment undation models; building up operational monitoring and models have been developed and used in commercial appli- forecasting capacity for sediment transport, including oper- cations for many years. Some of them are even made avail- ational data provision, model development and data assim- able for public use. It is expected that the existing knowledge ilation; and data assimilation of high-resolution observation and modelling tools for CSW will be integrated into opera- data: ocean colour, sediment, currents, sea level, etc.; prepa- tional systems through close cooperation between the opera- ration of high-quality input data sets for the CSW forecast- tional oceanography community and the private sector. ing system: high-resolution bathymetry, sea floor sedimenta- tion types and updates of such data sets, and high-resolution 4.1.2 Research priorities in coastal waters weather reanalysis and forecasts at kilometre resolution with riverine inputs. The long-term goal is to develop an operational oceanog- raphy framework which can resolve major marine data and 4.1.3 Coastal prediction information service issues, especially in the CSW. This re- quires upgrading of existing operational coastal ocean fore- Coastal hazards, including hydro-meteorological hazards, casting system with new components (e.g. sediment trans- coastal erosion, pollution, and ecological hazards, are one of port, inundation models, marine optics models) and new dy- the major threats to sustainable development in Blue Growth. namic processes which are currently missing. Risk management in response to the coastal hazards requires Establishment of operational oceanography addressing improved deterministic and probabilistic predictions in the CSW is a significant initiative and big step to lift the role of short term as well as estimation of historical events, statis- operational oceanography in Blue Growth. This needs sup- tics, and future projections.

Ocean Sci., 12, 953–976, 2016 www.ocean-sci.net/12/953/2016/ J. She et al.: Developing European operational oceanography for Blue Growth 965

For coastal erosion and pollution: research shall aim at – a seamless coastal forecasting service: model resolu- gaining understanding of (i) processes governing variabil- tion ranging from hundreds of metres to kilometres; ity in the surface layer (mixed layer turbulence, interactions high-resolution measurements from HF radar, Ferry- with air–sea fluxes) and linking surface waves, currents, and Box, buoys, and gliders assimilated; the model sys- sediment resuspension and pollutant transportation; (ii) pro- tem shall resolve challenging processes and features cesses in the bottom boundary layer including resuspension in coastal waters such as currents–sea level–wave–ice that are important e.g. for the exchange of properties across interaction, inter-basin and inter-sub-basin exchange, shelf breaks and for the behaviour of dense sill overflows strong density gradients in estuaries, and transport of and better water column optics; (iii) the role of riverine in- momentum, heat, and sediment in very shallow wa- puts, advection and sedimentation in coastal sediment bal- ters. Combining modelling and monitoring tools: assim- ance and modelling and predicting coastal sediment balance; ilating; advantages of high-performance computing are and (iv) the impact of coastal erosion due to waves and sea- drawn for high-resolution climate simulations; level rise. The knowledge obtained from the above should be used to improve predictive sediment and pollutant mod- – objective methods of generating indicators for ICZM els. The in situ monitoring of sediment should be enhanced based on seamless flow of data and information prod- with innovative technology. Operational sediment transporta- ucts; tion models should be developed and calibrated, and satel- – value-added operational indicator products for public lite sediment data should be assimilated. The long-term goal stakeholder use; of coastal sediment transport research should aim at an op- erational framework that can support seamless data and in- – transformation from new knowledge into new opera- formation flows for well-balanced and objective decision- tional services such as sediment forecast and coastal making in ICZM. morphology forecast; For coastal hydro-meteorological hazards: understanding, modelling, and prediction of hydro-meteorological hazards – transformation from new knowledge into operational such as flooding, storm surge, and high seas; developing information products in pan-European coastal waters, ensemble and super-ensemble technology for forecasting such as rapid mapping of coastal water mass properties hydro-meteorological extreme events; developing nowcast- (water quality and physical features), dynamic features ing technology by assimilating real-time radar and in situ and such as position of river fronts, distribution of en- satellite data into operational models for search and rescue; ergy, and position of (semi)permanent coastal currents; for civil protection and risk management, coupled weather– and ocean–wave–inundation models in the coastal zone should – Reconstruction, prediction and projection of the chang- be developed and calibrated. ing coastal environment due to climate change and nat- For ecological hazards: understanding, modelling, and ural variability. prediction of ecosystem hazards; an integrated forecasting system should be developed for predicting HAB, , Potential change of human activities in coastal oceans due and loss of habitat. New knowledge and understanding of the to climate change adaptation and mitigation, societal and driving and internal mechanisms and evolution of eco- economic change should be considered and transferred into logical hazards are required. Based on the new knowledge scenarios for European coastal oceans, such as obtained, the operational models can be further optimized so that they are capable of properly simulating the ecological – change in offshore exploitation (wind energy, oil and hazard events. Assimilation technology should be used to de- gas etc, some are due to climate change adaptation), velop the forecast and pre-warning capacity of the ecological – change in shipping activities (some are due to climate hazard. The research in this area needs to be integrated with change such as ice melting), R&D activities in Sect. 5 – Operational ecology. In the long term, an operational approach for the integrated – change in riverine discharge (due to legislation), coastal service focusing on the coastal zone should be devel- oped. Such an approach will, on the one hand, extend exist- – change in land use in the coastal zone, and ing coastal and shelf sea forecasting systems to the coastal – change in fishery (due to climate change and fishery zone with higher resolution, and on the other hand, develop management). new, standardized and integrated service tools and products, which feature The impacts of these scenarios can be projected and as- sessed by using the tools and products developed for the in- tegrated coastal service. – a common framework to bridge CMEMS and national Another long-term goal is to deepen our understanding on coastal services; the sub-mesoscale features in coastal and shelf seas. Due to www.ocean-sci.net/12/953/2016/ Ocean Sci., 12, 953–976, 2016 966 J. She et al.: Developing European operational oceanography for Blue Growth the launch of the SWOT satellite mission after 2020, swath- 4.2.1 Short- to mid-term objectives based altimetry data and hydrological observations will be available. This may lead to enhanced knowledge on the sub- – Reduction of systematic errors in the reprocessing, mesoscale features in the coastal waters. Advection and mix- modelling and assimilation components for the produc- ing associated with mesoscale and sub-mesoscale oceanic tion of long-term historical data, improved methods to features such as river fronts, meanders, eddies and filaments account for representability and sampling observation are of fundamental importance for the exchanges of heat, errors. fresh water and biogeochemical tracers between the surface – Advancement of operational coastal ocean-ice models and the ocean interior, but also exchanges between the open for climate modelling: benchmark equilibrium test of oceans and shelf seas. operational models to ensure their long-term stability The challenges associated with mesoscale and sub- using “free runs”; to reduce uncertainties in climate mesoscale variability (between 1 and 20 km) in the coastal downscaling by optimizing downscaling model dynam- oceans imply therefore high-resolution observations (both ics and set-up; development of reliable techniques to in situ and satellite) and multi-sensor approaches. Accord- forecast regional/local sea-level rise, including the land- ingly, as suggested in the CMEMS Service evolution strat- rising term in the ocean climate models; enhance the egy (CMEMS STAC, 2015), multi-platform synoptic exper- ocean climate model performance on modelling storm iments have to be designed in areas characterized by in- surge events; resolving the “skin effect” for more accu- tense density gradients and strong mesoscale activity to mon- rate SST modelling. itor and establish the vertical exchanges associated with mesoscale and sub-mesoscale structures and their contribu- – Improved understanding of coastal sea-level forcing tion to upper-ocean interior exchanges. mechanisms and coupling with the regional variability in climate models; research on relative sea-level trends in relation to future storm tracks and changing storm 4.2 Climate change impacts on the coastal environment surges; developing and undertaking a detailed assess- ment of the extent of coastal erosion in the EU at ap- propriate temporal and spatial scales; identification of Climate change poses one of the main challenges faced by climate variability on stratification and its relation to cli- society in the coming decades, especially to fragile coastal mate change of other ocean properties. environment. Its impact in many cases is amplified by anthro- pogenic activities in coastal regions. Operational oceanog- 4.2.2 Longer-term objectives raphy community in Europe also provides marine climate service to the society and Blue Growth through further ex- – Developing a probabilistic framework and metrics for tending its operational monitoring and modelling capacities ocean reanalysis using ensemble and super-ensemble to climate scale. Considering recent trend in seamless earth techniques, including inter-comparison, verification, system modelling and prediction, weather, ocean and climate and defining and generating probabilistic tailored prod- research will become more and more integrated. In this sec- ucts for users; and developing methods to ensure qual- tion we address research on the coastal ocean climate change ity, homogeneity and robust uncertainty measures in the adaptation and mitigation related to operational oceanogra- long-term time series reconstructed from data or model phy. reanalysis. Major research objectives of coastal operational oceanog- raphy on climate scales are (i) to provide long-term his- – New methods and diagnostics to evaluate the climate torical data, including both observations through integrat- change predictability of the ocean circulation, biogeo- ing and reprocessing and model reanalysis by assimilating chemistry and marine ecosystems at basin scale and observations into operational models; (ii) to develop oper- coastal scale to provide a theoretical basis for the long- ational ocean-ice models for climate modelling and projec- term prediction. tions; (iii) to identify major climate change signals in the past – Methodologies to project information about the present and future coastal environment ranging from seasonal to cen- ocean state and variability into the future, based on a tennial scales and (iv) to assess the impact of climate change combination of reanalysis and Earth system models. and adaptation and mitigation measure on operational sce- narios. In addition to improving the climate service quality at national level, these activities will also contribute to the 5 Operational ecology consolidation of Ocean State reports delivered by CMEMS, and to the development of the Copernicus Climate Change Timely and regular assessment of the status of the marine Service (C3S). The following research activities have been environment and its ecosystems is essential for ecosystem- identified. based management in the implementation of EU regulations

Ocean Sci., 12, 953–976, 2016 www.ocean-sci.net/12/953/2016/ J. She et al.: Developing European operational oceanography for Blue Growth 967 such as the MSFD, the Water Framework Directive (WFD), the Common Fishery Policy (CFP), and regional conven- tions. Operational ecology (OE) is the systematic and oper- ational provision of quality-assured data and information on the status of marine ecosystems (environment, low trophic and high trophic levels) to stakeholders by integrating re- search, operations, and services (the relationship of OE re- search to the operational service is shown in the flowchart in Fig. 2). OE data products are generated from combina- tions of remote sensing and in situ measurements and ma- rine ecosystem models with data assimilation for past (re- processed long-term observation time series and reanaly- sis), current and recent (analysis and updated rolling reanal- ysis), and future (short-term/seasonal/decadal forecast and scenario projections). OE information products are value- added and derived from the OE data products, for exam- ple GES (Good Environmental Status) criteria and indica- tors (as defined in the MSFD Common Implementation Strat- Figure 2. Flowchart of the operational ecology. egy) and seasonal/annual marine ecosystem status reports, derived from the OE data products. OE products will make ecosystem-based management more reliable, operational, ef- ficient, and timely by providing the ability to predict the “health” of European marine ecosys- – more frequent updates of environment and ecosystem tems. OPEC developed prototype ecological marine forecast state, systems for European seas (north-eastern Atlantic, Baltic, Mediterranean and Black seas), which include hydrodynam- – more reliable and efficient assessments based on an in- ics, lower and higher trophic levels (plankton to fish), and tegrated model-EO approach, biological data assimilation, and made demonstration reanal- – new capabilities for ecosystem forecast at seasonal to ysis simulations, assessed the effectiveness of the current op- decadal scales, erational ecosystem monitoring systems, and demonstrated the potential to make robust seasonal ecosystem forecasts. – flexible operational tools for scenario-based ecosys- In addition, the OPEC project has developed an open-source tem management through end-to-end modelling (lower web GIS data portal and a model benchmarking tool which trophic level, e.g. plankton, to higher trophic level, e.g. allow users to visualize, plot, download, and validate large fish and mammals; Rose et al., 2010), spatial–temporal data sets. Figure 3 shows an example of dy- namic viewing of reanalysis and rapid environmental assess- – provision of an operational higher trophic level service ment for a user-selected region (marked as a square). for fishery management, Simultaneously, the FP7 OSS2015 project has developed R&D activities with the objective of deriving representations – more reliable forecasts of biohazards such as harmful of biogeochemical variables from the integration of gliders and hypoxia, and and floats with EO satellite data into cutting-edge numeri- cal biogeochemical and bio-optical models. There is an ex- – more reliable projections of long-term trend, fluctua- pectation that the integrated Atlantic Ocean Observing Sys- tion, and regime shift of marine ecosystems. tem (developed through AtlantOS) will increase the number and quality of in situ observations on chemistry, biology, and 5.1 Enhanced monitoring and forecast capacities for ecology over the next decade. A co-evolution of the data use marine ecosystems in assessment and predictive models holds great potential for new products and users. Recent scientific developments and breakthroughs have pro- It is expected that results from these projects as well as vided a preliminary knowledge base and associated data de- similar advances in the field will be transferred to opera- livery, models, and analysis tools to begin to address the tional services such as CMEMS. The relevant short- to long- above issues. For example, EU FP7 project OPEC (Opera- term research objectives in this area have been identified in tional Ecology) has developed and evaluated ecosystem mon- the MSFD session in the CMEMS Service Evolution and itoring tools to help assess and manage the risks posed by User Uptaking Workshop (Brussels, 2015). They are further human activities to the marine environment, thus improving evolved in the following sections. www.ocean-sci.net/12/953/2016/ Ocean Sci., 12, 953–976, 2016 968 J. She et al.: Developing European operational oceanography for Blue Growth

Figure 3. OPEC Rapid Environment Assessment and multi-decadal biogeochemical reanalysis: an example of Baltic Sea Chl a. Upper panel: OPEC data portal for extracting OE products; lower panel: monthly mean Chl a time series during January 1990–May 2014 at a selected rectangular polygon shown in the upper panel. The shadow area shows the monthly standard deviation.

5.1.1 Short- to mid-term objectives of existing operational ecological models regarding to needs of ecosystem-based management in national and – Data: increasing the amount of biogeochemical data regional levels (e.g. MSFD). which can be used for validation and assimilation, through enhanced data sharing, shortening the delivery time and making new observations via innovative in- – Model optimization: improving existing operational struments e.g. Bio-Argo; extension of existing monitor- ecological models regarding the weaknesses identi- ing capabilities from primary production to plankton. fied by transferring state-of-the-art biological knowl- edge into model terms; developing new modules link- – Quality assurance: developing a standardized val- ing optical properties in the near-surface ocean to idation method/system for ecosystem model prod- biomass; improved representation of key processes such ucts/variables (particularly related to non-assimilated as primary production, nutrient uptake, and grazing observations/variables); to identify major weaknesses in models resolving the diurnal variability; demonstra-

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tion of consistent interfacing (nesting, downscaling) from seasonal to decadal. Therefore it is essential to under- between open ocean biogeochemical models and re- stand marine ecosystem change on climate scales in order gional/coastal ecosystem models and downstream ap- to make good prognostic models. Climate change and direct plications. anthropogenic activities are two major classes of changing the state of the marine ecosystem. The research in – Forecast technology: development of probabilistic this area has been carried out in EU project MEECE. Recent (ensemble-based) ecosystem modelling approaches in- progress has been reviewed by Barange et al. (2014). For the cluding uncertainty estimation capabilities. European seas, the climate change impacts on marine ecosys- – Multi-data assimilation capabilities (combining state tems were reviewed by EU FP6 project CLAMER (ESF Ma- and parameter estimation): combining ocean colour and rine Board, 2011). Future research priorities have also been sub-surface data from relevant ecological observations, identified. However, for the OE, what we are interested in is especially in regional seas; simultaneous assimilation of the research that can directly improve the predictive capabil- physical and biological properties. ity on marine ecosystems. – Tailored provision of operational products in addition to – Impacts of long-term change of water temperature, standard (water temperature, , ice, waves, mixing salinity, mixing features, , coastal circulation, features, residence time, Chl a, oxygen, pH, nutrients, riverine inputs, ice conditions, inter-basin exchange and light, plankton biomass) in support of predictive habitat their impacts on basin and coastal ecosystems; inves- forecasts, for ecological status and fisheries modelling tigate potential relations between climate change pres- and risk assessment (e.g. invasive species, HABs). sures and ecosystem long-term change such as regime shift. – Rapid environmental and ecosystem assessment: devel- oping an efficient data framework, assimilation and as- – Investigate whether an increasing atmospheric supply sessment tools to provide a rapid mapping of seasonal or of nutrients could potentially offset the reduced oceanic annual marine environment and ecosystem states. The vertical supply. marine environment and ecosystem states are assessed by a set of GES (Good Environmental Status) indica- – Couple regional climate change scenarios with river tors derived from the rolling analysis. Since the GES basin, nutrient transfer and coastal ecosystem models, indicators are used in MSFD assessment, the assess- to test the interacting effects of global climate change ment means an “operational approach” for the sustain- with scenarios of regional socio-economic change; bet- able management of ecosystem resources, which pro- ter understanding of the possible responses of coastal vides solid basis for the future MSFD assessment. ecosystems to changing riverine nutrient loads, flooding and warming. 5.1.2 Longer-term objectives – Improving the understanding and prediction of ocean – Monitoring: a more homogenous biogeochemical mon- acidification by combining in situ and satellite obser- itoring network in Europe; improved methodologies for vations. supplying operational information on sources of nutri- – Impacts of sea-level rise and land vertical movement on ents and pollution/chemicals to the oceans (e.g. CDOM, change of shorelines, loss of habitat, and coastal ecosys- underwater noise, and plastic/paraffin). tems. – Modelling: improved description of benthic–pelagic – Understanding predictability of the biogeochemistry coupling on short-term (seasonal) and long-term and marine ecosystems at basin scale or regional scale: (decadal) scales; identification of good initial condi- identifying major forcing-dependent predictability sig- tions; improving representation of biological cycles in nals in marine ecosystems; improved understanding of sea ice, including optical properties of sea ice and verti- impacts of long-term change in inter-basin, inter-sub- cal migration of nutrients in sea ice. basin, and riverine inputs on basin and coastal ecosys- – New capabilities for ecosystem projections at seasonal tems. (to decadal) scales. 5.3 Operational Ecology European Experiment – 5.2 Climate variability and marine ecosystems OEEE

While seasonal variability is the most prominent mode in Operational ecology is a new and emerging research area. the natural variability of marine ecosystems, these seasonal For the moment, provision of a quality-assured ecological cycles are also modulated by longer-term climate signals. service on seasonal forecasting, annual assessment, decadal Ecosystem-based management also normally has timescales reanalysis, and scenario projections of marine ecosystems on www.ocean-sci.net/12/953/2016/ Ocean Sci., 12, 953–976, 2016 970 J. She et al.: Developing European operational oceanography for Blue Growth an operational basis is non-existent. Major knowledge gaps In order to build up a quality-assured European capacity exist in to deliver the OE service, the Operational Ecology European Experiment – OEEE – is required. This would serve as part of – processes in understanding and modelling biogeochem- the mid- to long-term research element of European OE. The ical cycle in the regional seas, interaction between low goal of the OEEE is to integrate as many existing observa- trophic level and high trophic level and benthic ecosys- tions and advanced modelling technologies as possible to de- tems, velop and demonstrate OE showcases in European regional – data assimilation techniques for biogeochemical param- seas. This can be reached through six research activities: eters that focus on improving long-term forecasts and – to establish a comprehensive database by integrating ex- statistics, isting European marine monitoring components (as de- scribed in Sect. 2) for testbed studies; – forecasting technology on seasonal scales and longer timescales, – to develop new knowledge and related new/improved parameterizations on key biogeochemical processes in – more accurate modelling and estimation of river nutrient the models, new field experiments should be designed loading, spreading and fate in the sea, to collect necessary observations for the dedicated OE – high trophic level modelling and forecasting technol- research; ogy, and – to make breakthroughs in advancing ocean-ice- – end-to-end modelling for operational scenario projec- ecosystem full-scale models by transferring the new tions. knowledge obtained to model processes;

The gaps in the knowledge base, monitoring networks, and – to understand the ecosystem model behaviour in a prob- product quality are inter-dependent. Among them, the avail- abilistic framework, aiming at generating unbiased en- ability of the observations is the basis for advancing the pro- sembles (regarding ecosystem reality) for the dedicated cess understanding, filling the knowledge gaps and quanti- model system; fying and improving the product quality. On the one hand, – to improve the quality of the forcing data from atmo- operational monitoring systems provide information on the sphere deposits, riverine inputs, and physical ocean, as state of the system, which allows us to assess model perfor- well as better description and parameterization of the mance in predicting the state of the system and hence im- forcing terms; and prove skill through data assimilation and parameter tweak- ing. On the other hand, filling knowledge gaps requires ded- – to generate OE products to assimilate as much as icated process studies, which can be used to develop miss- possible observations into the improved model sys- ing terms and parameterize the processes in the models. This tem in an ensemble framework. The products will is arguably pre-cursor R&D that underpins the more applied cover different temporal scales. For historical reanal- R&D required for OE. In OPEC, it was found that significant ysis and rapid ecosystem mapping, the physical– monitoring gaps exist in the Mediterranean and the Black biogeochemical–ecosystem model (both lower and high Sea biogeochemical monitoring networks, while relatively trophic level) will be used; for the future outlook smaller gaps (in terms of effective spatial coverage) are en- and scenario projections, end-to-end models will be countered in the Baltic and North seas. However, the data used as necessary through coupling with the physical– availability is still not fit for the purpose of providing oper- biogeochemical–ecosystem models. The products will ational seasonal forecast and rapid environment assessment serve ecosystem-based management at the European on an annual basis. scale to serve dedicated stakeholders such as EEA, Without timely and sufficient observations, the OE prod- ICES, regional conventions, and member state envi- uct quality cannot be verified at basin scales, not to men- ronmental agencies for the implementation of WFD, tion further optimization of the modelling systems which MSFD, and CFP. needs observations for calibration and process studies. On the The research priorities in OEEE are as follows: other hand, rational sampling schemes (sampling frequency and locations) are essential for making better forecasts. It – development of modelling and forecasting techniques was found that optimal re-location of the existing North Sea for GES assessment and operational fishery manage- buoys can increase the explained North Sea temperature vari- ment: ability by a factor of 2 (She et al., ODON final report). In OPEC, it was found that changing sampling frequency from (a) developing fully coupled atmosphere–ocean–ice– weekly to daily of a FerryBox line in the Aegean Sea can biogeochemical IBM (individual-based model) – increase the explained Chl a variability from 35 to 96.5 %. food web models for ecosystem outlook at seasonal

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to decadal scales in a probabilistic framework, op- ational Ecology: development of operational ecology to re- timizing the computational performance and reso- solve entire marine ecosystems from the physical ocean to lution to resolve all important pressures and pro- high trophic level food webs at relevant scales. The first two cesses; areas, “European ocean observations” and “Modelling and (b) improving understanding of nutrient cycles and key Forecasting Technology”, are the basic instruments for Eu- parameterizations in forecast models; ropean operational oceanography. The last two, “Coastal Op- erational Oceanography” and “Operational Ecology”, aim at (c) improving understanding of ecosystem predictabil- developing corresponding operational approaches. ity from synoptic to seasonal scales; For European ocean observation research, further ad- (d) improving data assimilation for operational fore- vancement of the existing operational observation infrastruc- casts of marine ecological hazards and seasonal to ture remains the primary focus, especially on biogeochemi- decadal outlooks; cal variable, extreme events, and sub-mesoscale features. On- going use and new development of observation capacities, (e) further development of flexible end-to-end mod- such as Sentinels, FCI, Cryosat2, SWOT, ITP, and Bio-Argo, els/tools for scenario-based services; improving will make it possible to generate new and/or better scien- coupling between end-to-end models and opera- tific understanding, operational applications, products, and tional models; services. – improving the understanding of impacts of atmospheric For Modelling and Forecasting Technology, recent efforts deposit, riverine inputs, discharges from vessels and in advancing the ocean system models for next generation bottom resuspension on the ecosystem states; better de- super-computing architectures, coupled modelling, innova- scription of the forcing terms and improved forcing data tive data assimilation approaches, and probabilistic fore- quality for ecological models; casting will provide essential elements for building up the UOMs. The operational ocean system models will be cali- – integrating existing marine observation components (as brated to meet the energy and mass conservation conditions mentioned in Sect. 2) for operational ecology through so that they can be used for climate predictions and projec- data assimilation, model calibration, and validation; tions. Operational oceanography is a major developer and – designing and recommending new monitoring activities provider of marine services for supporting Blue Growth, and in order to reduce major uncertainties in operational also an important instrument to integrate and sustain Euro- ecology products; and pean marine science. By integrating and standardizing the – providing a pre-operational demonstration (multi- fragmented knowledge, monitoring, and modelling activities model ensemble approach) of rapid environmental as- into an operational framework with a common value chain, sessment with comprehensive data assimilation and sea- the operational approach will provide a sustained develop- sonal to decadal forecasting/projections for ecosystem ment and service platform and significantly improve the ef- components with high predictability and fisheries ser- ficiency, quality, and delivery time of the current services. vice. Two new areas are identified for developing operational ap- proaches for the implementation of integrated coastal zone management and ecosystem-based management, based on 6 Summary and discussion the scientific state-of-the-art and user needs. Three specific pillars are used when developing the operational framework In this paper, major research challenges in European op- for a relative new area: integration of existing capacities erational oceanography are identified for the four knowl- into an operational framework, identification and filling key edge areas as (i) European ocean observations: improving knowledge gaps, and transferring the new knowledge into op- the cost-effectiveness of the marine observation systems; in- erational instruments. Furthermore, it is essential for the op- tegration of European marine observations, developing in- erational oceanography community to work together with the novative monitoring technology and optimal design of sam- private sector, stakeholders, and the non-operational research pling schemes and harmonized use of the observational in- community when developing the operational frameworks in frastructure; (ii) Modelling and Forecasting Technology: de- the targeted areas. velopment of Unified Ocean system Models, data assimila- For coastal operational oceanography, new knowledge is tion, and forecasting technology for seamless modelling and needed to understand the interactions between the atmo- prediction; (iii) Coastal Operational Oceanography: devel- sphere, ocean, wave, ice, sediment, optics and ecosystem, opment of operational coastal oceanography to resolve sub- and between river, land and coastal waters, as well as be- mesoscale features and shallow coastal waters; integrating tween sub-mesoscales and other scales. By integrating the science, observations, and models for new knowledge gen- new knowledge, new observations, and coastal marine sys- eration and operational system development; and (iv) Oper- tem models into an operational framework, an operational www.ocean-sci.net/12/953/2016/ Ocean Sci., 12, 953–976, 2016 972 J. She et al.: Developing European operational oceanography for Blue Growth modelling and forecasting capacity will be established for the It should be mentioned that the knowledge areas and re- shallow coastal waters. search priorities identified are not exhaustive. Some impor- For the development of an operational approach for marine tant scientific areas, such as monitoring and forecasting at ecology, new knowledge is needed in understanding ecosys- global-scale and ice-infested waters and satellite operational tem functions such as nutrient cycle, benthic–pelagic interac- oceanography, are not addressed sufficiently in this paper. tion, lower–high trophic coupling, the response of the marine These issues can be found in scientific strategy documents ecosystem to external pressures caused by climate change in programmes contributing to the operational oceanography and human activities, and the transport of chemicals and pol- development such as CMEMS, YOPP, and PEEX (Pan Euro- lutants exported from the atmosphere, rivers, and vessels. Asia Experiment), and review papers, e.g. by Le Traon et European research on operational oceanography will be al. (2015). sustained by national activities for improving the national It is anticipated that more and more service areas for marine products and services, regional networking activities the Blue Growth, climate change adaptation and ecosystem- such as ROOSes, regional-EU joint research activities such based management will adopt an operational approach which as BONUS-163 (the joint Baltic Sea research and develop- shares a similar operational service value chain. In many ment programme), European programme Horizon 2020, es- cases integration of marine and sectorial information prod- pecially themes “Bio-economy, marine and maritime” and ucts is needed for such an approach, which requires that “Climate, environment and sustainable development”, and operational oceanography community to work together with CMEMS. the sectorial marine service providers, facilitators, stakehold- The research and development in EuroGOOS is coher- ers and end users. The European operational oceanography ent with the vision of IOC (Intergovernmental Oceano- community will be dedicated to identify, develop and cul- graphic Commission): “Strong scientific understanding and tivate the operational approaches for marine services in the systematic observations of the changing world ocean cli- corresponding socio-economic areas through address new re- mate and ecosystems shall underpin sustainable development search challenges in the emerging service areas. and global governance for a healthy ocean, and global, re- gional and national management of risks and opportunities from the ocean” (IOC, 2014). It significantly contributes to the four IOC high-level objectives in the IOC Medium-Term Strategy 2014–2021 document, i.e. (i) healthy ocean ecosys- tems and sustained ecosystem services; (ii) effective early warning systems and preparedness for ocean-related haz- ards; (iii) increased resilience to climate change and vari- ability and enhanced safety, efficiency, and effectiveness of all ocean-based activities through scientifically founded services, adaptation, and mitigation strategies; and (iv) en- hanced knowledge of emerging ocean science issues. Furthermore, European operational oceanography re- search will actively contribute to the relevant international or- ganizations and programmes such as WMO, JCOMM, GEO, GOOS, GCOS, GODAE-Oceanview, and YOPP. Their sci- entific strategies and implementation plans provide multiple focus issues and also references for European operational oceanography research and services. Due to the limits of space, the detailed relation between European operational oceanography research and the international programmes is not analysed in this paper.

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Appendix A

List of acronyms 3-D/4-DVAR Three-/four-dimensional VARiational method ADCP Acoustic Doppler current profiler AtlantOS Optimizing and Enhancing the Integrated Atlantic Ocean Observing System BFM Biogeochemical Flux Model BG Blue Growth BONUS The joint Baltic Sea research and development programme C3S Copernicus Climate Change Service CDOM Coloured dissolved organic matter CFP Common Fishery Policy CLAMER Climate change and European Marine Ecosystem Research project CMEMS Copernicus Marine Service COSYNA Coastal Observing System for Northern and Arctic Seas project CPU Central processing unit CSW Coastal shallow waters DG-MARE The Directorate-General for Maritime Affairs and Fisheries EDIOS European Directory of the Ocean-Observing System project ECMWF European Centre Medium-range Weather Forecast ECO3M Mechanistic Modular Ecological Model ECOOP European COastal-shelf sea OPerational observing and forecasting system project ECOSMO ECOSystem MOdel EEA European Environment Agency EGO Everyone’s Glider Observatories EMODnet European Marine Observation and Data Network EnKF Ensemble Kalman filter EnVAR Ensemble-variational method EO Earth Observation EOOS Sustained European Ocean Observing System ERIC European Research Infrastructure Consortium ERGOM Ecological ReGional Ocean Model ERSEM European Regional Seas Ecosystem Model ESF European Science Foundation EU European Union EuroGOOS European Global Ocean Observing System FCI Flexible Combined Imager FixO3 Fixed point Open Ocean Observatory network project FP EC Framework Program GCOS Global Climate Observing System GDP Gross Domestic Production GEO Group of Earth Observations GES Good Environmental Status GIS Geographic Information System GMES Global Monitoring for Environment and Security GODAE Global Ocean Data Assimilation Experiment HAB Harmful algae bloom HBM HIROMB-BOOS model HELCOM The Baltic Marine Environment Protection Commission HF High frequency HPC High-performance computing HYCOM HYbrid Coordinate Ocean Model

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List of acronyms IBM Individual-based model ICES International Council for the Exploration of the Sea ICZM Integrated coastal zone management IOC Intergovernmental Oceanographic Commission ISO International Organization for Standardization ITP Ice-Tethered Profiler JCOMM Joint Technical Commission for Oceanography and Marine Meteorology JERICO Joint European Research Infrastructure network for COastal observatories JPI-Oceans The Joint Programming Initiative Healthy and Productive Seas and Oceans MFC Monitoring and Forecasting Centres MITGCM MIT General Circulation Model MONALISA2 Securing the Chain by Intelligence at Sea project MSFD Marine Strategy Framework Directive NCAR National Center for Atmospheric Research NEMO Nucleus for European Modelling of the Ocean NORWECOM NORWegian ECOlogical Model system ODON Optimal Design of Observational Networks project OE Operational ecology OEEE Operational Ecology European Experiment OOPS Object Oriented Programming System project OPEC Operational Ecology project OSE Observing System Experiment OSS2015 Ocean Strategic Services beyond 2015 project OSSE Observing System Simulation Experiment OSPARCOM Convention for the Protection of the Marine Environment of the North-East Atlantic PDAF Parallel Data Assimilation Framework PSyKAl Parallel System, Kernel and Algorithm RASM Regional Arctic System Model ROMS Regional Ocean Modeling System ROOS Regional Operational Oceanography System R&D Research and Development SANGOMA Stochastic Assimilation for the Next Generation Ocean Model project SeaDataNet Pan-European infrastructure for ocean and marine data management project SEEK Singular evolutive extended Kalman filter SIMD Single instruction multiple data SMOS Soil moisture ocean salinity SST SSS Sea surface salinity SWOT Surface Water & Ocean Topography TB Tera Byte T /S Temperature/salinity UAM Unified Atmospheric Model UEM Unified Earth system Model UM Unified Model UOM Unified Ocean system Model YOPP Year of Polar Prediction WFD Water Framework Directive WMO World Meteorological Organisation

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