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The forum for air quality modelling in Eurupe (FAIRMODE): Results and activities 2011-2012.

Denby, B.R.; Tarrasón, L.; Galmarini, S.; Belis, C.; Thunis, P.; Lükewille, A.; Douros, J.; Borge, R.; Lumbreras, J.

2012

The Finokalia Aerosol Measurement Experiment - 2008 (FAME-08): an overview.

Pikridas, M.; Bougiatioti, A.; Hildebrandt, L.; Engelhart, G.J.; Kostenidou, E.; Mohr, C.; Prévôt, A.S.H.; Kouvarakis, G.; Zarmpas, P.; Burkhart, J.F.; Lee, B.-H.; Psichoudaki, M.; Mihalopoulos, N.; Pilinis, C.; Stohl, A.; Baltensperger, U.; Kulmala, M.; Pandis, S.N.

2010

The fingerprint of the summer 2018 drought in Europe on ground-based atmospheric CO2 measurements

Ramonet, Michel; Ciais, Philippe; Apadula, F.; Bartyzel, Jakub; Bastos, Ana; Bergamaschi, Peter; Blanc, P. E.; Brunner, D; Caracciolo di Torchiarolo, L.; Calzolari, F.; Chen, H.; Chmura, L.; Colomb, A.; Conil, S.; Cristofanelli, P.; Cuevas, E.; Curcoll, R.; Delmotte, M.; di Sarra, A.; Emmenegger, L.; Forster, G.; Frumau, A.; Gerbig, C.; Gheusi, F; Hammer, S.; Haszpra, L.; Hatakka, J.; Hazan, L.; Heliasz, M.; Henne, S.; Hensen, A.; Hermansen, Ove; Keronen, P.; Kivi, R.; Kominkova, K.; Kubistin, D.; Laurent, O.; Laurila, T; Lavric, J. V.; Lehner, I.; Lehtinen, K. E. J.; Leskinen, A.; Leuenberger, M.; Levin, I.; Lindauer, M.; Lopez, M.; Myhre, Cathrine Lund; Mammarella, I; Manca, G; Manning, A; Marek, M. V.; Marklund, P.; Martin, D.; Meinhardt, F; Mihalopoulos, N.; Mölder, M.; Morguí, J.A.; Necki, J.; O'Doherty, S.; O'Dowd, C; Ottosson, M.; Philippon, N.; Piacentino, S.; Pichon, J.M.; Plass-Duelmer, C.; Resovsky, A.; Rivier, L; Rodo, X; Sha, M. K.; Scheeren, H. A.; Sferlazzo, D.; Spain, T. G.; Stanley, K. M.; Steinbacher, M.; Trisolino, P.; Vermeulen, A.; Vitkova, G.; Weyrauch, D.; Xueref-Remy, I.; Yala, K.; Kwok, C. Yvwer

During the summer of 2018, a widespread drought developed over Northern and Central Europe. The increase in temperature and the reduction of soil moisture have influenced carbon dioxide (CO2) exchange between the atmosphere and terrestrial ecosystems in various ways, such as a reduction of photosynthesis, changes in ecosystem respiration, or allowing more frequent fires. In this study, we characterize the resulting perturbation of the atmospheric CO2 seasonal cycles. 2018 has a good coverage of European regions affected by drought, allowing the investigation of how ecosystem flux anomalies impacted spatial CO2 gradients between stations. This density of stations is unprecedented compared to previous drought events in 2003 and 2015, particularly thanks to the deployment of the Integrated Carbon Observation System (ICOS) network of atmospheric greenhouse gas monitoring stations in recent years. Seasonal CO2 cycles from 48 European stations were available for 2017 and 2018. Earlier data were retrieved for comparison from international databases or national networks. Here, we show that the usual summer minimum in CO2 due to the surface carbon uptake was reduced by 1.4 ppm in 2018 for the 10 stations located in the area most affected by the temperature anomaly, mostly in Northern Europe. Notwithstanding, the CO2 transition phases before and after July were slower in 2018 compared to 2017, suggesting an extension of the growing season, with either continued CO2 uptake by photosynthesis and/or a reduction in respiration driven by the depletion of substrate for respiration inherited from the previous months due to the drought. For stations with sufficiently long time series, the CO2 anomaly observed in 2018 was compared to previous European droughts in 2003 and 2015. Considering the areas most affected by the temperature anomalies, we found a higher CO2 anomaly in 2003 (+3 ppm averaged over 4 sites), and a smaller anomaly in 2015 (+1 ppm averaged over 11 sites) compared to 2018.

This article is part of the theme issue ‘Impacts of the 2018 severe drought and heatwave in Europe: from site to continental scale'.

2020

The FAIRness of ACTRIS Data Centre

Myhre, Cathrine Lund; Fiebig, Markus; Rud, Richard Olav; Mona, Lucia; Dema, Claudio; Pascal, Nicolas; Henry, Patrice; Picquet-Varrault, Bénédicte; Brissebrat, Guillaume; Boonne, Cathy; O'Connor, Ewan; Tukiainen, Simo

The purpose of this report is to document the status and implementation of FAIRness within ACTRIS Data centre as of March 2023, developed over the period January 2019 – March 2023.

The report is an extended version of ENVRI-FAIR deliverable D8.4 due March 2023 and available through Zenodo: ENVRI-FAIR D8.4: The FAIRness of ACTRIS | Zenodo, only including the work until autumn 2022. This present report adds more information to the implementation of the FAIR principles by ACTRIS Data Centre over the period January 2019 – March 2023. In addition to D8.4, the present report provides a comprehensive external FAIRness assessment covering the entire period 2019 - 2023, along with an evaluation of the implementation in the years 2022 and the first half of 2023. It's important to note that the project deliverable only encompasses the period from 2019 to 2021.

NILU

2024

The FAIR principles as a key enabler to operationalize safe and sustainable by design approaches

Karakoltzidis, Achilleas; Battistelli, Chiara Laura; Bossa, Cecilia; Bouman, Evert; Garmendia Aguirre, Irantzu; Iavicoli, Ivo; Jeddi, Maryam Zare; Karakitsios, Spyros; Leso, Veruscka; Løfstedt, Magnus; Magagna, Barbara; Sarigiannis, Denis; Schultes, Erik; Soeteman-Hernández, Lya G.; Subramanian, Vrishali; Nymark, Penny

Safe and sustainable development of chemicals, (advanced) materials, and products is at the heart of achieving a healthy future environment in line with the European Green Deal and the Chemicals Strategy for Sustainability. Recently, the Joint Research Center (JRC) of the European Commission (EC) developed the safe and sustainable by design (SSbD) framework for definition of criteria and evaluation procedure proposed to be established in Research and Innovation (R&I) activities. The framework aims to support the design of chemicals, materials and products that provide desirable functions (or services), while simultaneously minimizing the risk for harmful impacts to human health and the environment. While many industrial sectors already consider such aspects during R&I, the framework aims to harmonize safety and sustainability assessment across diverse sectors and innovation strategies to meet the mentioned overarching policy goals. A cornerstone to successfully implement and operationalize the SSbD framework lies in the availability of high-quality data and tools, and their interoperability, aspects which also play a key role in ensuring transparency and thereby trust in the assessment outcomes. Availability of data and tools depend on their machine-actionability in terms of findability, accessibility, interoperability, and reusability, in line with the FAIR principles. The principles were developed in order to harmonize digitalization across all data domains, supporting unanticipated data-driven “seamless” integration of information and generation of new knowledge. Here we discuss the essentiality of FAIR data and tools to operationalize SSbD providing views and examples of activities within the European Partnership for the Assessment of Risks from Chemicals (PARC). The discussion covers five areas previously brought up in relation to the SSbD framework, and which are highly dependent on implementation of the FAIR principles; (i) digitalization to leverage innovation towards a green transition; (ii) existing data sources and their interoperability; (iii) navigating SSbD with data from new scientific developments (iv) transparency and trust through automated assessment of data quality and uncertainty; and (v) “seamless” integration of SSbD tools.

Royal Society of Chemistry (RSC)

2024

The European hot spot of B[a]P and PM2.5 exposure - The Ostrava region, Czech Republic: Health research results.

Sram, R.J.; Dostal, M.; Libalova, H.; Rossner Jr.; P.; Rossnerova, A.; Svecova, V.; Topinka, J.; Bartonova, A.

2013

The European Fifth Framework Project GOA.

Kelder, H.; Eskes, H.; Boersma, F.; Isaksen, I.; Gauss, M.; Zerefos, C.S.; Balis, D.; Platt, U.; Wenig, M.; Beirle, S.; Wagner, T.; Hansen, G.; Vik, A.F.; Zehner, C.

2002

The European Database for Ultraviolet Climatology and Evaluation (EDUCE).

Seckmeyer, G.; Edvardsen, K.; Engelsen, O.; Kylling, A. et al.

2002

The European contribution to global coastal zone research: An ELOISE (European Land-Ocean Interaction Studies) project. Estuarine, Coastal and Shelf Science. Special issue. Vol. 62, no. 3

Pacyna, J.M.; Barrett, K.; Namiesnik, J. (eds.)

2005

Bok

The EUROCOM project: A collaborative reanalysis of European CO2 fluxes over the period 2006-2015

Monteil, Guillaume; Lang, Matthew; Broquet, Grégoire; Scholze, Marko; Karstens, Ute; Peylin, Philippe; Thompson, Rona Louise; Gerbig, Christoph; Koch, Thomas; van der Laan-Luijkx, Ingrid Theodora; Smith, Naomi; White, Emily; Meesters, Anton; Tarniewicz, Jerome; Rivier, Leonard

2018

The Eulerian urban dispersion model EPISODE – Part 2: Extensions to the source dispersion and photochemistry for EPISODE–CityChem v1.2 and its application to the city of Hamburg

Karl, Matthias; Walker, Sam-Erik; Solberg, Sverre; Ramacher, Martin O. P.

This paper describes the CityChem extension of the Eulerian urban dispersion model EPISODE. The development of the CityChem extension was driven by the need to apply the model in largely populated urban areas with highly complex pollution sources of particulate matter and various gaseous pollutants. The CityChem extension offers a more advanced treatment of the photochemistry in urban areas and entails specific developments within the sub-grid components for a more accurate representation of dispersion in proximity to urban emission sources. Photochemistry on the Eulerian grid is computed using a numerical chemistry solver. Photochemistry in the sub-grid components is solved with a compact reaction scheme, replacing the photo-stationary-state assumption. The simplified street canyon model (SSCM) is used in the line source sub-grid model to calculate pollutant dispersion in street canyons. The WMPP (WORM Meteorological Pre-Processor) is used in the point source sub-grid model to calculate the wind speed at plume height. The EPISODE–CityChem model integrates the CityChem extension in EPISODE, with the capability of simulating the photochemistry and dispersion of multiple reactive pollutants within urban areas. The main focus of the model is the simulation of the complex atmospheric chemistry involved in the photochemical production of ozone in urban areas. The ability of EPISODE–CityChem to reproduce the temporal variation of major regulated pollutants at air quality monitoring stations in Hamburg, Germany, was compared to that of the standard EPISODE model and the TAPM (The Air Pollution Model) air quality model using identical meteorological fields and emissions. EPISODE–CityChem performs better than EPISODE and TAPM for the prediction of hourly NO2 concentrations at the traffic stations, which is attributable to the street canyon model. Observed levels of annual mean ozone at the five urban background stations in Hamburg are captured by the model within ±15 %. A performance analysis with the FAIRMODE DELTA tool for air quality in Hamburg showed that EPISODE–CityChem fulfils the model performance objectives for NO2 (hourly), O3 (daily max. of the 8 h running mean) and PM10 (daily mean) set forth in the Air Quality Directive, qualifying the model for use in policy applications. Envisaged applications of the EPISODE–CityChem model are urban air quality studies, emission control scenarios in relation to traffic restrictions and the source attribution of sector-specific emissions to observed levels of air pollutants at urban monitoring stations.

2019

The ESA WACMOS-ET: WP1300 - Reference Input Data Set Technical Specification. NILU F

Jimenez, C.; Prigent, C.; Aires, F.; Trigo, I.; Viterbo, P.; Schneider, P.; Prata, F.; Muller, J.-P.; Disney, M.; Miralles, D.; McCabe, M.; Reichstein, M.; Jung, M.; Hirschi, M.; Muller, B.; Seneviratne, S.

2013

The ESA WACMOS-ET Project: Advancing in the production of evapotranspiration from satellite observations. NILU F

Jimenez, C.; Prigent, C.; Miralles, D.; Trigo, I.; Muller, J.-P.; Disney, M.; McCabe, M.; Ershadi, A.; Muller, B.; Hirschi, M.; Seneviratne, S.; Schneider, P.; Prata, F.; Fisher, J.; Mu, Q.; Su, B.; Timmermans, J.; Abouali, M.; Chen, X.; Aires, F.; Jung, M.; Reichstein, M.; Fernandez, D.

2013

The ESA WACMOS-ET Project: Advancing in the production of evapotranspiration from satellite observations. NILU F

Jimenez, C.; Prigent, C.; Aires, F.; Miralles, D.; Trigo, I.; Muller, J.-P.; Disney, M.; McCabe, M.; Ershadi, A.; Muller, B.; Hirschi, M.; Seneviratne, S.; Schneider, P.; Prata, F.; Jung, M.; Reichstein, M.; Fisher, J.; Mu, Q.; Su, B.; Timmermans, J.; Abouali, M.; Chen, X.; Fernandez, D.

2013

The ESA WACMOS-ET project: Advancing in the production of evapotranspiration from satellite observations. NILU F

Jimenez, C.; Prigent, C.; Aires, F.; Miralles, D.; Trigo, I.; Muller, J.P.; Disney, M.; McCabe, M.; Ershadi, A.; Muller, B.; Hirschi, M.; Seneviratne, S.; Schneider, P.; Prata, F.; Jung, M.; Reichstein, M.; Fisher, J.; Mu, Q.; Su, B.; Timmermans, J.; Abouali, M.; Chen, X.; Fernandez, D.

2014

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