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Found 9889 publications. Showing page 45 of 396:

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Year  
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The Greenhouse Gas Budget of Terrestrial Ecosystems in East Asia Since 2000

Wang, Xuhui; Gao, Yuanyi; Jeong, Sujong; Ito, Akihiko; Bastos, Ana; Poulter, Benjamin; Wang, Yilong; Ciais, Philippe; Tian, Hanqin; Yuan, Wenping; Chandra, Naveen; Chevallier, Frédéric; Fan, Lei; Hong, Songbai; Lauerwald, Ronny; Li, Wei; Lin, Zhengyang; Pan, Naiqing; Patra, Prabir K.; Peng, Shushi; Ran, Lishan; Sang, Yuxing; Sitch, Stephen; Takashi, Maki; Thompson, Rona Louise; Wang, Chenzhi; Wang, Kai; Wang, Tao; Xi, Yi; Xu, Liang; Yan, Yanzi; Yun, Jeongmin; Zhang, Yao; Zhang, Yuzhong; Zhang, Zhen; Zheng, Bo; Zhou, Feng; Tao, Shu; Canadell, Josep G.; Piao, Shilong

East Asia (China, Japan, Koreas, and Mongolia) has been the world's economic engine over at least the past two decades, exhibiting a rapid increase in fossil fuel emissions of greenhouse gases (GHGs) and has expressed the recent ambition to achieve climate neutrality by mid-century. However, the GHG balance of its terrestrial ecosystems remains poorly constrained. Here, we present a synthesis of the three most important long-lived greenhouse gases (CO2, CH4, and N2O) budgets over East Asia during the decades of 2000s and 2010s, following a dual constraint approach. We estimate that terrestrial ecosystems in East Asia is close to neutrality of GHGs, with a magnitude of between −46.3 ± 505.9 Tg CO2eq yr−1 (the top-down approach) and −36.1 ± 207.1 Tg CO2eq yr−1 (the bottom-up approach) during 2000–2019. This net GHG sink includes a large land CO2 sink (−1229.3 ± 430.9 Tg CO2 yr−1 based on the top-down approach and −1353.8 ± 158.5 Tg CO2 yr−1 based on the bottom-up approach) being offset by biogenic CH4 and N2O emissions, predominantly coming from the agricultural sectors. Emerging data sources and modeling capacities have helped achieve agreement between the top-down and bottom-up approaches, but sizable uncertainties remain in several flux terms. For example, the reported CO2 flux from land use and land cover change varies from a net source of more than 300 Tg CO2 yr−1 to a net sink of ∼−700 Tg CO2 yr−1. Although terrestrial ecosystems over East Asia is close to GHG neutral currently, curbing agricultural GHG emissions and additional afforestation and forest managements have the potential to transform the terrestrial ecosystems into a net GHG sink, which would help in realizing East Asian countries' ambitions to achieve climate neutrality.

American Geophysical Union (AGU)

2024

The GreenEO Project: Satellite-Based Services to Support Sustainable Land Use Practices Under the European Green Deal

Hamer, Paul David; Frohn, Lise Marie; Geels, Camilla; Christensen, Jesper; Denby, Bruce; Simpson, David; Hutchings, Nicholas; Lopez-Aparicio, Susana; Schneider, Philipp; Cao, Tuan-Vu; Jimenez, Isadora; Fontenelle, Thais; Van Der A, Ronald; Mijling, Bas; Ding, Jieying; Trigo, Isabel F.; Calvet, Jean-Christophe; Schante, Joanne; Judes, Thomas; Tarrasón, Leonor

2025

The global re-cycling of persistent organic pollutants is strongly retarded by soils.

Ockenden, W.A.; Breivik, K.; Meijer, S.N.; Steinnes, E.; Sweetman, A.J.; Jones, K.C.

2003

The Global Nitrous Oxide Budget: A joint new activity of GCP and INI.

Tian, H.; Thompson, R.; Canadell, J.; Jackson, R. B.; Sutton, M. A.

2016

The Global N2O model Intercomparison Project (NMIP): Objectives, simulation protocol and expected products

Tian, Hanqin; Yang, Jia; Lu, Chaoqun; Xu, Rongting; Canadell, Josep G.; Jackson, Robert; Arneth, Almut; Chang, Jinfeng; Chen, Guangsheng; Ciais, Philippe; Gerber, Stefan; Ito, Akihiko; Huang, Yuanyuan; Joos, Fortunat; Lienert, Sebastian; Messina, Palmira; Olin, Stefan; Pan, Shufen; Peng, Changhui; Saikawa, Eri; Thompson, Rona Louise; Vuichard, Nicolas; Winiwarter, Wilfried; Zaehle, Sönke; Zhang, Bowen; Zhang, Kerou; Zhu, Qiuan

American Meteorological Society (AMS)

2018

The Global Fire Assimilation System (GFAS) & Peat fire emissions

Kaiser, Johannes; Stebel, Kerstin; Schneider, Philipp

2024

The Global Atmosphere Watch reactive gases measurement network.

Schultz, M.G.; Akimoto, H.; Bottenheim, J.; Buchmann, B.; Galbally, I.E.; Gilge, S.; Helmig, D.; Koide, H.; Lewis, A.C.; Novelli, P.C.; Plass-Dülmer, C.; Ryerson, T.B.; Steinbacher, M.; Steinbrecher, R.; Tarasova, O.; Tørseth, K.; Thouret, V.; Zellweger, C.

2015

The GAW World Data Centre for Aerosol - features and recent improvements. NILU PP

Fiebig, M.; Fjæraa, A.M.; Tørseth, K.

2013

The Future of VGI.

Antoniou, V.; See, L.; Foody, G.; Fonte, C. C.; Mooney, P.; Bastin, L.; Fritz, S.; Liu, H.-Y.; Olteanu-Raimond, Vatseva, R.

2017

The Fukushima inverse problem.

Martinez-Camara, M.; Dokmanic, I.; Ranieri, J.; Scheibler, R.; Vetterli, M.; Stohl, A.

2013

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

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

2012

The forums 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

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