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Found 9941 publications. Showing page 206 of 398:

Publication  
Year  
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Integrating LUCAS data with AI-driven models for predicting soil Salinization across the EU

Zarif, Mohammad Aziz; Hassani, Amirhossein; Panagos, Panos; Lebron, Inma; Robinson, David A.; Shokri, Nima

2024

Integrating Low-cost Sensor Systems and Networks to Enhance Air Quality Applications

Amegah, Kofi; Basart, Sara; Diez, Sebastiàn; Rosales, Colleen Marciel F.; Zimmerman, Naomi; Archer, Jan-Michael; Barreto, África; Bi, Jianzhao; Biggs, Russ; Castell, Nuria; deSouza, Priyanka; Dye, Tim; Fujita, Ryo; Giordano, Michael R.; Gonzalez, Marisa E.; Hasenkopf, Christa; Hassani, Amirhossein; Hodoli, Collins Gameli; Hofman, Jelle; Huneeus, Nicolás Jorge; Jayaratne, Rohan; Kroll, Jesse H.; Labrador, Lorenzo; Legri, Radouane; Levy, Robert C.; Marques, Tomas; Martins, Leila Droprinchinski; McMahon, Ethan; Mead, Mohammed Iqbal; Molina, Luisa T.; Montgomery, Anastasia; Morawska, Lidia; Ning, Zhi; Peltier, Richard; Popoola, Olalekan; Rojas, Néstor; Retama, Armando; Schneider, Philipp; Shairsing, Kerolyn; Strużewska, Joanna; Tang, Beiming; Van Poppel, Martine; Westervelt, Daniel M.; Zhang, Yang; Zheng, Mei

Low-cost air quality sensor systems (LCS) are emerging technologies for policy-relevant air quality analysis, including pollution levels, source identification, and forecasting. This report discusses LCS use in networks and alongside other data sources for comprehensive air quality applications, complementing other WMO publications on LCS operating principles, calibration, performance assessment, and data communication.

The LCS’s utility lies in their ability to provide new insights into air quality that existing data sources may not offer. While LCS data must be verified, their integration with other data sources can enhance understanding and management of air quality. In areas without reference-grade monitors, LCS can identify factors affecting local air quality and guide future monitoring efforts. Combining LCS data with satellite and other air quality systems can improve data reliability and establish corroborating evidence for observed trends. LCS can extend the spatial coverage of existing monitoring networks, offering localized insights and supporting effective air quality management policies. Co-locating LCS with reference-grade monitors helps quantify measurement uncertainties and apply LCS data appropriately for forecasting, source impact analysis, and community engagement.

World Meteorological Organization

2024

Integrated water vapor during rain and rain-free conditions above the Swiss Plateau

Hocke, Klemens; Bernet, Leonie; Wang, Wenyue; Mätzler, Christian; Hervo, Maxime; Haefele, Alexander

Water vapor column density, or vertically-integrated water vapor (IWV), is monitored by ground-based microwave radiometers (MWR) and ground-based receivers of the Global Navigation Satellite System (GNSS). For rain periods, the retrieval of IWV from GNSS Zenith Wet Delay (ZWD) neglects the atmospheric propagation delay of the GNSS signal by rain droplets. Similarly, it is difficult for ground-based dual-frequency single-polarisation microwave radiometers to separate the microwave emission of water vapor and cloud droplets from the rather strong microwave emission of rain. For ground-based microwave radiometry at Bern (Switzerland), we take the approach that IWV during rain is derived from linearly interpolated opacities before and after the rain period. The intermittent rain periods often appear as spikes in the time series of integrated liquid water (ILW) and are indicated by ILW ≥ 0.4 mm. In the present study, we assume that IWV measurements from radiosondes are not affected by rain. We intercompare the climatologies of IWV(rain), IWV(no rain), and IWV(all) obtained by radiosonde, ground-based GNSS atmosphere sounding, ground-based MWR, and ECMWF reanalysis (ERA5) at Payerne and Bern in Switzerland. In all seasons, IWV(rain) is 3.75 to 5.94 mm greater than IWV(no rain). The mean IWV differences between GNSS and radiosonde at Payerne are less than 0.26 mm. The datasets at Payerne show a better agreement than the datasets at Bern. However, the MWR at Bern agrees with the radiosonde at Payerne within 0.41 mm for IWV(rain) and 0.02 mm for IWV(no rain). Using the GNSS and rain gauge measurements at Payerne, we find that IWV(rain) increases with increase of the precipitation rate during summer as well as during winter. IWV(rain) above the Swiss Plateau is quite well estimated by GNSS and MWR though the standard retrievals are limited or hampered during rain periods.

MDPI

2021

Integrated testing for safety of nanoparticles.

Dusinska, M.; El Yamani, N.; Fjellsbø, L.M.; Rundén-Pran E.

2016

Integrated systems for forecasting urban meteorology, air pollution and population exposure.

Baklanov, A.; Hänninen, O.; Slørdal, L.H.; Kukkonen, J.; Bjergene, N.; Fay, B.; Finardi, S.; Hoe, S.C.; Jantunen, M.; Karppinen, A.; Rasmussen, A.; Skouloudis, A.; Sokhi, R.S.; Sørensen, J.H.; Ødegaard, V.

2007

Integrated systems for forecasting urban meteorology, air pollution and population exposure: FUMAPEX achievements.

Baklanov, A.; Bjergene, N.; Deserti, M.; Fay, B.; Finardi, S.; Hanninen, O.; Jantunen, M.; Hoe, S.; Kukkonen, J.; Lollobrigida, F.; Millan, M.; Rasmussen, A.; Rosland, P.; Skouloudis, A.; Slørdal, L. H.; Sokhi, R.

2005

Integrated monitoring: review of case study in PCBs in Slovak Republic. NILU PP

Liu, H.-Y.; Bartonova, A.; Trnovec, T.

2010

Integrated monitoring program on acidification of Chinese terrestrial systems (impacts) - A Chinese-Norwegian cooperation project.

Tang, D.; Lydersen, E.; Seip, H.M.; Angell, V.; Eilertsen, O.; Larssen, T.; Liu, X.; Kong, G.; Mulder, J.; Semb, A.; Solberg, S.; Tørseth, K.; Vogt, R.D.; Xiao, J.; Zhao, D.

2001

Integrated Monitoring Program on Acidification of Chinese Terrestrial Systems - IMPACTS. Annual Report - Results 2003.

Larssen, T.; Dagang, T.; Yi, H. (editors). Authors: Aas, W. (NILU), Tørseth, K. (NILU) et al.

2004

Integrated modeling and monitoring of emerging organic contaminants in the Nordic region. NILU F

Krogseth, I.S.; Breivik, K.; Schlabach, M.; McLachlan, M.S.; Wania, F.; Arnot, J.

2013

Integrated modeling and monitoring of emerging organic contaminants in the Nordic region. NILU F

Krogseth, I.S.; Breivik, K.; Schlabach, M.; McLachlan, M.S.; Wania, F.; Arnot, J.

2013

Integrated modeling and monitoring of emerging organic contaminants in the Nordic region NILU F

Krogseth, I.S.; Breivik, K.; Schlabach, M.,McLachlan, M.S.; Wania, F.; Arnot, J.

2012

Integrated management plan for The North Sea and Skagerrak. Priority knowledge needs.

Iversen, S.A.; van der Meeren, G.I.; Brungot, A.L.; Olsen, M.; Fjærbu, R.J.; Hansen, G.H.; Nilsen, B.; Fadnes, T.; Storeng, A.B.; Walday, M.; Overvik, M.; Anker-Nilssen, T.; Newton, A.; Røsland, I.

2012

Integrated management plan for The North Sea and Skagerrak. Indicators for a monitoring programme.

Storeng, A.B.; Havelin, T.; Riisberg, I.; Måge, A.; Koefoed, J.H.; Fadnes, T.; Brungot, A.L. (red.), van der Meeren, G.I. (red.), Pettersen, C.F. (red.) Bidragsytere: Newton, A. m.fl.

2012

Integrated management plan for The North Sea and Skagerrak. Cumulative environmental effects.

Kroglund, M.; Olsen, M. (red.) Østby, C.; Thorvik, T.; van der Meeren, G.; Gjelsvik, L.; Nilsen, B.; Nybakke, K.; Newton, A.; Anker-Nilssen, T.; Walday, M.; Jarandsen, B.; Stenløkk, J.; Røsland, I.; Koefoed, J.H.; Brungot, A.L.

2012

Integrated exposure assessment of northern goshawk (Accipiter gentilis) nestlings to legacy and emerging organic pollutants using non-destructive samples

Briels, Nathalie; Torgersen, Lene Norstrand; Castano-Ortíz, Jose M.; Løseth, Mari Engvig; Herzke, Dorte; Nygård, Torgeir; Bustnes, Jan Ove; Ciesielski, Tomasz Maciej; Poma, Giulia; Malarvannan, Govindan; Covaci, Adrian; Jaspers, Veerle

In the present study, concentrations of legacy and emerging contaminants were determined in three non-destructive matrices (plasma, preen oil and body feathers) of northern goshawk (Accipiter gentilis) nestlings. Persistent organic pollutants (POPs), including polychlorinated biphenyls (PCBs), organochlorine pesticides (OCPs) and polybrominated diphenyl ethers (PBDEs), together with emerging pollutants, including per- and polyfluorinated alkyl substances (PFASs), novel brominated flame retardants (NBFRs), phosphorus flame retardants (PFRs) and Dechlorane Plus isomers (DPs) were targeted. Plasma, preen oil and feather samples were collected from 61 goshawk nestlings in Norway (Trøndelag and Troms) in 2015 and 2016, and pollutant concentrations were compared between the three matrices. In plasma, PFASs were detected in the highest concentrations, ranging between 1.37 and 36.0 ng/mL, which suggests that the nestlings were recently and continuously exposed to these emerging contaminants, likely through dietary input. In preen oil, OCPs (169–3560 ng/g) showed the highest concentrations among the investigated compounds, consistent with their high lipophilicity. PFRs (2.60–314 ng/g) were the dominant compounds in feathers and are thought to originate mainly from external deposition, as they were not detected in the other two matrices. NBFRs and DPs were generally not detected in the nestlings, suggesting low presence of these emerging contaminants in their environment and/or low absorption. Strong and significant correlations between matrices were found for all POPs (rs = 0.46–0.95, p < 0.001), except for hexachlorobenzene (HCB, rs = 0.20, p = 0.13). Correlations for PFASs were less conclusive: linear perfluorooctane sulfonate (PFOS), perfluoroundecanoate (PFUnA), perfluorododecanoate (PFDoA) and perfluorotetradecanoate (PFTeA) showed strong and significant correlations between plasma and feathers (rs = 0.42–0.72, p < 0.02), however no correlation was found for perfluorohexane sulfonate (PFHxS), perfluorononanoate (PFNA) and perfluorotridecanoate (PFTriA) (rs = 0.05–0.33, p = 0.09–0.85). A lack of consistency between the PFAS compounds (contrary to POPs), and between studies, prevents concluding on the suitability of the investigated matrices for PFAS biomonitoring.

Elsevier

2019

Integrated assessment of releases of heavy metals in Europe.

Friedrich, R.; Pacyna, J.; Theloke, J.; Nitter, S.; Dutchak, S.; Fantke, P.; Fudala, J.; Hawiczka, S.; Huck, I.; Munthe, J.; Searl, A.; Strzelecka-Jastrzab, E.; Travnikov, O.

2009

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