EGU25-10824, updated on 15 Mar 2025
https://doi.org/10.5194/egusphere-egu25-10824
EGU General Assembly 2025
© Author(s) 2025. This work is distributed under
the Creative Commons Attribution 4.0 License.
Geographic and Temporal Variability of atmospheric surface Ammonia (NH3) in France, Belgium, and the Netherlands (2015 – 2023) across different land-use types: Insights from Ground-Based and combined Satellite Observations.
Varun Katoch1, Anna Font1, Aude Bourin1, Esperanza Perdrix1, Mark Shephard2, Lieven Clarisse4, Jeroen Staelens3, Hans Berkhout5, Martin Van Damme4, and Véronique Riffault1
Varun Katoch et al.
  • 1IMT Nord Europe, Institut Mines-Télécom, Univ. Lille, Centre for Education, Research and Innovation in Energy Environment (CERI EE), 5900, Lille, France
  • 2Air Quality Research Division, Environment and Climate Change Canada (ECCC), Toronto, Ontario, Canada
  • 3Flanders Environment Agency (VMM), Unit Air, Kronenburgstraat 45, 2000 Antwerp, Belgium
  • 4Spectroscopy, Quantum Chemistry and Atmospheric Remote Sensing (SQUARES), BLU-ULB Research Center, Université libre de Bruxelles (ULB), Brussels, Belgium.
  • 5Environmental Systems Analysis Group, Wageningen University & Research, the Netherlands

This research study analyzes atmospheric ammonia (NH₃) surface concentrations in France, Belgium (Flanders region), and the Netherlands, highlighting their geographic, temporal, and diel variability from 2015 to 2023 using ground-based measurements (31 sites) and combined satellite data (IASI and CrIS). NH3 is the major alkaline gas in the atmosphere, affects air quality and aerosol formation, and degrades ecosystems, making its monitoring essential. The highest annual average NH₃ levels were observed in the Netherlands (7.4 ± 4.1 µg/m³), followed by Belgium (4.5±3.4 µg/m³) and France (3.7±2.1 µg/m³) as per in-situ observations. Rural areas characterized by agricultural practices showed higher levels than other land-use types, peaking in spring and summer due to fertilizer application and manure volatilization. Rural sites reached 8.5 ± 4.0 µg/m³ and 5.4 ± 3.9 µg/m³, in the Netherlands and Belgium (Flanders region) respectively. Urban areas recorded noticeable NH₃ concentrations either across Belgium (Flanders region) (3.5±2.0 µg/m³) and France (4.4 ± 2.0 µg/m³) which may be attributable to vehicular traffic, wastewater management, industrial operations, and the geographical dispersion of agricultural emissions. Seasonal variations observed notable NH₃ peaks in spring and summer, due to agricultural intensification and increased temperatures, while winter had the lowest concentrations due to decreased emissions. Diel patterns showed midday peaks in rural areas due to increased volatilization, while urban areas showed morning peaks related to traffic emissions. Satellite-derived NH₃ data from combined IASI and CrIS sensing showed moderate to strong correlations with ground-based measurements (R = 0.32–0.8), while satellites tended to underestimate local concentrations. Unlike surface measurements, satellite data revealed NH₃ concentrations across land-use types were little different, with means and standard deviations as follows: Crops (2.35 ± 2.08 µg/m³), High-Density Urban (2.39 ± 2.20 µg/m³), Low-Density Urban (2.35 ± 2.14 µg/m³), and Rural (2.26 ± 2.00 µg/m³). Comparable trends were noted in entire Belgium (+0.023 µg/m³ per year) and the Netherlands (+0.043 µg/m³ per year), where NH₃ concentrations were higher in 2020 and decreased in the following years possibly due to improved air dispersion and increased precipitation. The results highlight the key role of agriculture, which is the dominant source of NH₃ emissions, but urban regions also contribute significantly through vehicular and industrial activities. Effective mitigation techniques are crucial, including optimal fertilizer application, sophisticated manure management, and stringent urban emission regulations. These plans are in line with regional and national regulations, such as France’s PREPA plan, which aims to reduce NH₃ emissions by 13% by 2030 (Chatain et al., 2022). The integration of satellite and ground-based data offers a thorough understanding of NH₃ dynamics, facilitating the formulation of specific regulatory frameworks to reduce emissions, protect ecosystems, and improve air quality in these areas.

References

Chatain, M., Chretien, E., Crunaire, S., & Jantzem, E. (2022). Road Traffic and Its Influence on Urban Ammonia Concentrations (France). Atmosphere, 13(7), Article 7. https://doi.org/10.3390/atmos13071032

 

How to cite: Katoch, V., Font, A., Bourin, A., Perdrix, E., Shephard, M., Clarisse, L., Staelens, J., Berkhout, H., Damme, M. V., and Riffault, V.: Geographic and Temporal Variability of atmospheric surface Ammonia (NH3) in France, Belgium, and the Netherlands (2015 – 2023) across different land-use types: Insights from Ground-Based and combined Satellite Observations., EGU General Assembly 2025, Vienna, Austria, 27 Apr–2 May 2025, EGU25-10824, https://doi.org/10.5194/egusphere-egu25-10824, 2025.