The Impact of Farming Mitigation Measures on Ammonia Concentrations and Nitrogen Deposition in the UK
Ammonia (NH<sub>3</sub>) is an important precursor to airborne fine particulate matter (PM<sub>2.5</sub>) which causes significant health issues and can significantly impact terrestrial and aquatic ecosystems through deposition. The largest source of NH<sub>3</sub>...
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2025-03-01
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| author | Matthieu Pommier Jamie Bost Andrew Lewin Joe Richardson |
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| description | Ammonia (NH<sub>3</sub>) is an important precursor to airborne fine particulate matter (PM<sub>2.5</sub>) which causes significant health issues and can significantly impact terrestrial and aquatic ecosystems through deposition. The largest source of NH<sub>3</sub> emissions in the UK is agriculture, including animal husbandry and NH<sub>3</sub>-based fertilizer applications. This study investigates the impact of mitigation measures targeting UK NH<sub>3</sub> emissions from farming activities, focusing on their implications for air quality and nitrogen deposition in 2030. A series of mitigation scenarios—low2030, medium2030, and high2030—were developed through engagement with stakeholders, including farmers, advisers, and researchers, and their impact was modelled using the CMAQ air quality model. These scenarios represent varying levels of the uptake of mitigation measures compared to a baseline (base2030). The results indicate that reductions in total NH₃ emissions across the UK could reach up to 13% under the high2030 scenario (but reaching nearly 20% for some regions). These reductions can lead to significant decreases in NH₃ concentrations in some parts of the UK (up to 22%, ~1.2 µg/m<sup>3</sup>) but with a mean reduction of 8% across the UK. However, the reductions have a limited effect on fine ammonium particulate (<inline-formula><math display="inline"><semantics><mrow><msubsup><mrow><mi mathvariant="normal">N</mi><mi mathvariant="normal">H</mi></mrow><mrow><mn>4</mn></mrow><mrow><mo>+</mo></mrow></msubsup></mrow></semantics></math></inline-formula>) concentrations, achieving only modest reductions of up to 4%, with mean reductions of 1.6–1.9% due to a NH<sub>3</sub>-rich atmosphere. Consequently, the mitigation measures have minimal impact on secondary inorganic aerosol formation and PM<sub>2.5</sub> concentrations, aligning with findings from other studies in Europe and beyond. These results suggest that addressing the primary sources of PM<sub>2.5</sub> or other PM<sub>2.5</sub> precursors, either alone or in combination with NH<sub>3</sub>, may be necessary for more substantial air quality improvements. In terms of nitrogen (N) deposition, reductions in NH<sub>3</sub> emissions primarily affect NH<sub>3</sub> dry deposition, which constitutes approximately two-thirds of reduced nitrogen deposition. Total N deposition declines by 15–18% in source regions depending on the scenario, but national average reductions remain modest (~4%). While the study emphasizes annual estimates, further analyses focusing on finer temporal scales (e.g., daily or seasonal) could provide additional insights into exposure impacts. This research highlights the need for integrated mitigation strategies addressing multiple pollutants to achieve meaningful reductions in air pollution and nitrogen deposition. |
| format | Article |
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| spelling | doaj-art-bd9967c3eb424f6c8afdecb303b3d0c82025-08-20T02:17:19ZengMDPI AGAtmosphere2073-44332025-03-0116435310.3390/atmos16040353The Impact of Farming Mitigation Measures on Ammonia Concentrations and Nitrogen Deposition in the UKMatthieu Pommier0Jamie Bost1Andrew Lewin2Joe Richardson3Ricardo Energy & Environment, 18 Blythswood Square, Glasgow G2 4BG, UKRicardo Energy & Environment, 18 Blythswood Square, Glasgow G2 4BG, UKRicardo Energy & Environment, 18 Blythswood Square, Glasgow G2 4BG, UKRicardo Energy & Environment, 30 Eastbourne Terrace, London W2 6LA, UKAmmonia (NH<sub>3</sub>) is an important precursor to airborne fine particulate matter (PM<sub>2.5</sub>) which causes significant health issues and can significantly impact terrestrial and aquatic ecosystems through deposition. The largest source of NH<sub>3</sub> emissions in the UK is agriculture, including animal husbandry and NH<sub>3</sub>-based fertilizer applications. This study investigates the impact of mitigation measures targeting UK NH<sub>3</sub> emissions from farming activities, focusing on their implications for air quality and nitrogen deposition in 2030. A series of mitigation scenarios—low2030, medium2030, and high2030—were developed through engagement with stakeholders, including farmers, advisers, and researchers, and their impact was modelled using the CMAQ air quality model. These scenarios represent varying levels of the uptake of mitigation measures compared to a baseline (base2030). The results indicate that reductions in total NH₃ emissions across the UK could reach up to 13% under the high2030 scenario (but reaching nearly 20% for some regions). These reductions can lead to significant decreases in NH₃ concentrations in some parts of the UK (up to 22%, ~1.2 µg/m<sup>3</sup>) but with a mean reduction of 8% across the UK. However, the reductions have a limited effect on fine ammonium particulate (<inline-formula><math display="inline"><semantics><mrow><msubsup><mrow><mi mathvariant="normal">N</mi><mi mathvariant="normal">H</mi></mrow><mrow><mn>4</mn></mrow><mrow><mo>+</mo></mrow></msubsup></mrow></semantics></math></inline-formula>) concentrations, achieving only modest reductions of up to 4%, with mean reductions of 1.6–1.9% due to a NH<sub>3</sub>-rich atmosphere. Consequently, the mitigation measures have minimal impact on secondary inorganic aerosol formation and PM<sub>2.5</sub> concentrations, aligning with findings from other studies in Europe and beyond. These results suggest that addressing the primary sources of PM<sub>2.5</sub> or other PM<sub>2.5</sub> precursors, either alone or in combination with NH<sub>3</sub>, may be necessary for more substantial air quality improvements. In terms of nitrogen (N) deposition, reductions in NH<sub>3</sub> emissions primarily affect NH<sub>3</sub> dry deposition, which constitutes approximately two-thirds of reduced nitrogen deposition. Total N deposition declines by 15–18% in source regions depending on the scenario, but national average reductions remain modest (~4%). While the study emphasizes annual estimates, further analyses focusing on finer temporal scales (e.g., daily or seasonal) could provide additional insights into exposure impacts. This research highlights the need for integrated mitigation strategies addressing multiple pollutants to achieve meaningful reductions in air pollution and nitrogen deposition.https://www.mdpi.com/2073-4433/16/4/353ammoniafine particulate matteragricultureemissionsair pollutionregional modelling |
| spellingShingle | Matthieu Pommier Jamie Bost Andrew Lewin Joe Richardson The Impact of Farming Mitigation Measures on Ammonia Concentrations and Nitrogen Deposition in the UK Atmosphere ammonia fine particulate matter agriculture emissions air pollution regional modelling |
| title | The Impact of Farming Mitigation Measures on Ammonia Concentrations and Nitrogen Deposition in the UK |
| title_full | The Impact of Farming Mitigation Measures on Ammonia Concentrations and Nitrogen Deposition in the UK |
| title_fullStr | The Impact of Farming Mitigation Measures on Ammonia Concentrations and Nitrogen Deposition in the UK |
| title_full_unstemmed | The Impact of Farming Mitigation Measures on Ammonia Concentrations and Nitrogen Deposition in the UK |
| title_short | The Impact of Farming Mitigation Measures on Ammonia Concentrations and Nitrogen Deposition in the UK |
| title_sort | impact of farming mitigation measures on ammonia concentrations and nitrogen deposition in the uk |
| topic | ammonia fine particulate matter agriculture emissions air pollution regional modelling |
| url | https://www.mdpi.com/2073-4433/16/4/353 |
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