CommentReducing the health effect of particles from agriculture
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Cited by (20)
Ammonia emissions from agriculture and their contribution to fine particulate matter: A review of implications for human health
2022, Journal of Environmental ManagementCitation Excerpt :Despite the significant role that NH3 has in the formation of PM2.5, it has been relatively lagging in terms of regulation when in comparison to other precursors such as SO2 and NOx (Megaritis et al., 2013). In fact, NH3 can increase the rate of reactions in the atmosphere of both SO2 and NOx, resulting in an even larger concentration of particulates (Brunekreef et al., 2015). In Europe for example, the NEC Directive required that in 2020, emissions of SO2 and NOx were to be reduced by 59% and 42% respectively, but NH3 emissions were to be reduced by only 6% in comparison (Brunekreef et al., 2015).
Impacts of nitrogen emissions on ecosystems and human health: A mini review
2021, Current Opinion in Environmental Science and HealthCitation Excerpt :However, epidemiological studies have frequently found adverse health effects of secondary inorganic aerosols [69], which may be due to several mechanisms, including an effect on the hygroscopicity of PM enhancing the exposure to toxic PM components, such as soluble transition metals [69]. Based on research over the past 20 years, it has thus been concluded that N particle components do not contribute less to the health risks than other particles [70–72]. Current experimental and epidemiological studies do not allow to relate specific health effects to individual components [66].
Respiratory Diseases in Farmers
2021, Encyclopedia of Respiratory Medicine, Second EditionUnderstanding the effects of air pollution on neurogenesis and gliogenesis in the growing and adult brain
2020, Current Opinion in PharmacologyEffects of the emergency control measures in Beijing on air quality improvement
2019, Atmospheric Pollution ResearchCitation Excerpt :BJ1 (N-CtrP) and BJ4 (CtrP) were two windy sample groups and the dust contributions were 3.1 μg/m3 (22.6%) and 2.0 μg/m3 (13.2%), respectively, which confirmed the effectiveness of dust control. Livestock and arable agricultural regions contributed largely to SIA formation due to their emissions of ammonia (Stokstad, 2014; Brunekreef et al., 2015; Chang et al., 2016). These regions were predominantly outside of the emission control areas and influenced Beijing by long range atmospheric transport (Meng et al., 2011).