Cargando…
The contribution of new particle formation and subsequent growth to haze formation
We investigated the contribution of atmospheric new particle formation (NPF) and subsequent growth of the newly formed particles, characterized by high concentrations of fine particulate matter (PM(2.5)). In addition to having adverse effects on visibility and human health, these haze particles may...
Autores principales: | , , , , , , , , , |
---|---|
Formato: | Online Artículo Texto |
Lenguaje: | English |
Publicado: |
RSC
2022
|
Materias: | |
Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9119031/ https://www.ncbi.nlm.nih.gov/pubmed/35694136 http://dx.doi.org/10.1039/d1ea00096a |
_version_ | 1784710624202194944 |
---|---|
author | Kulmala, Markku Cai, Runlong Stolzenburg, Dominik Zhou, Ying Dada, Lubna Guo, Yishuo Yan, Chao Petäjä, Tuukka Jiang, Jingkun Kerminen, Veli-Matti |
author_facet | Kulmala, Markku Cai, Runlong Stolzenburg, Dominik Zhou, Ying Dada, Lubna Guo, Yishuo Yan, Chao Petäjä, Tuukka Jiang, Jingkun Kerminen, Veli-Matti |
author_sort | Kulmala, Markku |
collection | PubMed |
description | We investigated the contribution of atmospheric new particle formation (NPF) and subsequent growth of the newly formed particles, characterized by high concentrations of fine particulate matter (PM(2.5)). In addition to having adverse effects on visibility and human health, these haze particles may act as cloud condensation nuclei, having potentially large influences on clouds and precipitation. Using atmospheric observations performed in 2019 in Beijing, a polluted megacity in China, we showed that the variability of growth rates (GR) of particles originating from NPF depend only weakly on low-volatile vapor – highly oxidated organic molecules (HOMs) and sulphuric acid – concentrations and have no apparent connection with the strength of NPF or the level of background pollution. We then constrained aerosol dynamic model simulations with these observations. We showed that under conditions typical for the Beijing atmosphere, NPF is capable of contributing with more than 100 μg m(−3) to the PM(2.5) mass concentration and simultaneously >10(3) cm(−3) to the haze particle (diameter > 100 nm) number concentration. Our simulations reveal that the PM(2.5) mass concentration originating from NPF, strength of NPF, particle growth rate and pre-existing background particle population are all connected with each other. Concerning the PM pollution control, our results indicate that reducing primary particle emissions might not result in an effective enough decrease in total PM(2.5) mass concentrations until a reduction in emissions of precursor compounds for NPF and subsequent particle growth is imposed. |
format | Online Article Text |
id | pubmed-9119031 |
institution | National Center for Biotechnology Information |
language | English |
publishDate | 2022 |
publisher | RSC |
record_format | MEDLINE/PubMed |
spelling | pubmed-91190312022-06-10 The contribution of new particle formation and subsequent growth to haze formation Kulmala, Markku Cai, Runlong Stolzenburg, Dominik Zhou, Ying Dada, Lubna Guo, Yishuo Yan, Chao Petäjä, Tuukka Jiang, Jingkun Kerminen, Veli-Matti Environ Sci Atmos Chemistry We investigated the contribution of atmospheric new particle formation (NPF) and subsequent growth of the newly formed particles, characterized by high concentrations of fine particulate matter (PM(2.5)). In addition to having adverse effects on visibility and human health, these haze particles may act as cloud condensation nuclei, having potentially large influences on clouds and precipitation. Using atmospheric observations performed in 2019 in Beijing, a polluted megacity in China, we showed that the variability of growth rates (GR) of particles originating from NPF depend only weakly on low-volatile vapor – highly oxidated organic molecules (HOMs) and sulphuric acid – concentrations and have no apparent connection with the strength of NPF or the level of background pollution. We then constrained aerosol dynamic model simulations with these observations. We showed that under conditions typical for the Beijing atmosphere, NPF is capable of contributing with more than 100 μg m(−3) to the PM(2.5) mass concentration and simultaneously >10(3) cm(−3) to the haze particle (diameter > 100 nm) number concentration. Our simulations reveal that the PM(2.5) mass concentration originating from NPF, strength of NPF, particle growth rate and pre-existing background particle population are all connected with each other. Concerning the PM pollution control, our results indicate that reducing primary particle emissions might not result in an effective enough decrease in total PM(2.5) mass concentrations until a reduction in emissions of precursor compounds for NPF and subsequent particle growth is imposed. RSC 2022-03-22 /pmc/articles/PMC9119031/ /pubmed/35694136 http://dx.doi.org/10.1039/d1ea00096a Text en This journal is © The Royal Society of Chemistry https://creativecommons.org/licenses/by-nc/3.0/ |
spellingShingle | Chemistry Kulmala, Markku Cai, Runlong Stolzenburg, Dominik Zhou, Ying Dada, Lubna Guo, Yishuo Yan, Chao Petäjä, Tuukka Jiang, Jingkun Kerminen, Veli-Matti The contribution of new particle formation and subsequent growth to haze formation |
title | The contribution of new particle formation and subsequent growth to haze formation |
title_full | The contribution of new particle formation and subsequent growth to haze formation |
title_fullStr | The contribution of new particle formation and subsequent growth to haze formation |
title_full_unstemmed | The contribution of new particle formation and subsequent growth to haze formation |
title_short | The contribution of new particle formation and subsequent growth to haze formation |
title_sort | contribution of new particle formation and subsequent growth to haze formation |
topic | Chemistry |
url | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9119031/ https://www.ncbi.nlm.nih.gov/pubmed/35694136 http://dx.doi.org/10.1039/d1ea00096a |
work_keys_str_mv | AT kulmalamarkku thecontributionofnewparticleformationandsubsequentgrowthtohazeformation AT cairunlong thecontributionofnewparticleformationandsubsequentgrowthtohazeformation AT stolzenburgdominik thecontributionofnewparticleformationandsubsequentgrowthtohazeformation AT zhouying thecontributionofnewparticleformationandsubsequentgrowthtohazeformation AT dadalubna thecontributionofnewparticleformationandsubsequentgrowthtohazeformation AT guoyishuo thecontributionofnewparticleformationandsubsequentgrowthtohazeformation AT yanchao thecontributionofnewparticleformationandsubsequentgrowthtohazeformation AT petajatuukka thecontributionofnewparticleformationandsubsequentgrowthtohazeformation AT jiangjingkun thecontributionofnewparticleformationandsubsequentgrowthtohazeformation AT kerminenvelimatti thecontributionofnewparticleformationandsubsequentgrowthtohazeformation AT kulmalamarkku contributionofnewparticleformationandsubsequentgrowthtohazeformation AT cairunlong contributionofnewparticleformationandsubsequentgrowthtohazeformation AT stolzenburgdominik contributionofnewparticleformationandsubsequentgrowthtohazeformation AT zhouying contributionofnewparticleformationandsubsequentgrowthtohazeformation AT dadalubna contributionofnewparticleformationandsubsequentgrowthtohazeformation AT guoyishuo contributionofnewparticleformationandsubsequentgrowthtohazeformation AT yanchao contributionofnewparticleformationandsubsequentgrowthtohazeformation AT petajatuukka contributionofnewparticleformationandsubsequentgrowthtohazeformation AT jiangjingkun contributionofnewparticleformationandsubsequentgrowthtohazeformation AT kerminenvelimatti contributionofnewparticleformationandsubsequentgrowthtohazeformation |