Cargando…
Using Stable Sulfur Isotope to Trace Sulfur Oxidation Pathways during the Winter of 2017–2019 in Tianjin, North China
After the implementation of the Coal Replacing Project (CRP) in the northern parts of China in 2017, its effect on PM(2.5) composition is still unclear. In the study, water-soluble ionic components (WSICs) and stable sulfur isotope ratios (δ(34)S) of SO(4)(2−) in PM(2.5) collected during the domesti...
Autores principales: | , , , |
---|---|
Formato: | Online Artículo Texto |
Lenguaje: | English |
Publicado: |
MDPI
2022
|
Materias: | |
Acceso en línea: | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9518053/ https://www.ncbi.nlm.nih.gov/pubmed/36078683 http://dx.doi.org/10.3390/ijerph191710966 |
_version_ | 1784799089320263680 |
---|---|
author | Ding, Shiyuan Chen, Yingying Li, Qinkai Li, Xiao-Dong |
author_facet | Ding, Shiyuan Chen, Yingying Li, Qinkai Li, Xiao-Dong |
author_sort | Ding, Shiyuan |
collection | PubMed |
description | After the implementation of the Coal Replacing Project (CRP) in the northern parts of China in 2017, its effect on PM(2.5) composition is still unclear. In the study, water-soluble ionic components (WSICs) and stable sulfur isotope ratios (δ(34)S) of SO(4)(2−) in PM(2.5) collected during the domestic heating period before and after the implementation of CRP in Tianjin were analyzed. Results showed that the average concentrations of both PM(2.5) and WSICs have dropped dramatically after the CRP, especially for the SO(4)(2−) (by approximately 57–60%). After the CRP, the range of δ(34)S(sulfate) was significantly narrowed to 4.1–7.5‰ in January 2018 and 1.4–6.1‰ in January 2019, which suggested that the sulfur source was becoming simple. It was interesting that the δ(34)S(sulfate) value in the pollution period before the CRP was higher than that in the clean period, whereas it showed the opposite tendency after the CRP, which implied that the contribution of sea salt was high during the pollution period before the CRP. The MIXSIAR model calculated that the contributions of the transition-metal ion (TMI) oxidation and NO(2) oxidation pathways in the three sampling stages were higher than those of the OH radical oxidation and H(2)O(2)/O(3) oxidation pathways, indicating that the formation pathway of sulfate was mainly dominated by heterogeneous oxidation. Before the CRP, the NO(2) oxidation pathway was the dominant sulfate oxidation pathway during a haze episode, and the TMI oxidation pathway dominated the formation of sulfates after the CRP. |
format | Online Article Text |
id | pubmed-9518053 |
institution | National Center for Biotechnology Information |
language | English |
publishDate | 2022 |
publisher | MDPI |
record_format | MEDLINE/PubMed |
spelling | pubmed-95180532022-09-29 Using Stable Sulfur Isotope to Trace Sulfur Oxidation Pathways during the Winter of 2017–2019 in Tianjin, North China Ding, Shiyuan Chen, Yingying Li, Qinkai Li, Xiao-Dong Int J Environ Res Public Health Article After the implementation of the Coal Replacing Project (CRP) in the northern parts of China in 2017, its effect on PM(2.5) composition is still unclear. In the study, water-soluble ionic components (WSICs) and stable sulfur isotope ratios (δ(34)S) of SO(4)(2−) in PM(2.5) collected during the domestic heating period before and after the implementation of CRP in Tianjin were analyzed. Results showed that the average concentrations of both PM(2.5) and WSICs have dropped dramatically after the CRP, especially for the SO(4)(2−) (by approximately 57–60%). After the CRP, the range of δ(34)S(sulfate) was significantly narrowed to 4.1–7.5‰ in January 2018 and 1.4–6.1‰ in January 2019, which suggested that the sulfur source was becoming simple. It was interesting that the δ(34)S(sulfate) value in the pollution period before the CRP was higher than that in the clean period, whereas it showed the opposite tendency after the CRP, which implied that the contribution of sea salt was high during the pollution period before the CRP. The MIXSIAR model calculated that the contributions of the transition-metal ion (TMI) oxidation and NO(2) oxidation pathways in the three sampling stages were higher than those of the OH radical oxidation and H(2)O(2)/O(3) oxidation pathways, indicating that the formation pathway of sulfate was mainly dominated by heterogeneous oxidation. Before the CRP, the NO(2) oxidation pathway was the dominant sulfate oxidation pathway during a haze episode, and the TMI oxidation pathway dominated the formation of sulfates after the CRP. MDPI 2022-09-02 /pmc/articles/PMC9518053/ /pubmed/36078683 http://dx.doi.org/10.3390/ijerph191710966 Text en © 2022 by the authors. https://creativecommons.org/licenses/by/4.0/Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/). |
spellingShingle | Article Ding, Shiyuan Chen, Yingying Li, Qinkai Li, Xiao-Dong Using Stable Sulfur Isotope to Trace Sulfur Oxidation Pathways during the Winter of 2017–2019 in Tianjin, North China |
title | Using Stable Sulfur Isotope to Trace Sulfur Oxidation Pathways during the Winter of 2017–2019 in Tianjin, North China |
title_full | Using Stable Sulfur Isotope to Trace Sulfur Oxidation Pathways during the Winter of 2017–2019 in Tianjin, North China |
title_fullStr | Using Stable Sulfur Isotope to Trace Sulfur Oxidation Pathways during the Winter of 2017–2019 in Tianjin, North China |
title_full_unstemmed | Using Stable Sulfur Isotope to Trace Sulfur Oxidation Pathways during the Winter of 2017–2019 in Tianjin, North China |
title_short | Using Stable Sulfur Isotope to Trace Sulfur Oxidation Pathways during the Winter of 2017–2019 in Tianjin, North China |
title_sort | using stable sulfur isotope to trace sulfur oxidation pathways during the winter of 2017–2019 in tianjin, north china |
topic | Article |
url | https://www.ncbi.nlm.nih.gov/pmc/articles/PMC9518053/ https://www.ncbi.nlm.nih.gov/pubmed/36078683 http://dx.doi.org/10.3390/ijerph191710966 |
work_keys_str_mv | AT dingshiyuan usingstablesulfurisotopetotracesulfuroxidationpathwaysduringthewinterof20172019intianjinnorthchina AT chenyingying usingstablesulfurisotopetotracesulfuroxidationpathwaysduringthewinterof20172019intianjinnorthchina AT liqinkai usingstablesulfurisotopetotracesulfuroxidationpathwaysduringthewinterof20172019intianjinnorthchina AT lixiaodong usingstablesulfurisotopetotracesulfuroxidationpathwaysduringthewinterof20172019intianjinnorthchina |