A comprehensive multi-tiered approach to assessing weather penalties on O3 levels and exceedance days in Seoul using generalized additive models (2001–2019)

Over the past two decades, ambient O<sub>3</sub> air pollution in Seoul, the capital city of South Korea, has increased. As a secondary air pollutant, O<sub>3</sub> is affected not only by precursor gas emissions but also by meteorological conditions. This study examined the influence of weather changes in Seoul for 2001-2019 on the long-term daily maximum 8-h O<sub>3</sub> concentration (MDA8 O<sub>3</sub>) trends measured at 25 monitoring sites. As the relationship between O<sub>3</sub> and meteorological variables may not be linear, we used a generalized additive model framework to estimate O<sub>3</sub> trends, incorporating quantile and logistic regressions for continuous O<sub>3</sub> data and O<sub>3</sub> exceedance days (>60 ppb), respectively. Over the 19-year period, the O<sub>3</sub> concentrations in Seoul increased by 14.7 (SD = 3.2) and 13.1 (SD = 3.1) ppb before and after adjusting for local meteorology, respectively, resulting in an average weather penalty of 1.55 ppb. Seasonal variations in the penalty were substantial, showing a greater penalty (4.5 ppb) during the warm season (May-October) than during the cold season (November-April). Furthermore, the increase in O<sub>3</sub> concentration was more pronounced on days with comparatively high O<sub>3</sub> levels. During the warm season, the weather penalties on O<sub>3</sub> trends reached 3.7-4.0 ppb on high-O<sub>3</sub> days (75<sup>th</sup>, 95<sup>th</sup>, and 99<sup>th</sup> percentiles). From 2001 to 2019, the O<sub>3</sub> exceedance days started 2.66 days earlier and ended 2.30 days later per year, extending the peak-O<sub>3</sub> season by approximately 89 days in total. Weather changes accelerated the upward trend in the odds ratio of O<sub>3</sub> exceedance days by 3.8 years. Our findings indicate that O<sub>3</sub> exceedance days can occur in nearly all months owing to weather changes. The significant weather penalties on O<sub>3</sub> concentrations and exceedance days emphasize the need for a comprehensive O<sub>3</sub> air pollution mitigation strategy, considering non-emission factors that are increasingly being recognized in the context of climate change.

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Publication Details

Journal
Chemosphere
Published
2024-11-01
DOI
https://doi.org/10.1016/j.chemosphere.2024.143687
Citations
1
Primary Topic
Air Quality and Health Impacts
Type
article
Field-Weighted Citation Impact
0.31
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article

A comprehensive multi-tiered approach to assessing weather penalties on O3 levels and exceedance days in Seoul using generalized additive models (2001–2019)

Min Young Shin, Hyung Joo Lee
1 citations
Chemosphere
Air Quality and Health Impacts
0.31
article

A comprehensive multi-tiered approach to assessing weather penalties on O3 levels and exceedance days in Seoul using generalized additive models (2001–2019)

Min Young Shin, Hyung Joo Lee
article en
1 citations

Abstract

Over the past two decades, ambient O<sub>3</sub> air pollution in Seoul, the capital city of South Korea, has increased. As a secondary air pollutant, O<sub>3</sub> is affected not only by precursor gas emissions but also by meteorological conditions. This study examined the influence of weather changes in Seoul for 2001-2019 on the long-term daily maximum 8-h O<sub>3</sub> concentration (MDA8 O<sub>3</sub>) trends measured at 25 monitoring sites. As the relationship between O<sub>3</sub> and meteorological variables may not be linear, we used a generalized additive model framework to estimate O<sub>3</sub> trends, incorporating quantile and logistic regressions for continuous O<sub>3</sub> data and O<sub>3</sub> exceedance days (>60 ppb), respectively. Over the 19-year period, the O<sub>3</sub> concentrations in Seoul increased by 14.7 (SD = 3.2) and 13.1 (SD = 3.1) ppb before and after adjusting for local meteorology, respectively, resulting in an average weather penalty of 1.55 ppb. Seasonal variations in the penalty were substantial, showing a greater penalty (4.5 ppb) during the warm season (May-October) than during the cold season (November-April). Furthermore, the increase in O<sub>3</sub> concentration was more pronounced on days with comparatively high O<sub>3</sub> levels. During the warm season, the weather penalties on O<sub>3</sub> trends reached 3.7-4.0 ppb on high-O<sub>3</sub> days (75<sup>th</sup>, 95<sup>th</sup>, and 99<sup>th</sup> percentiles). From 2001 to 2019, the O<sub>3</sub> exceedance days started 2.66 days earlier and ended 2.30 days later per year, extending the peak-O<sub>3</sub> season by approximately 89 days in total. Weather changes accelerated the upward trend in the odds ratio of O<sub>3</sub> exceedance days by 3.8 years. Our findings indicate that O<sub>3</sub> exceedance days can occur in nearly all months owing to weather changes. The significant weather penalties on O<sub>3</sub> concentrations and exceedance days emphasize the need for a comprehensive O<sub>3</sub> air pollution mitigation strategy, considering non-emission factors that are increasingly being recognized in the context of climate change.

ChemosphereVol. 368
Pohang University of Science and Technology (KR)
Climate action
Openalex Percentile: Top 36%
Air Quality and Health Impacts
0.31
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