1,713 research outputs found

    Analysis of influential factors for the relationship between PM_(2.5) and AOD in Beijing

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    The relationship between aerosol optical depth (AOD) and PM_(2.5) is often investigated in order to obtain surface PM_(2.5) from satellite observation of AOD with a broad area coverage. However, various factors could affect the AODโ€“PM_(2.5) regressions. Using both ground and satellite observations in Beijing from 2011 to 2015, this study analyzes the influential factors including the aerosol type, relative humidity (RH), planetary boundary layer height (PBLH), wind speed and direction, and the vertical structure of aerosol distribution. The ratio of PM_(2.5) to AOD, which is defined as ฮท, and the square of their correlation coefficient (R^2) have been examined. It shows that ฮท varies from 54.32 to 183.14, 87.32 to 104.79, 95.13 to 163.52, and 1.23 to 235.08โ€ฏยตgโ€ฏm^(โˆ’3) with aerosol type in spring, summer, fall, and winter, respectively. ฮท is smaller for scattering-dominant aerosols than for absorbing-dominant aerosols, and smaller for coarse-mode aerosols than for fine-mode aerosols. Both RH and PBLH affect the ฮท value significantly. The higher the RH, the smaller the ฮท, and the higher the PBLH, the smaller the ฮท. For AOD and PM2.5 data with the correction of RH and PBLH compared to those without, R^2 of monthly averaged PM_(2.5) and AOD at 14:00โ€ฏLT increases from 0.63 to 0.76, and R^2 of multi-year averaged PM_(2.5) and AOD by time of day increases from 0.01 to 0.93, 0.24 to 0.84, 0.85 to 0.91, and 0.84 to 0.93 in four seasons respectively. Wind direction is a key factor for the transport and spatialโ€“temporal distribution of aerosols originated from different sources with distinctive physicochemical characteristics. Similar to the variation in AOD and PM_(2.5), ฮท also decreases with the increasing surface wind speed, indicating that the contribution of surface PM_(2.5) concentrations to AOD decreases with surface wind speed. The vertical structure of aerosol exhibits a remarkable change with seasons, with most particles concentrated within about 500โ€ฏm in summer and within 150โ€ฏm in winter. Compared to the AOD of the whole atmosphere, AOD below 500โ€ฏm has a better correlation with PM_(2.5), for which R^2 is 0.77. This study suggests that all the above influential factors should be considered when we investigate the AODโ€“PM_(2.5) relationships

    Long-term effects of mitigation measures and meteorological conditions on aerosol characteristics in Beijing, China

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    The aim of this dissertation was to study the characteristics and development of Beijing aerosol pollution and to evaluate the effects of governmental mitigation measures thereon, while considering meteorological conditions. Based on a decade of aerosol measurements, chemical elements, black carbon (BC), particulate mercury (HgP) and size distribution of aerosol particles were studied to quantify the effects of these measures. Gallium was recommended as a tracer for coal combustion

    Interprovincial reliance for improving air quality in China:A case study on black carbon aerosol

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    Black carbon (BC) is of global concern because of its adverse effects on climate and human health. It can travel long distances via atmospheric movement and can be geographically relocated through trade. Here, we explored the integrated patterns of BC transport within 30 provinces in China from the perspective of meteorology and interprovincial trade using the Weather Research and Forecasting with Chemistry (WRF/Chem) model and multiregional input-output analysis. In general, cross-border BC transport, which accounts for more than 30% of the surface concentration, occurs mainly between neighboring provinces. Specifically, Hebei contributes 1.2 ฮผgยทm(-3) BC concentration in Tianjin. By contrast, trade typically drives virtual BC flows from developed provinces to heavily industrial provinces, with the largest net flow from Beijing to Hebei (4.2 Gg). Shanghai is most vulnerable to domestic consumption with an average interprovincial consumption influence efficiency of 1.5 ร— 10(-4) (ฮผgยทm(-3))/(billion Yuanยทyr(-1)). High efficiencies (โˆผ8 ร— 10(-5) (ฮผgยทm(-3))/(billion Yuanยทyr(-1))) are also found from regions including Beijing, Jiangsu, and Shanghai to regions including Hebei, Shandong, and Henan. The above source-receptor relationship indicates two control zones: Huabei and Huadong. Both mitigating end-of-pipe emissions and rationalizing the demand for pollution-intense products are important within the two control zones to reduce BC and other pollutants

    Assessing Atmospheric Pollution and Its Impacts on the Human Health

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    This reprint contains articles published in the Special Issue entitled "Assessing Atmospheric Pollution and Its Impacts on the Human Health" in the journal Atmosphere. The research focuses on the evaluation of atmospheric pollution by statistical methods on the one hand, and on the other hand, on the evaluation of the relationship between the level of pollution and the extent of its effect on the population's health, especially on pulmonary diseases

    Ground-level ozone pollution in China: A synthesis of recent findings on influencing factors and impacts

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    Ozone (O3) in the troposphere is an air pollutant and a greenhouse gas. In mainland China, after the Air Pollution Prevention and Action Plan was implemented in 2013 - and despite substantial decreases in the concentrations of other air pollutants - ambient O3 concentrations paradoxically increased in many urban areas. The worsening urban O3 pollution has fuelled numerous studies in recent years, which have enriched knowledge about O3-related processes and their impacts. In this article, we synthesise the key findings of over 500 articles on O3 over mainland China that were published in the past six years in English-language journals. We focus on recent changes in O3 concentrations, their meteorological and chemical drivers, complex O3 responses to the drastic decrease in human activities during coronavirus disease 2019 lockdowns, several emerging chemical processes, impacts on crops and trees, and the latest government interventions. ยฉ 2022 The Author(s). Published by IOP Publishing Ltd

    Estimating PM 2.5 concentrations in Xi'an City using a generalized additive model with multi-source monitoring data

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    ยฉ 2015 Song et al. This is an open access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited. Particulate matter with an aerodynamic diameter <2.5 ฮผm (PM2.5) represents a severe environmental problem and is of negative impact on human health. Xi'an City, with a population of 6.5 million, is among the highest concentrations of PM2.5 in China. In 2013, in total, there were 191 days in Xi'an City on which PM2.5 concentrations were greater than 100 ฮผg/m3. Recently, a few studies have explored the potential causes of high PM2.5 concentration using remote sensing data such as the MODIS aerosol optical thickness (AOT) product. Linear regression is a commonly used method to find statistical relationships among PM2.5 concentrations and other pollutants, including CO, NO2, SO2, and O3, which can be indicative of emission sources. The relationships of these variables, however, are usually complicated and non-linear. Therefore, a generalized additive model (GAM) is used to estimate the statistical relationships between potential variables and PM2.5 concentrations. This model contains linear functions of SO2 and CO, univariate smoothing non-linear functions of NO2, O3, AOT and temperature, and bivariate smoothing non-linear functions of location and wind variables. The model can explain 69.50% of PM2.5 concentrations, with R2 = 0.691, which improves the result of a stepwise linear regression (R2 = 0.582) by 18.73%. The two most significant variables, CO concentration and AOT, represent 20.65% and 19.54% of the deviance, respectively, while the three other gas-phase concentrations, SO2, NO2, and O3 account for 10.88% of the total deviance. These results show that in Xi'an City, the traffic and other industrial emissions are the primary source of PM2.5. Temperature, location, and wind variables also non-linearly related with PM2.5

    ์šฐ๋ฆฌ๋‚˜๋ผ ์ฃผ์š” ๋Œ€๋„์‹œ(์„œ์šธ, ๋Œ€์ „, ๊ด‘์ฃผ, ์šธ์‚ฐ)์˜ PM2.5 ๊ตฌ์„ฑ์„ฑ๋ถ„ ๋ฐ ์˜ค์—ผ์› ๊ธฐ์—ฌ๋„์— ์˜ํ•œ ๊ฑด๊ฐ•์˜ํ–ฅ ๋ถ„์„

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    ํ•™์œ„๋…ผ๋ฌธ(๋ฐ•์‚ฌ) -- ์„œ์šธ๋Œ€ํ•™๊ต๋Œ€ํ•™์› : ๋ณด๊ฑด๋Œ€ํ•™์› ํ™˜๊ฒฝ๋ณด๊ฑดํ•™๊ณผ, 2023. 2. ์ด์Šน๋ฌต.PM2.5์— ๋Œ€ํ•œ ๋…ธ์ถœ์€ ์ „ ์„ธ๊ณ„์ ์œผ๋กœ ์‚ฌ๋žŒ์˜ ๊ฑด๊ฐ•์— ์‹ฌ๊ฐํ•œ ์œ„ํ˜‘์ด ๋˜๊ณ  ์žˆ์œผ๋ฉฐ, ์‚ฌ๋ง๊ณผ ์žฅ์• ์— ์˜ํ–ฅ์„ ๋ฏธ์น˜๋Š” ๋Œ€ํ‘œ์ ์ธ ์œ„ํ—˜ ์ธ์ž(risk factor)์ด๋‹ค. ์šฐ๋ฆฌ๋‚˜๋ผ ์—ญ์‹œ ๊ธ‰์†ํ•œ ์‚ฐ์—…ํ™” ๋ฐ ๋„์‹œํ™”์— ๋”ฐ๋ผ PM2.5์— ์˜ํ•œ ์‹ฌ๊ฐํ•œ ๋Œ€๊ธฐ์งˆ ๋ฌธ์ œ๋ฅผ ๊ฒช๊ณ  ์žˆ์œผ๋ฉฐ, ๋Œ€๊ธฐ ์ค‘ PM2.5 ๋†๋„ ์ €๊ฐ์„ ์œ„ํ•ด ๋‹ค์–‘ํ•œ ์ •์ฑ…์ด ์ถ”์ง„๋˜๊ณ  ์žˆ๋‹ค. PM2.5๋Š” ๋ถˆ๊ท ์ผ ํ˜ผํ•ฉ๋ฌผ(heterogeneous mixture)๋กœ ํ™ฉ์‚ฐ์—ผ, ์งˆ์‚ฐ์—ผ, ์œ ๊ธฐํƒ„์†Œ, ์›์†Œํƒ„์†Œ ๋ฐ ๋น„์†Œ, ํฌ๋กฌ๊ณผ ๊ฐ™์€ ์ค‘๊ธˆ์† ๋“ฑ์˜ ๋งค์šฐ ๋‹ค์–‘ํ•œ ํ™”ํ•™๋ฌผ์งˆ๋กœ ๊ตฌ์„ฑ๋˜๋Š”๋ฐ, PM2.5์˜ ํ™”ํ•™์  ์กฐ์„ฑ์€ ์ง€์—ญ์— ๋”ฐ๋ผ ๋‹ค๋ฅธ (region- specific) ํŠน์„ฑ์ด ์žˆ๋‹ค. ์ด๋Š” PM2.5๊ฐ€ ๋ฐฐ์ถœ์›์—์„œ์˜ ์ง์ ‘ ๋ฐฐ์ถœ(primary emission) ๋ณด๋‹ค ํ™ฉ์‚ฐํ™”๋ฌผ(SOx), ์งˆ์†Œ์‚ฐํ™”๋ฌผ(NOx), ํœ˜๋ฐœ์„ฑ ์œ ๊ธฐํ™”ํ•ฉ๋ฌผ(VOCs) ๋“ฑ ๊ฐ€์Šค์ƒ ์ „๊ตฌ๋ฌผ์งˆ์˜ ๋Œ€๊ธฐ ์ค‘ ํ™”ํ•™๋ฐ˜์‘์— ์˜ํ•œ 2์ฐจ ์ƒ์„ฑ(secondary formation)์„ ํ†ตํ•ด ์ฃผ๋กœ ๋Œ€๊ธฐ ์ค‘์— ์กด์žฌํ•˜๊ธฐ ๋•Œ๋ฌธ์ด๋‹ค. ์ฆ‰, ๋Œ€์ƒ์ง€์—ญ ๋ฐ ์ธ๊ทผ์ง€์—ญ์˜ ์ „๊ตฌ๋ฌผ์งˆ ๋ฐฐ์ถœ๋Ÿ‰, ๋Œ€๊ธฐ ์ค‘ ์ „๊ตฌ๋ฌผ์งˆ์˜ ๋†๋„, ๊ธฐ์ƒ์กฐ๊ฑด, ์˜ค์—ผ์›์˜ ์œ„์น˜, ์ง€๋ฆฌ์  ํŠน์„ฑ ๋“ฑ ๋งค์šฐ ๋‹ค์–‘ํ•œ ์ธ์ž๋“ค์— ์˜ํ•ด PM2.5 ์กฐ์„ฑ์ด ๊ฒฐ์ •๋œ๋‹ค. PM2.5 ํ™”ํ•™์  ์กฐ์„ฑ์€ ๋Œ€์ƒ ์ง€์—ญ์˜ PM2.5์— ์˜ํ–ฅ์„ ๋‚˜ํƒ€๋‚ด๋Š” ์ฃผ์š” ์˜ค์—ผ์›์„ ๊ทœ๋ช…ํ•˜๊ณ , ๊ฐ ์˜ค์—ผ์›์˜ ๊ธฐ์—ฌ๋„๋ฅผ ์‚ฐ์ •ํ•จ์— ์žˆ์–ด ๋งค์šฐ ์ค‘์š”ํ•œ ์š”์†Œ์ด๋‹ค. ๋˜ํ•œ, ํ™”ํ•™์  ์กฐ์„ฑ์€ ๊ถ๊ทน์ ์œผ๋กœ PM2.5 ๋…ธ์ถœ์ด ์ธ์ฒด์— ์œ ๋ฐœํ•˜๋Š” ๊ฑด๊ฐ•์˜ํ–ฅ๊ณผ๋„ ๋ฐ€์ ‘ํ•˜๊ฒŒ ์—ฐ๊ด€๋˜์–ด ์žˆ๊ธฐ ๋•Œ๋ฌธ์— ๋ณด๊ฑดํ•™์  ์ธก๋ฉด์—์„œ์˜ PM2.5 ๊ด€๋ฆฌ๋ฅผ ์œ„ํ•ด์„œ๋Š” ๋Œ€์ƒ ์ง€์—ญ์—์„œ์˜ PM2.5์˜ ๊ตฌ์„ฑ์„ฑ๋ถ„ ๋ฐ ์˜ค์—ผ์›์— ์˜ํ•œ ๊ฑด๊ฐ•์˜ํ–ฅ์„ ์ •๋Ÿ‰์ ์œผ๋กœ ์‚ฐ์ •ํ•  ํ•„์š”๊ฐ€ ์žˆ๋‹ค.๋ณธ ์—ฐ๊ตฌ์—์„œ๋Š”๋Œ€๊ธฐ๊ด€๋ฆฌ๊ถŒ์—ญ์˜ ๋Œ€๊ธฐํ™˜๊ฒฝ๊ฐœ์„ ์— ๊ด€ํ•œ ํŠน๋ณ„๋ฒ•์— ๋”ฐ๋ผ ์ง€์ •๋œ 4๊ฐœ ๋Œ€๊ธฐ๊ด€๋ฆฌ๊ถŒ์—ญ์„ ๋Œ€ํ‘œํ•˜๋Š” ๋Œ€๋„์‹œ์ธ ์„œ์šธ, ๋Œ€์ „, ๊ด‘์ฃผ, ์šธ์‚ฐ์—์„œ 2014๋…„๋ถ€ํ„ฐ 5๋…„๊ฐ„ ๋ถ„์„๋œ ์ผ๋ณ„ PM2.5 ์งˆ๋Ÿ‰๋†๋„ ๋ฐ ๊ตฌ์„ฑ์„ฑ๋ถ„ ๋†๋„๋ฅผ ์ด์šฉํ•˜์—ฌ ๋„์‹œ๋ณ„ ์˜ค์—ผ์›์„ ๊ทœ๋ช…ํ•˜๊ณ , ๊ฐ ์˜ค์—ผ์›์˜ ๊ธฐ์—ฌ๋„๋ฅผ ์‚ฐ์ •ํ•˜์˜€๋‹ค. ๋˜ํ•œ, ๊ฐ™์€ ๊ธฐ๊ฐ„ PM2.5 ๊ตฌ์„ฑ์„ฑ๋ถ„ ๋†๋„ ๋ฐ ์˜ค์—ผ์› ๊ธฐ์—ฌ๋„์™€ ์ผ๋ณ„ ์‚ฌ๋ง์ž ์ˆ˜ ๋ฐ ์‘๊ธ‰์‹ค ๋‚ด์›ํ™˜์ž ์ˆ˜์˜ ์—ฐ๊ด€์„ฑ์„ ๋ถ„์„ํ•จ์œผ๋กœ์จ PM2.5 ๋…ธ์ถœ์ด ์‚ฌ๋ง๊ณผ ์งˆ๋ณ‘์— ๋ฏธ์น˜๋Š” ๊ฑด๊ฐ•์˜ํ–ฅ์„ ์‚ฐ์ •ํ•˜์—ฌ ๊ฑด๊ฐ•์˜ํ–ฅ ์ธก๋ฉด์—์„œ ๋„์‹œ๋ณ„ ์˜ค์—ผ์› ๊ด€๋ฆฌ์˜ ์šฐ์„ ์ˆœ์œ„ ์„ ์ •์„ ์œ„ํ•œ ๊ธฐ์ดˆ์ž๋ฃŒ๋ฅผ ๊ตฌ์ถ•ํ•˜์˜€๋‹ค.PMF ๋ชจ๋ธ๋ง์„ ํ†ตํ•ด ํ™•์ธ๋œ ์˜ค์—ผ์›์€ ์„œ์šธ, ๊ด‘์ฃผ, ์šธ์‚ฐ์˜ ๊ฒฝ์šฐ ์ด 10๊ฐœ๋กœ ์ด์ฐจ ์งˆ์‚ฐ์—ผ, ์ด์ฐจ ํ™ฉ์‚ฐ์—ผ, ์ž๋™์ฐจ, ์ƒ๋ฌผ์„ฑ ์—ฐ์†Œ, ์†Œ๊ฐ์‹œ์„ค, ํ† ์–‘, ์‚ฐ์—…, ์„ํƒ„ ์—ฐ์†Œ, ์„์œ  ์—ฐ์†Œ, ๋…ธํ›„ ํ•ด์—ผ์ž…์ž ์˜ค์—ผ์›์œผ๋กœ ๋‚˜ํƒ€๋‚ฌ๋‹ค. ๋Œ€์ „์˜ ๊ฒฝ์šฐ ์ง€๋ฆฌ์  ์œ„์น˜๋กœ ์ธํ•ด ๋…ธํ›„ ํ•ด์—ผ์ž…์ž ์˜ค์—ผ์›์€ ํ™•์ธ๋˜์ง€ ์•Š์•˜๊ณ , ๋‚˜๋จธ์ง€ 9๊ฐœ ์˜ค์—ผ์›์€ ๋‹ค๋ฅธ ๋„์‹œ๋“ค๊ณผ ๋™์ผํ•œ ๊ฒƒ์œผ๋กœ ํ™•์ธ๋˜์—ˆ๋‹ค. ์˜ค์—ผ์› ๊ธฐ์—ฌ๋„์— ์žˆ์–ด์„œ๋Š” 4๊ฐœ ๋„์‹œ ๋ชจ๋‘์—์„œ ๊ณตํ†ต์ ์œผ๋กœ ์ด์ฐจ ์งˆ์‚ฐ์—ผ, ์ด์ฐจ ํ™ฉ์‚ฐ์—ผ ๋ฐ ์ž๋™์ฐจ ์˜ค์—ผ์›์— ์˜ํ•œ ๊ธฐ์—ฌ๋„๊ฐ€ 60% ์ด์ƒ์œผ๋กœ ๋‚˜ํƒ€๋‚˜ PM2.5๊ฐ€ ์ฃผ๋กœ ๋Œ€๊ธฐ ์ค‘ ์ด์ฐจ์ƒ์„ฑ ๋ฐ ์ž๋™์ฐจ์— ๊ธฐ์ธํ•˜๋Š” ๊ฒƒ์„ ํ™•์ธํ•˜์˜€๋‹ค. ํ•˜์ง€๋งŒ ๋‹ค๋ฅธ ์˜ค์—ผ์›์˜ ๊ธฐ์—ฌ๋„๋Š” ๋„์‹œ๋ณ„ ํŠน์„ฑ์— ๋”ฐ๋ผ ๋‹ค๋ฅด๊ฒŒ ๋‚˜ํƒ€๋‚ฌ๋Š”๋ฐ ํŠนํžˆ, ๋Œ€๊ทœ๋ชจ ํ™”๋ ฅ๋ฐœ์ „์†Œ์— ์ธ์ ‘ํ•œ ์„œ์šธ, ๊ด‘์ฃผ์˜ ๊ฒฝ์šฐ ์„ํƒ„ ์—ฐ์†Œ ์˜ค์—ผ์›์˜ ๊ธฐ์—ฌ๋„๊ฐ€ 10% ๋‚ด์™ธ๋กœ ๋†’๊ฒŒ ๋‚˜ํƒ€๋‚˜ ํ•ด๋‹น ๋„์‹œ์—์„œ ๋„ค๋ฒˆ์งธ๋กœ ๋†’์€ ๊ธฐ์—ฌ๋„๋ฅผ ๋ณด์˜€๋‹ค. ๋ฐ˜๋ฉด, ๊ฐ€์žฅ ๋™์ชฝ์— ์œ„์น˜ํ•œ ์šธ์‚ฐ์—์„œ๋Š” ์„ํƒ„ ์—ฐ์†Œ ์˜ค์—ผ์›์˜ ๊ธฐ์—ฌ์œจ์€ ์ƒ๋Œ€์ ์œผ๋กœ ๋‚ฎ์•˜์œผ๋‚˜ ๋Œ€๊ทœ๋ชจ ์ค‘ํ™”ํ•™ ๊ณต์—… ๋„์‹œ์˜ ํŠน์„ฑ์ด ๋ฐ˜์˜๋˜์–ด ์‚ฐ์—… ์˜ค์—ผ์›์˜ ๊ธฐ์—ฌ๋„๊ฐ€ ๋‹ค๋ฅธ ๋„์‹œ์— ๋น„ํ•ด ์›”๋“ฑํžˆ ๋†’๊ฒŒ ๋‚˜ํƒ€๋‚ฌ๋‹ค.PM2.5 ๊ตฌ์„ฑ์„ฑ๋ถ„ ๋ฐ ์˜ค์—ผ์› ๊ธฐ์—ฌ๋„์™€ ๊ฑด๊ฐ•์˜ํ–ฅ์˜ ์—ฐ๊ด€์„ฑ์„ ๋ถ„์„ํ•œ ๊ฒฐ๊ณผ๋Š” PM2.5 ๊ตฌ์„ฑ์„ฑ๋ถ„ ๋†๋„ ๋ฐ ์˜ค์—ผ์› ๊ธฐ์—ฌ๋„์˜ ๋‹จ์œ„(IQR) ์ฆ๊ฐ€๊ฐ€ ์ „๋ฐ˜์ ์œผ๋กœ ์‚ฌ๋ง ๋ฐ ์งˆ๋ณ‘์˜ ์ƒ๋Œ€์œ„ํ—˜๋„ ์ฆ๊ฐ€๋กœ ์ด์–ด์ง์„ ๋ณด์—ฌ์ฃผ์—ˆ๋‹ค. ๊ทธ๋Ÿฌ๋‚˜ ๊ตฌ์„ฑ์„ฑ๋ถ„ ๋ฐ ์˜ค์—ผ์› ๊ธฐ์—ฌ๋„์™€ ๊ฑด๊ฐ•์˜ํ–ฅ ์‚ฌ์ด ์—ฐ๊ด€์„ฑ์˜ ์œ ์˜์„ฑ ๋ฐ ์ •๋„๋Š” ์ง€์—ญ๋งˆ๋‹ค ๋‹ค๋ฅด๊ฒŒ ๋‚˜ํƒ€๋‚ฌ๋‹ค. ๋จผ์ € ๊ตฌ์„ฑ์„ฑ๋ถ„์ด ์‚ฌ๋ง์— ๋ฏธ์น˜๋Š” ์˜ํ–ฅ์˜ ๊ฒฝ์šฐ ์„œ์šธ, ๋Œ€์ „์—์„œ๋Š” ์ฃผ๋กœ ์‹ฌํ˜ˆ๊ด€๊ณ„ ์‚ฌ๋ง์—์„œ ์ค‘๊ธˆ์†, ์œ ๊ธฐํƒ„์†Œ ๋“ฑ์˜ ๊ตฌ์„ฑ์„ฑ๋ถ„๊ณผ์˜ ์œ ์˜ํ•œ ์—ฐ๊ด€์„ฑ์ด ํ™•์ธ๋˜์—ˆ์œผ๋‚˜ ๊ด‘์ฃผ์—์„œ๋Š” ์ฃผ๋กœ ํ˜ธํก๊ธฐ๊ณ„ ์‚ฌ๋ง์˜ ์ƒ๋Œ€์œ„ํ—˜๋„๊ฐ€ ์ค‘๊ธˆ์†, ์ด์˜จ์„ฑ๋ถ„๊ณผ ๋ฐ€์ ‘ํ•œ ๊ด€๊ณ„๊ฐ€ ์žˆ๋Š” ๊ฒƒ์œผ๋กœ ๋‚˜ํƒ€๋‚ฌ๋‹ค. ์˜ค์—ผ์›-์‚ฌ๋ง์˜ ์—ฐ๊ด€์„ฑ์— ์žˆ์–ด์„œ๋Š” ์‚ฌ๋ง์˜ ์ƒ๋Œ€์œ„ํ—˜๋„๋ฅผ ์ฆ๊ฐ€์‹œํ‚จ ๊ตฌ์„ฑ์„ฑ๋ถ„๊ณผ ๋ฐ€์ ‘ํ•œ ์˜ค์—ผ์›์˜ ๊ธฐ์—ฌ๋„ ์ฆ๊ฐ€๊ฐ€ ์‚ฌ๋ง๊ณผ ๋ฐ€์ ‘ํ•œ ๊ฒƒ์œผ๋กœ ํ™•์ธ๋˜์—ˆ๋‹ค. ๋”ฐ๋ผ์„œ PM2.5 ๋…ธ์ถœ๋กœ ์ธํ•œ ์‚ฌ๋ง ์˜ํ–ฅ์„ ์ค„์ด๊ธฐ ์œ„ํ•ด์„œ๋Š” ๋„์‹œ๋ณ„ ๊ฑด๊ฐ•์˜ํ–ฅ ๋ถ„์„์— ๋”ฐ๋ผ ์˜ค์—ผ์› ๊ด€๋ฆฌ์˜ ์šฐ์„ ์ˆœ์œ„๋ฅผ ๋งˆ๋ จํ•˜๊ณ , ๊ฐ ์˜ค์—ผ์›๋ณ„ ๋ฐฐ์ถœ๋Ÿ‰ ์ €๊ฐ์„ ์œ„ํ•œ ์ •์ฑ…์ด ์ˆ˜๋ฐ˜๋  ํ•„์š”์„ฑ์ด ์žˆ๋‹ค. ์‚ฌ๋ง๊ณผ ๋‹ค๋ฅด๊ฒŒ PM2.5 ๋…ธ์ถœ์— ๋”ฐ๋ฅธ ์งˆ๋ณ‘ ์˜ํ–ฅ์€ ์ฃผ๋กœ ํ˜ธํก๊ธฐ๊ณ„ ์งˆ๋ณ‘์„ ์ค‘์‹ฌ์œผ๋กœ ๊ตฌ์„ฑ์„ฑ๋ถ„ ๋ฐ ์˜ค์—ผ์› ๊ธฐ์—ฌ๋„์™€ ์œ ์˜ํ•œ ์—ฐ๊ด€์„ฑ์ด ํ™•์ธ๋˜์—ˆ๋‹ค. ์ด ๊ฐ™์€ ๊ฒฐ๊ณผ๋Š” PM2.5์˜ ์ฃผ ๋…ธ์ถœ๊ฒฝ๋กœ๊ฐ€ ํ˜ธํก(inhalation)์ด๊ณ , PM2.5๊ฐ€ ๋งค์šฐ ๋ฏธ์„ธํ•œ ํฌ๊ธฐ๋กœ ์ธํ•ด ๋งค์งˆ์ธ ๊ณต๊ธฐ์™€ ์œ ์‚ฌํ•˜๊ฒŒ ๊ฑฐ๋™ํ•จ์— ๋”ฐ๋ผ ์ƒ๊ธฐ๋„ ๋ฟ๋งŒ ์•„๋‹ˆ๋ผ ํ•˜๊ธฐ๋„์ธ ๊ธฐ๊ด€, ๊ธฐ๊ด€์ง€, ํํฌ ๋“ฑ์—๋„ ์‰ฝ๊ฒŒ ๋„๋‹ฌํ•œ ํ›„ ์—ผ์ฆ ๋ฐ˜์‘, ์‚ฐํ™”์ŠคํŠธ๋ ˆ์Šค ๋“ฑ์˜ ๋ฉ”์ปค๋‹ˆ์ฆ˜์„ ํ†ตํ•ด ํ˜ธํก๊ธฐ๊ณ„์— ๊ธ‰์„ฑ ์˜ํ–ฅ์„ ๋‚˜ํƒ€๋‚ด๊ธฐ ๋•Œ๋ฌธ์œผ๋กœ ํŒ๋‹จ๋œ๋‹ค. ์ƒ๊ธฐ ๋ฉ”์ปค๋‹ˆ์ฆ˜์— ์˜ํ•ด ํ˜ธํก๊ธฐ๊ณ„ ๊ธฐ๊ด€์—์„œ ์ƒ์„ฑ๋œ ์—ผ์ฆ์„ฑ ์‚ฌ์ดํ† ์นด์ธ, ํ™œ์„ฑ์‚ฐ์†Œ์ข… ๋“ฑ์€ ๋‹ค์‹œ ์ „์‹ ์ˆœํ™˜์„ ํ†ตํ•ด ์‹ฌํ˜ˆ๊ด€๊ณ„์— ๋„๋‹ฌํ•ด ์งˆ๋ณ‘์„ ์œ ๋ฐœํ•  ์ˆ˜ ์žˆ๊ณ , ๊ถ๊ทน์ ์œผ๋กœ ์‚ฌ๋ง์˜ ์œ„ํ—˜๋„๋ฅผ ์ฆ๊ฐ€์‹œํ‚ฌ ์ˆ˜ ์žˆ๋‹ค. ๋ณธ ์—ฐ๊ตฌ์˜ ๊ฒฐ๊ณผ๋Š” ๋Œ€๊ธฐ ์ค‘ ์งˆ๋Ÿ‰๋†๋„ ์ €๊ฐ์— ์ดˆ์ ์ด ๋งž์ถ”์–ด์ ธ ์žˆ๋Š” ํ˜„์žฌ์˜ PM2.5 ๊ด€๋ฆฌ์ •์ฑ…์ด ์ง€์—ญ๋ณ„ ์กฐ์„ฑ, ์˜ค์—ผ์› ๊ธฐ์—ฌ๋„ ๋ฐ ๊ฑด๊ฐ•์˜ํ–ฅ ํŠน์„ฑ์„ ๊ณ ๋ คํ•œ ์ •์ฑ…์œผ๋กœ ํ™•๋Œ€๋  ํ•„์š”์„ฑ์ด ์žˆ์Œ์„ ์‹œ์‚ฌํ•œ๋‹ค. ์ฆ‰, ํ™˜๊ฒฝ ์˜ค์—ผ๋ฌผ์งˆ ๊ด€๋ฆฌ์˜ ๊ถ๊ทน์ ์ธ ๋ชฉ์ ์€ ์˜ค์—ผ๋ฌผ์งˆ์— ๋Œ€ํ•œ ๋…ธ์ถœ์ด ์ธ์ฒด์— ์œ ๋ฐœํ•˜๋Š” ๋ถ€์ •์ ์ธ ์˜ํ–ฅ์„ ์ตœ์†Œํ™”ํ•จ์œผ๋กœ์จ ๊ตญ๋ฏผ์˜ ๊ฑด๊ฐ•๊ณผ ์•ˆ๋…•์„ ์œ ์ง€ํ•˜๋Š” ๊ฒƒ์ด๊ธฐ ๋•Œ๋ฌธ์— ์ง€์—ญ ํŠน์ด์ ์ธ PM2.5์˜ ์กฐ์„ฑ๊ณผ ๊ทธ๋กœ ์ธํ•ด ๋‹ค๋ฅด๊ฒŒ ๋‚˜ํƒ€๋‚˜๋Š” ๊ฑด๊ฐ•์˜ํ–ฅ์„ ํ‰๊ฐ€ํ•จ์œผ๋กœ์จ ์ตœ์ ์˜ ๋Œ€๊ธฐ๊ด€๋ฆฌ ์ •์ฑ… ๋ฐ ๊ณ„ํš ๋“ฑ์„ ์ˆ˜๋ฆฝํ•˜์—ฌ ์‹คํ–‰ํ•  ํ•„์š”๊ฐ€ ์žˆ๋‹ค.Exposure to fine particulate matter (PM2.5) has been revealed as severe threats to human health and one of the major risk factors driving both death and disability. South Korea is one of the countries have been suffering from serious air pollution, especially problems related to PM2.5. PM2.5 is a heterogeneous mixture of numerous components such as sulfate, nitrate, organic carbon, elemental carbon, arsenic, lead. The chemical compositional characteristics are highly region-specific because most of the PM2.5 mass concentration is attributable to secondary particles, formed by the reactions among gaseous precursors in the atmosphere. In general, the factors affecting secondary formation are meteorological conditions, source locations, geographical features of the region well as the ambient concentration of gaseous pollutants including sulfur oxides, nitrogen oxides. Therefore, understanding the chemical composition and source profiles in the region of interest is crucial for controlling PM2.5. Moreover, the assessment of health risk caused by PM2.5 exposure needs to conducted to mitigate the adverse health effects from a public health perspective. In this study, the associations of cause-specific mortality and morbidity with both PM2.5 constituents and source contributions were investigated in four metropolitan cities, namely Seoul, Daejeon, Gwangju, and Ulsan. Each city represents the air control zone in the country designated by a special act as of April 2020 to mitigate and control the air pollution on a regional basis. For the analyses, generalized linear model (GLM) was applied to the data including daily health outcomes, the average concentrations of PM2.5 constituents and the results of PMF modelling. The findings show that short-term exposure to PM2.5 constituents largely increased the relative risk (RR) of mortality and morbidity. However, the significance and strength of associations were different among the cities. In addition, source contributions also increased the RR of mortality and morbidity with different strength. In summary, the results of the study imply the importance of approaches based on compositional characteristics and health risk in making proper policies in the region of interest to mitigate the negative health effects of PM2.5 exposure more efficiently.Chapter 1. Background 1 1. Introduction 2 2. Potential mechanisms of health effects of PM2.5 exposure 4 2.1 Respiratory system 4 2.2 Cardiovascular system 6 3. Objectives of the study 7 References 10 Chapter 2. Compositional characteristics of ambient PM2.5 in Seoul, Daejeon, Gwangju, and Ulsan during 2014โ€“2018 16 Abstract 17 1. Introduction 18 2. Materials and methods 19 2.1 Study area and period 19 2.2 Data 22 3. Results and discussion 23 3.1 PM2.5 mass and gaseous precursors 23 3.2 PM2.5 chemical constituents 31 4. Conclusions 50 References 52 Chapter 3. Source apportionment of PM2.5 in Seoul, Daejeon, Gwangju, and Ulsan during 2014-2018 56 Abstract 57 1. Introduction 58 2. Materials and methods 59 2.1 Input data 59 2.2 PMF modelling 59 2.3 Conditional probability function 61 2.4 Potential source contribution function 62 3. Results and discussion 64 3.1 Source apportionment 64 3.2 Seasonal source contributions 78 3.3 Possible source locations 86 4. Conclusions 108 References 110 Chapter 4. Associations of PM2.5 chemical constituents and source contributions with mortality 122 Abstract 123 1. Introduction 124 2. Materials and methods 125 2.1 Data 125 2.2 Statistical model 126 3. Results and discussion 129 4. Conclusions 150 References 152 Chapter 5. Associations of PM2.5 chemical constituents and source contributions with morbidity 158 Abstract 159 1. Introduction 160 2. Materials and methods 161 2.1 Data 161 2.2 Statistical model 163 3. Results and discussion 165 4. Conclusions 181 References 183 Chapter 6. Summary, significance, and conclusions 192 1. Summary 193 1.1 Compositional characteristics and source apportionment of ambient PM2.5 in Seoul, Daejeon, Gwangju, and Ulsan during 2014-2018 193 1.2 Associations of PM2.5 chemical constituents and source contributions with mortality 195 1.3 Associations of PM2.5 chemical constituents and source contributions with morbidity 196 2. Significance 197 2.1 Region-specific characteristics of the health effects of PM2.5 exposure on mortality 197 2.2 Impacts of government policy interventions on PM2.5 composition, source contribution, and health effects 198 3. Conclusions 207 References 210 ๊ตญ๋ฌธ์ดˆ๋ก 213๋ฐ•

    Integrated human exposure to air pollution

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    The book โ€œIntegrated human exposure to air pollutionโ€ aimed to increase knowledge about human exposure in different micro-environments, or when citizens are performing specific tasks, to demonstrate methodologies for the understanding of pollution sources and their impact on indoor and ambient air quality, and, ultimately, to identify the most effective mitigation measures to decrease human exposure and protect public health. Taking advantage of the latest available tools, such as internet of things (IoT), low-cost sensors and a wide access to online platforms and apps by the citizens, new methodologies and approaches can be implemented to understand which factors can influence human exposure to air pollution. This knowledge, when made available to the citizens, along with the awareness of the impact of air pollution on human life and earth systems, can empower them to act, individually or collectively, to promote behavioral changes aiming to reduce pollutantsโ€™ emissions. Overall, this book gathers fourteen innovative studies that provide new insights regarding these important topics within the scope of human exposure to air pollution. A total of five main areas were discussed and explored within this book and, hopefully, can contribute to the advance of knowledge in this field

    Introduction to Special Issue - In-depth study of air pollution sources and processes within Beijing and its surrounding region (APHH-2 Beijing)

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    Abstract. The Atmospheric Pollution and Human Health in a Chinese Megacity (APHH-Beijing) programme is an international collaborative project focusing on understanding the sources, processes and health effects of air pollution in the Beijing megacity. APHH-Beijing brings together leading China and UK research groups, state-of-the-art infrastructure and air quality models to work on four research themes: (1) sources and emissions of air pollutants; (2) atmospheric processes affecting urban air pollution; (3) air pollution exposure and health impacts; and (4) interventions and solutions. Themes 1 and 2 are closely integrated and support Theme 3, while Themes 1-3 provide scientific data for Theme 4 to develop cost-effective air pollution mitigation solutions. This paper provides an introduction to (i) the rationale of the APHH-Beijing programme, and (ii) the measurement and modelling activities performed as part of it. In addition, this paper introduces the meteorology and air quality conditions during two joint intensive field campaigns - a core integration activity in APHH-Beijing. The coordinated campaigns provided observations of the atmospheric chemistry and physics at two sites: (i) the Institute of Atmospheric Physics in central Beijing, and (ii) Pinggu in rural Beijing during 10 November โ€“ 10 December 2016 (winter) and 21 May- 22 June 2017 (summer). The campaigns were complemented by numerical modelling and automatic air quality and low-cost sensor observations in the Beijing megacity. In summary, the paper provides background information on the APHH-Beijing programme, and sets the scene for more focussed papers addressing specific aspects, processes and effects of air pollution in Beijing
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