안산 도심지 계절별 PM1 화학적 성분 특성
Characteristics of Seasonal PM1 Chemical Componentsin the urban area of Ansan
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초록
In this study, chemical properties of particulate matter (PM1) present in the urban area of Ansan in 2021 were analyzed using a high-resolution time-of-flight aerosol mass spectrometer (HR-ToF-AMS). Intensive observation was conducted during the measurement periods of spring (22 days), summer (29 days), autumn (60 days), and winter (29 days). High concentrations of PM1 were observed when a wind speed was low (< 0.81 m/s) and a direction of air flow was the east. PM1 concentration was the highest in spring (March), followed by summer (June and August), winter (December), and autumn (September and October). The main components of PM1 were organic, followed by nitrate, ammonium, and sulfate. The ratio of organic oxygen to organic carbon (O/C) was high in summer (0.64) and low in winter (0.51); conversely, the ratio of organic hydrogen to organic carbon (H/C) was higher in winter (1.66) than in summer (1.58). As for the oxidation rates of inorganic components, the nitrogen oxidation rate and sulfur oxidation rate were the highest in spring (NOR, 0.12; SOR, 0.64), which directly affected the rise in PM1 mass concentration in spring. Highly soluble nitrate was the largest component among the inorganic components of PM1, and the PM1 was found to be rich in ammonium in all seasons. PM1mass concentration and chemical composition increased with an increase of relative humidity (RH): the concentration of PM1 in wet conditions (RH > 60%) was found to be more than twice of that in dry conditions (RH < 40%). The largest component of PM1 in Ansan consisted of organic compounds; however, a high proportion of inorganic components, including nitrate, was also recorded.
Abstract
In this study, chemical properties of particulate matter (PM1) present in the urban area of Ansan in 2021 were analyzed using a high-resolution time-of-flight aerosol mass spectrometer (HR-ToF-AMS). Intensive observation was conducted during the measurement periods of spring (22 days), summer (29 days), autumn (60 days), and winter (29 days). High concentrations of PM1 were observed when a wind speed was low (< 0.81 m/s) and a direction of air flow was the east. PM1 concentration was the highest in spring (March), followed by summer (June and August), winter (December), and autumn (September and October). The main components of PM1 were organic, followed by nitrate, ammonium, and sulfate. The ratio of organic oxygen to organic carbon (O/C) was high in summer (0.64) and low in winter (0.51); conversely, the ratio of organic hydrogen to organic carbon (H/C) was higher in winter (1.66) than in summer (1.58). As for the oxidation rates of inorganic components, the nitrogen oxidation rate and sulfur oxidation rate were the highest in spring (NOR, 0.12; SOR, 0.64), which directly affected the rise in PM1 mass concentration in spring. Highly soluble nitrate was the largest component among the inorganic components of PM1, and the PM1 was found to be rich in ammonium in all seasons. PM1mass concentration and chemical composition increased with an increase of relative humidity (RH): the concentration of PM1 in wet conditions (RH > 60%) was found to be more than twice of that in dry conditions (RH < 40%). The largest component of PM1 in Ansan consisted of organic compounds; however, a high proportion of inorganic components, including nitrate, was also recorded.
참고문헌 (37)
- R. J. Charlson, "Climate forcing by anthropogenic aerosols", Science, 255(5043), pp.423~430 (1992)
- Intergovernmental Panel on Climate Change(IPCC), "IPCC Fourth Assessment Report 2007" (2007), Cambridge University Press
- F. Dominici, "Fine particulate air pollution and hospital admission for cardiovascular and respiratory diseases", Journal of the American Medical Association, 295, pp.1127~1134 (2006)
- IARC: Outdoor air pollution a leading environmental cause of cancer deaths, "International Agency for Research on Cancer (IARC)", ~ (2013)
- K. Huang, "Extreme haze pollution in beijing during january 2013 : Chemical characteristics, formation mechanism and role of fog processing", Atmospheric Chemistry and Physics, 14, pp.7517~7556 (2014)
- X. J. Zhao, "Analysis of a winter regional haze event and its formation mechanism in the north china plain", Atmospheric Chemistry and Physics, 13, pp.5685~5696 (2013)
- J. Chen, "Aerosol hygroscopicity parameter derived from the light scattering enhancement factor measurements in the north china plain", Atmospheric Chemistry and Physics, 14, pp.8105~8118 (2014)
- 이형민, "서울과 고산의 PM2.5 수분함량 계절 특성", 한국대기환경학회지, 26(1), pp.94~102 (2010), 한국대기환경학회
- 이승하, "서울시 PM10 내의 수용성 유기탄소와 수분함량과의 상관성 분석", 한국대기환경학회지, 33(1), pp.64~74 (2017), 한국대기환경학회[DOI]
- 김민석, "서울의 기상 조건에 따른 미세먼지와 시정의 상관성", 대기, 30(4), pp.391~404 (2020), 한국기상학회[DOI]
- 유혁균, "기상 조건이 서울의 PM 2.5와 PM 10에 미치는 영향", 한국기후변화학회지, 11(5), pp.521~528 (2020), 한국기후변화학회[DOI]
- 유근혜, "겨울 및 여름철 백령도와 서울에서 측정한 PM2.5 오염 특성", 한국대기환경학회지, 34(1), pp.38~55 (2018), 한국대기환경학회[DOI]
- 유근혜, "대기오염집중측정소별 2013~2015년 사이의 PM2.5 화학적 특성 차이 및 유발인자 조사", 한국대기환경학회지, 34(1), pp.16~37 (2018), 한국대기환경학회[DOI]
- 최진수, "한반도 서부유입권역에서 대기 중 에어로졸 성분의 화학적 특성 연구 I. PM 농도 및 화학 성분 특성", 한국대기환경학회지, 32(5), pp.469~484 (2016), 한국대기환경학회[DOI]
- 김정호, "여름철 서울과 백령도에서 PM1.0과 유기성분의 오염원에 관한 연구", 한국도시환경학회지, 17(3), pp.213~230 (2017), 한국도시환경학회
- T. Park, "Aircraft Measurements of Physicochemical Evolution of Atmospheric Aerosols in Air Pollution Plumes over a Megacity and Suburban Areas", Aerosol and Air Quality Research, 20, pp.2485~2494 (2020)
- 최진수, "한반도 서부유입권역에서 대기 중 에어로졸 성분의 화학적 특성 연구 II. 입자의 산성도 및 산화 특성", 한국대기환경학회지, 32(5), pp.485~500 (2016), 한국대기환경학회[DOI]
- H. Kim, "Measurement report : Characterization of servers spring have episodes and influences of long-range transport in the Seoul metropolitan area in March 2019", Atmospheric Chemistry and Physics, 20, pp.11527~11550 (2020)
- H. Kim, "Influence of intense secondary aerosol formation and long-range transport on aerosol chemistry and properties in the Seoul Metropolitan Area during spring time : results from KORUS-AQ", Atmospheric Chemistry and Physics, 18, pp.7149~7168 (2018)
- 박규태, "거주지역 내 여름기간 산화흐름반응기 (OFR)를 이용한 잠재성 2차 입자상물질 생성 및 화학적 특성 분석", 한국대기환경학회지, 35(6), pp.786~801 (2019), 한국대기환경학회[DOI]
- 최진수, "백령도에서 ToF-AMS를 이용한 2011년 5월 고농도 에어로졸 사례 연구", 한국도시환경학회지, 13(1), pp.19~32 (2013), 한국도시환경학회
- 김정호, "백령도에서 관측된 2011년 5월 고농도 에어로졸 사례의 유기성분 특성", 한국도시환경학회지, 14(3), pp.203~211 (2014), 한국도시환경학회
- 박종성, "AMS를 이용한 초미세입자의 서울지역 2014년 봄철 고농도 사례 특성 연구", 환경분석과 독성보건, 18(1), pp.12~25 (2015), 한국환경분석학회
- 박진수, "실시간 에어로졸 질량분석기를 이용한 PM1.0의 화학적성분의특성에 관한 연구", 한국도시환경학회지, 18(4), pp.485~494 (2018), 한국도시환경학회[DOI]
- J. R. Kimmel, "Real-time aerosol mass spectrometry with millisecond resolution", International Journal of Mass Spectrometry, 303(1), pp.15~26 (2011)
- I. H. Song, "Seasonal characteristics of PM1 in Seoul, Korea, measured using HR-ToF-Aerosol Mass Spectrometer in 2018", Atmospheric Environment, 266, pp.118717~ (2021)
- 2017년 대기오염집중측정소 연간 운영결과보고서, "국립환경과학원", ~ (2018)
- J. -E. Petit, "A user-friendly tool for comprehensive evaluation of the geographical origins of atmospheric pollution : wind and trajectory analyses", Environmental Modelling & Software, 88, pp.183~187 (2017)
- N. L. Ng, "Changes in organic aerosol composition with aging inferred from aerosol mass spectra", Atmospheric Chemistry and Physics, 11, pp.6465~6474 (2011)
- Q. Fu, "Mechanism of formation of the heaviest pollution episode ever recorded in the Yangtze River Delta, China", Atmospheric Environment, 42(9), pp.2023~2036 (2008)
- Y. Sun, "Investigation of the sources and evolution processes of severe haze pollution in Beijing in January 2013", Journal of Geophysical Research : Atmospheres, 119, pp.4380~4398 (2014)
- Q. Zhang, "Variations in PM2. 5, TSP, BC, and trace gases(NO2, SO2, and O3)between haze and non-haze episodes in winter over Xi'an, China", Atmospheric Environment, 112, pp.64~71 (2015)
- H. Xiao, "Chemical Characteristics of Major Inorganic Ions in PM2. 5 Based on Year-Long Observations in Guiyang, Southwest China-Implications for Formation Pathways and the Influences of Regional Transport", Atmosphere, 11(8), pp.847~ (2020)
- L. Zang, "Roles of Relative Humidity in Aerosol Pollution Aggravation over Central China during Wintertime", International Journal of Environmental Research and Public Health, 16, pp.4422~ (2019)
- 김창혁, "고농도 PM2.5 발생 시 국내외 영향에 따른 산업단지 인근 지역의 PM2.5 특성 분석", 한국대기환경학회지, 39(1), pp.62~76 (2023), 한국대기환경학회[DOI]
- Y. Ha, "Spatiotemporal differences on the real-time physicochemical characteristics of PM2. 5 particles in four Northeast Asian countries during Winter and Summer 2020-2021", Atmospheric Research, 283, pp.106581~ (2023)
- M. Ehn, "A large source of low-volatility secondary organic aerosol", Nature, 506, pp.476~479 (2014)
