• Proceedings of the Korea Air Pollution Research Association Conference
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• 2002.11a
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• pp.137-138
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• 2002

입자상 물질은 자연적 또는 인위적인 오염원에 의해 직접 대기로 배출되거나 가스상 물질의 전환 과정을 통해 생성된다. 서울을 비롯한 우리나라 시정(visibility)은 맡은 부분이 가스상 물질의 전환을 통해 생성된 미세 입자에 영향을 받고 있기 때문에 미세 입자의 생성(formation)과 성장(growth) 변화를 연구하는 것은 시정(visibility)의 원인을 밝히는 중요한 과정이라고 할 수 있다. (중략)

• Proceedings of the Korea Air Pollution Research Association Conference
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• 2002.11a
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• pp.391-392
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• 2002

대기 중에는 오염원으로부터 직접 배출된 1차 에어로졸과 광화학 반응 등에 의해 가스가 입자로 변환되어 생긴 2차 에어로졸이 존재한다. 2차 에어로졸의 생성과정을 규명하기 위하여 스모그 챔버 연구가 많이 수행되고 있다. 본 연구팀에서도 대기를 실내 스모그 챔버에 도입하여 광화학 반응에 의한 2차 에어로졸의 생성 및 성장과정을 규명하는 실험을 수행하고 있다 (박주연 등, 2002). (중략)

• Journal of Environmental Science International
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• v.14 no.2
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• pp.231-240
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• 2005

The number of cases exceeding environmental standards of atmospheric ozone in the major cities in Korea has steadily increased during the past decades. In order to understand and analyze the atmospheric reactions in the atmosphere, especially the secondary photochemical reactions, smog chambers studies have been performed very actively by many research groups worldwide. However, these studies have focused on the mechanism of photochemical reactions in high concentration conditions, not at the ambient levels. Therefore, in-depth studies in these conditions are essentially needed to realize exact mechanism in the atmosphere near the earth surface, especially at Korean atmospheric conditions. In this experiment, the mechanism of photochemical smog was examined through a comparative experiment of smog chambers under sun light and black light conditions. The results of our study indicated that concentrations of ozone, aldehyde, and PAN increased as the radiation of light source increases. Photochemical reaction patterns can be considered quite similar for both black light and sun light experiments. Based on our experiments using toluene as a reactant which is present at significant high levels in ambient air relative to other VOCs, it was found that toluene could contribute notably to oxidize NO to $NO_2$, this reaction can eventually generate some other photochemical oxidants such as ozone, aldehyde, and PAN. The results of simulation and experiments generally showed a good agreement quite well except for the case of $O_3$. The restriction of oxidization of NO to $NO_2$ seems to cause this difference, which is mainly from the reaction of peroxy radical itself and other reactants in the real gas.

• Journal of Korean Society for Atmospheric Environment
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• v.21 no.1
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• pp.15-26
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• 2005

An experimental investigation of the gas-phase photooxidation of toluene-NO$_{x}$-air mixtures at sub-ppm concentrations has been carried out in a 6.9 m3, indoor smog chamber irradiated by blacklights. Measured parameters in the toluene-NO$_{x}$ experiments included $O_3$, NO, NO$_2$, NO$_{x}$, CO, SO$_2$ toluene, and air temperature. The initial toluene concentration ranged from 225 ppb to 991 ppb and the initial concentration ratio of toluene/NO$_{x}$ in ppbC/ppb was in the range of 5～20. It was found that the variation of gaseous species with irradiation time caused by the photooxidation of toluene-NO$_{x}$-air mixtures depended on the initial toluene concentration for similar concentration ratio of toluene/NO$_{x}$. The dependency of initial toluene concentration on the photooxidation of toluene-NO$_{x}$-air mixtures for toluene/NO$_{x}$=5～6 seemed to be opposite to that for toluene/NO$_{x}$=10～11. The arriving time at maximum ozone concentration depended on both initial toluene concentration and initial concentration ratio of toluene/NO$_{x}$. However, the maximum concentration of ozone formed by photooxidation depended only on the initial toluene concentration.luene concentration.

• Journal of Korean Society for Atmospheric Environment
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• v.21 no.1
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• pp.27-38
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• 2005

An experimental investigation of the gas-phase photooxidation of toluene-NO$_{x}$-air mixtures at sub-ppm concentrations has been carried out in a 6.9 ㎥, indoor smog chamber irradiated by blacklights. Measured parameters in the toluene-NO$_{x}$ experiments included aerosol, $O_3$, NO, NO$_2$, NO$_{x}$ CO, SO$_2$ toluene, and air temperature. The initial toluene concentration ranged from 225 ppb to 991 ppb and the initial concentration ratio of toluene/NO$_{x}$ in ppbC/ppb was in the range of 5～20. It was found that the variation of aerosol number concentration with irradiation time caused by the photooxidation of toluene-NO$_{x}$-air mixtures depended on the initial toluene concentration for similar concentration ratio of toluene/NO$_{x}$. The dependency of initial toluene concentration on the photooxidation of toluene-NO$_{x}$-air mixtures for toluene/NO$_{x}$= 5～6 seemed to be opposite to that for toluene/NO$_{x}$=10～11. The maximum number concentration of aerosols formed by photooxidation and the aerosol yield depended on both initial toluene concentration and initial concentration ratio of toluene/NO$_{x}$. In this study, the aerosol yield, defined as aerosol formed per unit toluene consumed, was found to be 0.01～0.16.und to be 0.01～0.16.

• Proceedings of the Korea Air Pollution Research Association Conference
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• 2003.05b
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• pp.167-168
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• 2003

광화학 스모그는 대기 중으로 배출된 일차 오염물질인 /NO$_{x}$와 휘발성 유기화합물(volatile organic compounds)이 햇빛에 의해 반응하여 오존과 그외 다른 광화학 물질들을(photochemical oxidants) 생성시키는 현상이다. 서울의 경우 이런 VOCs 중에서 가장 많은 양을 차지하는 톨루엔은 광화학 반응을 통해 이차 유기 에어로졸(secondary organic aerosols)을 생성하는 능력이 매우 높은 방향족 화합물이다(Na and Kim, 2001). 지금까지 톨루엔의 이차 유기 에어로졸 생성에 관한 연구와 다른 방향족 탄화수소에 관한 연구가 스모그 챔버 실험을 통해 많이 이루어져 왔다. (중략)

• Proceedings of the Korea Air Pollution Research Association Conference
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• 2003.05b
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• pp.43-44
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• 2003

스모그 챔버는 대기화학 반응을 물리적 변수를 제어할 수 있는 공간 내에서 재현하여 스모그 현상을 체계적으로 규명하기 위해 가장 많이 사용되는 방법이다(Dodge, 2000). 대기화학 반응을 통해 생성된 입자상 물질(secondary particles) 또는 초미세 입자(ultrafine particle, 〈0.1 $\mu\textrm{m}$)는 연속된 물리화학 반응을 통해 accumulation mode(0.1~l.0 $\mu\textrm{m}$) 입자로 성장한다. 특히, 대도시의 시정(visibility)은 accumulation mode 입자의 산란(scattering)과 흡수(adsorption)가 주요한 원인이기 때문에 이러한 물질의 생성에 영향을 주는 가스상 물질의 전화(gas-to-particle conversion) 반응과 초미세 입자의 성장 현상을 규명하는 것은 매우 중요하다. (중략)

• Journal of Korean Society for Atmospheric Environment
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• v.16 no.E
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• pp.1-17
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• 2000

In this study, the concentrations of particulate organic constituents of environmental tobacco smoke(ETS) were determined using an environmental smog chamber, where ETS is the sole source of target compounds. ETS was generated in a 30 ㎥ environmental chamber by a number of different cigarettes, including the Kentucky 1R4F reference cigarette and eight commercial brands. A total of 12 experimental runs was conducted, and target analytes included a group of ETS markers both in vapor and particulate phase and a class of polycylic aromatic hydrocarbos(PAHs) associated with ETS particles. The mass concentrations of PAH in ETS particles were also determined. The average contents of benzo(a) pyrene and benzo(a) anthracene in ETS particles for the commercial brands were 12.8 and 21.5$\mu\textrm{g}$/g, respectively, There values are all somewhat higher than those determined previously by other studies. Results form the chamber study are further used to estimate the average and variability of cigarette yields for target compounds associated with ETS. Finally, ratios of RSP to the surrogate standards of UVPM, FPM and solanesol were calculated for each sample. The average conversion factors factors for the eight commercial brands were 7.3, 38, and 41 for UVPM, EPM, and solanesol, respectively. The UVPM and FPM factors are in good agreement with the recently published values. Whereas there might be a substantial difference in the solanesol content among cigarettes produced in different countries, the variability is somewhat greater than those of UVPM and FPM, Unfortunately, comparison of the PAH yield data from this study with literature values was complicated by a lack of consistency in cigarette smoke generating methodology. Validation of the PAH yields was also difficult due to a lack of information on the ETS related PAH in the literature. From and engineering viewpoint , however, these data on the cigarette yields of ETS components may still provide useful information to studies on the mathematical modeling of indoor air quality management regarding tobacco smoke as a source of interest, or to studies on the assessment of human exposure to ETS.