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Interference of Sulphur Dioxide on Balloon-borne Electrochemical Concentration Cell Ozone Sensors over the Mexico City Metropolitan Area
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  • Interference of Sulphur Dioxide on Balloon-borne Electrochemical Concentration Cell Ozone Sensors over the Mexico City Metropolitan Area
  • Interference of Sulphur Dioxide on Balloon-borne Electrochemical Concentration Cell Ozone Sensors over the Mexico City Metropolitan Area
저자명
Kanda. Isao,Basaldud. Roberto,Horikoshi. Nobuji,Okazaki. Yukiyo,Benitez-Garcia. Sandy-Edith,Ortinez. Abraham,Benitez. Victor Ram
간행물명
Asian journal of atmospheric environment
권/호정보
2014년|8권 3호|pp.162-174 (13 pages)
발행정보
한국대기환경학회
파일정보
정기간행물|ENG|
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기타
이 논문은 한국과학기술정보연구원과 논문 연계를 통해 무료로 제공되는 원문입니다.
서지반출

기타언어초록

An abnormal decrease in ozonesonde sensor signal occurred during air-pollution study campaigns in November 2011 and March 2012 in Mexico City Metropolitan Area (MCMA). Sharp drops in sensor signal around 5 km above sea level and above were observed in November 2011, and a reduction of signal over a broad range of altitude was observed in the convective boundary layer in March 2012. Circumstantial evidence indicated that $SO_2$ gas interfered with the electrochemical concentration cell (ECC) ozone sensors in the ozonesonde and that this interference was the cause of the reduced sensor signal output. The sharp drops in November 2011 were attributed to the $SO_2$ plume from Popocat$acute{e}$petl volcano southeast of MCMA. Experiments on the response of the ECC sensor to representative atmospheric trace gases showed that only $SO_2$ could cause the observed abrupt drops in sensor signal. The vertical profile of the plume reproduced by a Lagrangian particle diffusion simulation supported this finding. A near-ground reduction in the sensor signal in March 2012 was attributed to an $SO_2$ plume from the Tula industrial complex north-west of MCMA. Before and at the time of ozonesonde launch, intermittent high $SO_2$ concentrations were recorded at ground-level monitoring stations north of MCMA. The difference between the $O_3$ concentration measured by the ozonesonde and that recorded by a UV-based $O_3$ monitor was consistent with the $SO_2$ concentration recorded by a UV-based monitor on the ground. The vertical profiles of the plumes estimated by Lagrangian particle diffusion simulation agreed fairly well with the observed profile. Statistical analysis of the wind field in MCMA revealed that the effect Popocat$acute{e}$petl was most likely to have occurred from June to October, whereas the effect of the industries north of MCMA, including the Tula complex, was predicted to occur throughout the year.