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Student : Shen-Feng Chang Advisor : Yi-Chyun Hsu Atmospheric Environment 43 (2009) 584–593 journal homepage: www.elsevier.com/locate/atmosenv Aircraft measurements of O 3, NO x, CO, VOCs, and SO 2 in the Yangtze River Delta region
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Introduction Description of the measurements Analysis of the result
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The Yangtze River Delta (YRD) region located in east China (with longitude from 120°E to 121°E, and latitude from 30.5°N to 31.5°N) is highly urbanized with a cluster of large cities (including Shanghai, Hangzhou, Shuzhou, Wuxi, etc.). Among these large cities, Shanghai has the highest population in China (about 20 millions). During the past 20 years, this region is undergoing a rapid increase in economical development. Introduction (1/3)
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The GDP has increased by 500% from 1996 to 2006, accounting for more than 5% of the total GDP in China. The rapid urbanization causes wide-ranging potential consequences for weather and climate related to urban environments, such as air pollutions. Like other large cities in east China, Shanghai is suffering severe air pollution problems, such as high particular matter (PM) concentrations and poor visibility. Introduction (2/3)
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Introduction (3/3) As industrial activities and the number of automobiles increase together with the changes in natural activities (such as vegetation and forest), emission of VOCs and NO x will significantly increase in the YRD region. Both VOCs and NOx play critical roles during O 3 formation in the troposphere. Several studies regarding the air quality in the YRD region have been conducted.
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Description of the measurements (1/2) Fig. 1 displays the horizontal routes for several representative flights. It shows that the flight routes are located in west side of the megacity (Shanghai) with several large cities, such as Suzhou, Wuxi and Jiading. In addition, there are several large power plants in this region. For example, the Changshou power plant generates 1200MW per year.
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Description of the measurements (2/2) There are totally five flights between September/30 and October/11 (flight-1 on September/30, flight-2 on October/2, flight-3 on October/5, flight-4 on October/9, and flight-5 on October/11), which are analyzed in this study. There are also several inter-state high ways, and high density of small towns and villages. As a result, the local emissions of air pollutants from automobiles, and area and point sources are intensive.
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Analysis of the result (1/2) Both the O 3 mean values are generally lower than the US national standard values (84 ppbv), suggesting that the O 3 values are modest in the YRD region. The NO x concentrations have large variability, ranging from 3 to 40 ppbv. The highest concentrations of NO x are observed normally in the NCITY case, ranging from 10 to 40 ppbv.
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Analysis of the result (2/2) The SO 2 concentrations also have a large variability, ranging from 1 to 35 ppbv. The highest concentrations of SO 2 are measured in the NCITY case, ranging from 7 to 35 ppbv. The CO concentrations are relatively high, and have smaller variability compared to NO x and SO 2, ranging from 3 to 7 ppmv.
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The results are summarized in the follows: (1) The measured O 3 concentrations range from 20 to 60 ppbv. These values are normally below the US national standard (84 ppbv), suggesting that at the present, the O 3 pollutions are modest in this region. The NO x concentrations have a large variability, ranging from 3 to 40 ppbv. The SO 2 concentrations have very large variability, ranging from 1 to 35 ppbv.
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The CO concentrations are relatively high, and have less variability, ranging from 3 to 7 ppmv. The concentrations of VOCs are relatively small, with the total VOC concentration of 6 ppbv. Among the total VOCs, alkanes have highest values (2.8 ppbv). (2) The relatively small VOC concentrations and large NO x concentrations indicate that the O 3 chemical formation is under “VOC-limited” regime in the YRD region.
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The measured O 3 and NO x concentrations are strongly anti-correlated, suggesting that enhancements in NO x concentrations lead to decrease in O 3 concentrations. (3) The O 3 concentrations are more sensitive to NO x concentrations in the rural PBL region than in the city region. This result suggests that changes in NO x emissions could have strong effects on O 3 concentrations in rural areas of the YRD region.
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(4) The O 3 -isopleth diagram study shows that the O 3 concentrations could increase rapidly with increase in VOC concentrations in the YRD region. For example, if the VOC concentrations increase to 75 ppbC in the future, O 3 concentrations could exceed to 84 ppbv, which is normally considered as the national standard for human’s health.
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Thank you for your attention!
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