Atmospheric mercury monitoring survey in Beijing, China
With the aid of one industrial, two urban, two suburban, and two rural sampling locations, diurnal patterns of total gaseous mercury (TGM) were monitored in January, February and September of 1998 in Beijing, China. Monitoring was conducted in six (two urban, two suburban, one rural and the industri...
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Published in | Chemosphere (Oxford) Vol. 48; no. 1; pp. 97 - 107 |
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Main Authors | , , , , , , |
Format | Journal Article |
Language | English |
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Oxford
Elsevier Ltd
01.07.2002
Elsevier |
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Abstract | With the aid of one industrial, two urban, two suburban, and two rural sampling locations, diurnal patterns of total gaseous mercury (TGM) were monitored in January, February and September of 1998 in Beijing, China. Monitoring was conducted in six (two urban, two suburban, one rural and the industrial sites) of the seven sampling sites during January and February (winter) and in four (two urban, one rural, and the industrial sites) of the sampling locations during September (summer) of 1998. In the three suburban sampling stations, mean TGM concentrations during the winter sampling period were 8.6, 10.7, and 6.2 ng/m
3, respectively. In the two urban sampling locations mean TGM concentrations during winter and summer sampling periods were 24.7, 8.3, 10, and 12.7 ng/m
3, respectively. In the suburban-industrial and the two rural sampling locations, mean mercury concentrations ranged from 3.1–5.3 ng/m
3 in winter to 4.1–7.7 ng/m
3 in summer sampling periods. In the Tiananmen Square (urban), and Shijingshan (suburban) sampling locations the mean TGM concentrations during the summer sampling period were higher than winter concentrations, which may have been caused by evaporation of soil-bound mercury in warm periods. Continuous meteorological data were available at one of the suburban sites, which allowed the observation of mercury concentration variations associated with some weather parameters. It was found that there was a moderate negative correlation between the wind speed and the TGM concentration at this suburban sampling location. It was also found that during the sampling period at the same site, the quantity of TGM transported to or from the sampling site was mainly influenced by the duration and frequency of wind occurrence from certain directions. |
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AbstractList | With the aid of one industrial, two urban, two suburban, and two rural sampling locations, diurnal patterns of total gaseous mercury (TGM) were monitored in January, February and September of 1998 in Beijing, China. Monitoring was conducted in six (two urban, two suburban, one rural and the industrial sites) of the seven sampling sites during January and February (winter) and in four (two urban, one rural, and the industrial sites) of the sampling locations during September (summer) of 1998. In the three suburban sampling stations, mean TGM concentrations during the winter sampling period were 8.6, 10.7, and 6.2 ng/m super(3), respectively. In the two urban sampling locations mean TGM concentrations during winter and summer sampling periods were 24.7, 8.3, 10, and 12.7 ng/m super(3), respectively. In the suburban-industrial and the two rural sampling locations, mean mercury concentrations ranged from 3.1-5.3 ng/m super(3) in winter to 4.1-7.7 ng/m super(3) in summer sampling periods. In the Tiananmen Square (urban), and Shijingshan (suburban) sampling locations the mean TGM concentrations during the summer sampling period were higher than winter concentrations, which may have been caused by evaporation of soil-bound mercury in warm periods. Continuous meteorological data were available at one of the suburban sites, which allowed the observation of mercury concentration variations associated with some weather parameters. It was found that there was a moderate negative correlation between the wind speed and the TGM concentration at this suburban sampling location. It was also found that during the sampling period at the same site, the quantity of TGM transported to or from the sampling site was mainly influenced by the duration and frequency of wind occurrence from certain directions. Ambient atmospheric mercury concentrations were measured at a number of locations in Beijing, China, in 1998. During each short-term monitoring period, which comprised summer and winter periods, wind direction was determined. High gaseous Hg concentrations were measured in the urban areas during both day and night in both sampling seasons. The highest concentrations, however, were found in an urban residential sector during winter, which implicated the use of coal. At Xuanwu and Tiananmen Square, background total gaseous Hg levels were higher in summer than in winter, suggesting evaporation of soil-bound Hg. All relevant Hg concentration data are tabulated. With the aid of one industrial, two urban, two suburban, and two rural sampling locations, diurnal patterns of total gaseous mercury (TGM) were monitored in January, February and September of 1998 in Beijing, China. Monitoring was conducted in six (two urban, two suburban, one rural and the industrial sites) of the seven sampling sites during January and February (winter) and in four (two urban, one rural, and the industrial sites) of the sampling locations during September (summer) of 1998. In the three suburban sampling stations, mean TGM concentrations during the winter sampling period were 8.6, 10.7, and 6.2 ng/m 3, respectively. In the two urban sampling locations mean TGM concentrations during winter and summer sampling periods were 24.7, 8.3, 10, and 12.7 ng/m 3, respectively. In the suburban-industrial and the two rural sampling locations, mean mercury concentrations ranged from 3.1–5.3 ng/m 3 in winter to 4.1–7.7 ng/m 3 in summer sampling periods. In the Tiananmen Square (urban), and Shijingshan (suburban) sampling locations the mean TGM concentrations during the summer sampling period were higher than winter concentrations, which may have been caused by evaporation of soil-bound mercury in warm periods. Continuous meteorological data were available at one of the suburban sites, which allowed the observation of mercury concentration variations associated with some weather parameters. It was found that there was a moderate negative correlation between the wind speed and the TGM concentration at this suburban sampling location. It was also found that during the sampling period at the same site, the quantity of TGM transported to or from the sampling site was mainly influenced by the duration and frequency of wind occurrence from certain directions. With the aid of one industrial, two urban, two suburban, and two rural sampling locations, diurnal patterns of total gaseous mercury (TGM) were monitored in January, February and September of 1998 in Beijing, China. Monitoring was conducted in six (two urban, two suburban, one rural and the industrial sites) of the seven sampling sites during January and February (winter) and in four (two urban, one rural, and the industrial sites) of the sampling locations during September (summer) of 1998. In the three suburban sampling stations, mean TGM concentrations during the winter sampling period were 8.6, 10.7, and 6.2 ng/m3, respectively. In the two urban sampling locations mean TGM concentrations during winter and summer sampling periods were 24.7, 8.3, 10, and 12.7 ng/m3, respectively. In the suburban-industrial and the two rural sampling locations, mean mercury concentrations ranged from 3.1-5.3 ng/m3 in winter to 4.1-7.7 ng/m3 in summer sampling periods. In the Tiananmen Square (urban), and Shijingshan (suburban) sampling locations the mean TGM concentrations during the summer sampling period were higher than winter concentrations, which may have been caused by evaporation of soil-bound mercury in warm periods. Continuous meteorological data were available at one of the suburban sites, which allowed the observation of mercury concentration variations associated with some weather parameters. It was found that there was a moderate negative correlation between the wind speed and the TGM concentration at this suburban sampling location. It was also found that during the sampling period at the same site, the quantity of TGM transported to or from the sampling site was mainly influenced by the duration and frequency of wind occurrence from certain directions. |
Author | Nadim, Farhad Chen, Letian Hoag, George E. Perkins, Chris Liu, Shili Carley, Robert J. Lin, Yuhan |
Author_xml | – sequence: 1 givenname: Shili surname: Liu fullname: Liu, Shili email: sliu@aqua.eri.uconn.edu organization: The Environmental Research Institute, University of Connecticut, Longley Building, Box Unit 5210, 270 Middle Turnpike (Route. 44), Storrs, CT 06269-3210, USA – sequence: 2 givenname: Farhad surname: Nadim fullname: Nadim, Farhad email: fnadim@aqua.eri.uconn.edu organization: The Environmental Research Institute, University of Connecticut, Longley Building, Box Unit 5210, 270 Middle Turnpike (Route. 44), Storrs, CT 06269-3210, USA – sequence: 3 givenname: Chris surname: Perkins fullname: Perkins, Chris email: cperkins@aqua.eri.uconn.edu organization: The Environmental Research Institute, University of Connecticut, Longley Building, Box Unit 5210, 270 Middle Turnpike (Route. 44), Storrs, CT 06269-3210, USA – sequence: 4 givenname: Robert J. surname: Carley fullname: Carley, Robert J. email: rcarley@aqua.eri.uconn.edu organization: The Environmental Research Institute, University of Connecticut, Longley Building, Box Unit 5210, 270 Middle Turnpike (Route. 44), Storrs, CT 06269-3210, USA – sequence: 5 givenname: George E. surname: Hoag fullname: Hoag, George E. email: ghoag@aqua.eri.uconn.edu organization: The Environmental Research Institute, University of Connecticut, Longley Building, Box Unit 5210, 270 Middle Turnpike (Route. 44), Storrs, CT 06269-3210, USA – sequence: 6 givenname: Yuhan surname: Lin fullname: Lin, Yuhan organization: Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Academia Sinica, 18 Shuang Quing Road, Haidian P.O. Box 2871, Beijing 100085, China – sequence: 7 givenname: Letian surname: Chen fullname: Chen, Letian organization: Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Academia Sinica, 18 Shuang Quing Road, Haidian P.O. Box 2871, Beijing 100085, China |
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Keywords | Beijing Rural Urban Atmospheric mercury China Atmospheric condition Air content Air quality Urban area Diurnal variation Spatial variation Time variation Heavy metal Surveillance Correlation analysis Seasonal variation Rural area Air pollution Suburban zone Industrial area Sampling Mercury |
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Snippet | With the aid of one industrial, two urban, two suburban, and two rural sampling locations, diurnal patterns of total gaseous mercury (TGM) were monitored in... Ambient atmospheric mercury concentrations were measured at a number of locations in Beijing, China, in 1998. During each short-term monitoring period, which... |
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SubjectTerms | Air Pollutants - analysis Applied sciences Atmospheric mercury Atmospheric pollution Beijing China Cities Environmental Monitoring Exact sciences and technology Industry Mercury - analysis Pollution Pollution sources. Measurement results Reproducibility of Results Rural Seasons Urban Wind |
Title | Atmospheric mercury monitoring survey in Beijing, China |
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