Meng Zhaoyang, Xie Yulin, Jia Shihui, et al. Characteristics of atmospheric ammonia at gucheng, a rural site on North China Plain in summer of 2013. J Appl Meteor Sci, 2015, 26(2): 141-150. DOI:  10.11898/1001-7313.20150202.
Citation: Meng Zhaoyang, Xie Yulin, Jia Shihui, et al. Characteristics of atmospheric ammonia at gucheng, a rural site on North China Plain in summer of 2013. J Appl Meteor Sci, 2015, 26(2): 141-150. DOI:  10.11898/1001-7313.20150202.

Characteristics of Atmospheric Ammonia at Gucheng, a Rural Site on North China Plain in Summer of 2013

DOI: 10.11898/1001-7313.20150202
  • Received Date: 2014-11-04
  • Rev Recd Date: 2014-12-31
  • Publish Date: 2015-03-31
  • In-situ measurement of ambient ammonia (NH3) and water-soluble ions in PM2.5 is conducted at Gucheng, a rural site, from June to August in 2013. Gucheng is an integrated experiment site on ecological and meteorological observation belonging to Chinese Academy of Meteorological Sciences. This station is influenced by high NH3 emissions from fertilizer use and animal production in surrounding areas. Ammonia and other trace gases are observed by DLT-100 Ammonia Analyzer and a set of commercial instruments during summer of 2013. Hourly concentrations of the water-soluble inorganic ions in PM2.5 are also measured with the Ambient Ion Monitor (URG 9000 Series, USA). Concentrations of NH3 at Gucheng range from 0.9×10-9 to 862.9×10-9, with the average of 43.9×10-9±65.9×10-9. In summer, high temperatures favor ammonia volatilization from fertilizer applied to the cropland. NH3 concentrations increase sharply after fertilizer application in July for summer maize. Mean concentrations of SO2, NOX and O3 are 4.3×10-9±5.5×10-9, 13.2×10-9±6.8×10-9 and 42.4×10-9±31.5×10-9 during the sampling period. The ammonia shows a significant diurnal variation during the sampling period. NH3 concentration maximum occurs at 0900 BT and the minimum at 1900 BT. The sulfate, ammonium and nitrate are dominant ions in PM2.5 with their average concentration being (20.46±13.62), (19.77±33.24) μg·m-3 and (11.34±9.14) μg·m-3, respectively. Ammonium shows significant positive correlations with NH3 concentration. To understand the relationship between particulate ions and their respective precursors, sulfur oxidation ratio (SOR), nitrogen oxidation ratio (NOR) and ammonia conversion ratio (NHR) are investigated. SOR and NOR represent the oxidation ratio of sulfate and nitrate, and NHR represents the conversion ratio of ammonium. Higher SOR and NHR have important effects on the conversion of SO2 to SO42- and NH3 to NH4+. The dependence of inorganic PM2.5 on NH3 levels suggest that controlling NH3 emission from agricultural sources could be an efficient way to reduce secondary inorganic particle pollution on North China Plain.
  • Fig. 1  Correlation of NH3 to NH4+ in PM2.5 in summer of 2013 at Gucheng Station

    Fig. 2  Diurnal variations of NH3, SO2, NOX, NH4+, SO42-, NO3- and meteorological factors in summer of 2013 at Gucheng Station

    Fig. 3  Temporal variations of concentrations of NH3, SO2, NOX, NH4+, SO42-, NO3- and meteorological factors from 7 Aug to 11 Aug in 2013 at Gucheng Station

    Fig. 4  Correlations of [NH4+] to [SO42-], [SO42-]+[NO3-] and [SO42-]+[NO3-]+[Cl-] from 7 Aug to 11 Aug in 2013 at Gucheng Station

    Table  1  Statistics of observed gases and aerosol components from 1 Jun to 31 Aug in 2013 at Gucheng Station

    统计量 气体体积分数/10-9 水溶性离子质量浓度/(μg·m-3)
    NH3 SO2 NOX O3 NH4+ SO42- NO3-
    平均值 43.9 4.3 13.2 42.4 19.77 20.46 11.34
    最大值 862.9 73.0 67.7 149.9 340.60 116.9 109.3
    最小值 0.9 0.1 2.7 1.0 1.07 3.30 1.09
    标准偏差 65.9 5.5 6.8 31.5 33.24 13.62 9.14
    DownLoad: Download CSV

    Table  2  Sulfur oxidation ratio, nitrogen oxidation ratio and ammonia conversion ratio in summer of 2013 at Gucheng Station

    月份 硫氧化率 氮氧化率 氨转化率
    6月 0.66 0.23 0.32
    7月 0.79 0.25 0.30
    8月 0.82 0.22 0.35
    DownLoad: Download CSV

    Table  3  Correlation of sulfur oxidation ratio, nitrogen oxidation ratio and ammonia conversions ratio to meteorological factors in summer of 2013 at Gucheng Station

    气象因子 硫氧化率 氮氧化率 氨转化率
    相对湿度 0.44 0.31 0.39
    气温 -0.29 -0.09 -0.15
    太阳总辐射强度 -0.17 -0.06 -0.23
    DownLoad: Download CSV
  • [1]
    Ni Jiqin, Albert J H, Teng T L, et al.Ammonia Emission from a Large Mechanically-ventilated Swine Building During Warm Weather.Disney's Coronado Springs Resort, Orlando, Florida, 1998. http://www.docin.com/p-526197127.html
    [2]
    Shen Jianlin, Liu Xuejun, Zhang Ying, et al.Atmospheric ammonia and particulate ammonium from agricultural sources in the North China Plain.Atmos Environ, 2011, 45:5033-5041. doi:  10.1016/j.atmosenv.2011.02.031
    [3]
    Cao J J, Zhang T, Chow J C, et al.Characterization of atmospheric ammonia over Xi'an, China.Aerosol and Air Quality Research, 2009, 9:277-289. https://www.researchgate.net/publication/307822442_Characterization_of_Atmospheric_Ammonia_over_Xi'an_China
    [4]
    孟昭阳, 丁国安, 于海青, 等.北京北部城区SO2和NO2浓度垂直分布特点初探.应用气象学报, 2002, 13(增刊Ⅰ):109-112.
    [5]
    孟昭阳, 张怀德, 蒋晓明, 等.太原冬季PM2.5中有机碳和元素碳的变化特征.应用气象学报, 2007, 18(4):524-531. doi:  10.11898/1001-7313.20070413
    [6]
    颜鹏, 刘桂清, 周秀骥, 等.上甸子秋冬季雾霾期间气溶胶光学特性.应用气象学报, 2010, 21(3):257-265. doi:  10.11898/1001-7313.20100301
    [7]
    颜鹏, 郇宁, 张养梅, 等.北京郊区乡村背景地区分粒径大气气溶胶OC及EC分析.应用气象学报, 2012, 23(3):285-293. http://qikan.camscma.cn/jams/ch/reader/view_abstract.aspx?file_no=20120304&flag=1
    [8]
    董文煊, 邢佳, 王书肖.1994—2006年中国人为源大气氨排放时空分布.环境科学, 2010, 31(7):1457-1463. http://www.cnki.com.cn/Article/CJFDTOTAL-HJKZ201007010.htm
    [9]
    Meng Z Y, Lin W L, Jiang X M, et al.Characteristics of atmospheric ammonia over Beijing, China.Atmos Chem Phys, 2011, 11:6139-6151. doi:  10.5194/acp-11-6139-2011
    [10]
    Ianniello A, Spataro F, Esposito G, et al.Occurrence of gas phase ammonia in the area of Beijing (China).Atmos Chem Phys, 2010, 10:9487-9503. doi:  10.5194/acp-10-9487-2010
    [11]
    Meng Z Y, Xu X B, Wang T, et al.Ambient sulfur dioxide, nitrogen dioxide, and ammonia at ten background and rural sites in China during 2007-2008.Atmos Environ, 2010, 44:2625-2631. doi:  10.1016/j.atmosenv.2010.04.008
    [12]
    Lin Weili, Xu Xiaobin, Ge Baozhu, et al.Characteristics of gaseous pollutants at Gucheng, a rural site southwest of Beijing.J Geophys Res, 2009, 114, D00G14, doi: 10.1029/2008JD010339.
    [13]
    刘希文, 徐晓斌, 林伟立.北京及周边地区典型站点近地面O3的变化特征.中国环境科学, 2010, 30(7):328-332. http://mall.cnki.net/magazine/Article/ZGHJ201007017.htm
    [14]
    任三学, 赵花荣, 姜朝阳, 等.土壤水分胁迫对冬小麦旗叶光合特性的影响.气象科技, 2010, 38(1):114-119. http://www.cnki.com.cn/Article/CJFDTOTAL-QXKJ201001023.htm
    [15]
    李阳, 徐晓斌, 林伟立, 等.基于观测的污染气体区域排放特征.应用气象学报, 2012, 23(1):10-19. http://qikan.camscma.cn/jams/ch/reader/view_abstract.aspx?file_no=20120102&flag=1
    [16]
    王静, 高晓梅, 寿幼平, 等.济南春季大气PM2.5水溶性组分的半连续在线观测.中国环境科学, 2010, 30(1):18-24.
    [17]
    Zhu T, Pattey E, Desjardins R L.Relaxed eddy-accumulation technique for measuring ammonia volatilization.Environmental Science & Technology, 2000, 34(1):199-203.
    [18]
    孟昭阳, 贾小芳, 张仁健, 等.2010年长江三角洲临安区域本底站PM2.5理化特征.应用气象学报, 2012, 23(4):424-432. doi:  10.11898/1001-7313.20120405
    [19]
    Walker J T, Whitall D R, Robarge W, et al.Ambient ammonia and ammonium aerosol across a region of variable ammonia emission density.Atmos Environ, 2004, 38(9):1235-1246. doi:  10.1016/j.atmosenv.2003.11.027
    [20]
    McCulloch R B, Few G S, Murray J G C, et al.Analysis of ammonia, ammonium aerosols and acid gases in the atmosphere at a commercial hog farm in eastern North Carolina, USA.Environmental Pollution, 1998, 102(1):263-268. doi:  10.1016/S0269-7491(98)80042-0
    [21]
    Hu Guoyuan, Zhang Yangmei, Sun Junying, et al.Variability, formation and acidity of water-soluble ions in PM2.5 in Beijing based on the semi-continuous observation.Atmos Res, 2014, 145-146:1-11. doi:  10.1016/j.atmosres.2014.03.014
    [22]
    唐孝炎, 张远航, 邵敏.大气环境化学 (第二版).北京:高等教育出版社, 2006:268-351.
    [23]
    杨起超, 曾立民, 唐静玥, 等.无锡冬季和春季大气中细粒子化学组分及其特性分析.环境化学, 2014, 33(9):1501-1513. doi:  10.7524/j.issn.0254-6108.2014.09.002
    [24]
    张婷, 曹军骥, 吴枫, 等.西安春夏季气体及PM2.5中水溶性组分的污染特征.中国科学院研究生院学报, 2007, 24(5):643-646. http://www.ir.xjtu.edu.cn/item/142191
    [25]
    Nemitz E, Sutton M A, Choularton T W, et al.Modelling the concentration and profiles of size and composition distributed NH4+ aerosol as modified by the NH3-HNO3-NH4NO3 equilibrium.J Aerosol Sci, 1997, 28:S387-S388. doi:  10.1016/S0021-8502(97)85193-2
    [26]
    Pierson W R, Brachaczek W W, Mckee D E.Sulfate emissions from catalyst equipped automobiles on the high way.Journal of Air Pollution Control Association, 1979, 29:255-257. doi:  10.1080/00022470.1979.10470790
    [27]
    Truex T J, Pierson W R, Mckee D E.Sulfate in diesel exhaust.Environ Sci Technol, 1980, 14:1118-1121. doi:  10.1021/es60169a013
    [28]
    McMurry P H, Wilson J C.Droplet phase (heterogeneous) and gas phase (homogeneous) contributions to secondary ambient aerosol formation as functions of relative humidity.J Geophys Res, 1983, 88:5101-5108. doi:  10.1029/JC088iC09p05101
    [29]
    赵鹏, 朱彤, 梁宝生, 等.北京郊区农田夏季大气颗粒物质量和离子成分谱分布特征.环境科学, 2006, 27(2):193-199. http://www.cnki.com.cn/Article/CJFDTOTAL-HJKZ200602000.htm
    [30]
    胡敏, 赵云良, 何凌燕, 等.北京冬、夏季颗粒物及其离子成分质量浓度谱分布.环境科学, 2005, 26(4):1-6. http://www.cnki.com.cn/Article/CJFDTOTAL-HJKZ200504001.htm
    [31]
    程萌田, 潘月鹏, 王辉, 等.大气PM2.5中水溶性离子在线观测技术的应用研究.环境科学, 2013, 34(8):2943-2949. http://mall.cnki.net/magazine/Article/HJKZ201308002.htm
  • 加载中
  • -->

Catalog

    Figures(4)  / Tables(3)

    Article views (3841) PDF downloads(1137) Cited by()
    • Received : 2014-11-04
    • Accepted : 2014-12-31
    • Published : 2015-03-31

    /

    DownLoad:  Full-Size Img  PowerPoint