南京大学学报(自然科学版) ›› 2015, Vol. 51 ›› Issue (3): 499–.

• • 上一篇    下一篇

浙江省城市大气污染特性研究

毛敏娟1*,孟燕军2 ,齐 冰3   

  • 出版日期:2015-04-23 发布日期:2015-04-23
  • 作者简介:(1. 浙江省气象科学研究所,杭州,310008;2. 中国气象局北京城市气象研究所,北京,100089;
    3. 浙江省杭州市气象局,杭州,310008)
  • 基金资助:
    国家自然科学基金面上项目(41475134),浙江省公益性社会发展重点项目(2014C23004),国家科技支撑计划课题(2014BAC16B05)

The research of air pollution characteristics in urban area over Zhejiang

Mao Minjuan1*, Meng Yanjun2, Qi Bing3   

  • Online:2015-04-23 Published:2015-04-23
  • About author:(1. Zhejiang Institute of Meteorology Science, Hangzhou 310008China; 2. Beijing Research Institute of Meteorological Science, Beijing 100089, China; 3. Meteorological Bureau of Hangzhou, Hangzhou 310008China)

摘要: 本文以浙江省城市(主要指杭州)为研究区域,利用大气成分观测数据,通过对比、相关分析研究了浙江省城市的大气污染特性。研究结果表明,2011-2013年间,杭州PM2.5和NO2月均质量浓度均呈上升趋势,增幅皆为10 ?g.m-3左右,PM10和SO2则呈下降趋势,PM10降幅微弱,SO2降幅为8 ?g.m-3左右。PM1、PM2.5、PM10质量浓度与大气消光系数之间相关系数为0.73、0.83和0.74,其中粒径为0.25-1.0 ?m的粒子对大气消光系数的贡献率最大,达到66.4%, 1.0-2.5 ?m粒子为23.2%,大于2.5 ?m 的粗粒子仅为10.4%。与临安相比,杭州NO2日均浓度超标日数多了50天左右。杭州大气气溶胶中占主导地位的无机水溶性离子依次为NO3-、NH4+和SO42-,它们占到总水溶性离子浓度的52.66-96.61%,与北京、广州等地区SO42- > NO3-的研究结果明显不同。NO3-、NH4+浓度季节变化特点与NO2相似,而且NO3-和NH4+具有较好的相关性,SO42-与SO2浓度季节变化特点则不同。受夏季主导风向的影响,这一季节Na+和Cl-浓度最高,而秋季明显偏高的K+浓度是长三角秋季秸秆焚烧现象的指示。

Abstract: Based on observations data of atmospheric compositions, the characteristics of air pollution were investigated in urban area (mainly focus on Hangzhou) over Zhejiang province through the comparison and correlation analysis. The results showed that the increasing trends of the monthly average mass concentrations of PM2.5 and NO2 with 10 ?m.m-3 amplitude and the decreasing trends of PM10 and SO2 with drop slightly and 8 ?m.m-3 were present in Hangzhou from 2011 to 2013. The average correlation coefficients were 0.73, 0.83 and 0.74 between atmospheric extinction and mass concentration of PM1, PM2.5 as well as PM10, respectively. The contributions of 0.25-1.0 ?m and 1.0-2.5 ?m particles on atmospheric extinction were 66.4% and 23.2%, respectively, and larger than 0.25 ?m particles only 10.4%. Compared with Lin’an, the above-norm days of daily average concentration of NO2 was over 50, which is the important reason of heavier haze pollution in Hangzhou. The results also showed that NO3-, NH4+, and SO42- were the dominant water-soluble fractions in PM2.5, accounting for 52.66-96.61% of the total water-soluble ion concentration in , and present NO3- > NH4+ > SO42- descending order, which was different from the condition of Beijing and Guangzhou with SO42- > NO3-. In addition, NO3- and NH4+ present the same seasonal variations of NO2 and good correlation each other, but SO42- was different to the seasonal variations of SO2. The highest concentrations of Na+ and Cl- were found in summer because dominant wind direction Marine aerosol to inland transportation, and the highest concentration of K+ was found in autumn which is a good indicator of straw burning in Yangtze River delta.

[1] 胡建林, 张远航. 长江三角洲地区臭氧生成过程分析. 环境科学研究, 2005, 18(2): 13~18.
[2] 张远航.大气复合污染是灰霾诱因.环境, 2008 (7): 32~33.
[3] 傅家谟.二次气溶胶对灰霾贡献大.环境, 2008 (7): 28~29.
[4] 韩素芹,冯银厂,边 海. 天津大气污染物日变化特征的WRF-Chem数值模拟. 中国环境科学, 2008, 28(9): 828~832.
[5] Wiedensohler A, Cheng Y F, Nowak A, et al. Rapid aerosol particle growth and increase of cloud condensation nucleus activity by secondary aerosol formation and condensation: A case study for regional air pollution in northeastern china. Journal of Geophysical Research, 2009, 114, D00G08, Doi:10.1029/2008jd010884.
[6] 朱 彤,尚 静,赵德峰.大气复合污染及灰霾形成中非均相化学过程的作用.中国科学:化学,2010, 40(12): 1731~1740.
[7] 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.
[8] 牛红亚,邵龙义,刘君霞等.北京灰霾天气PM_(10)中微量元素的分布特征.中国环境监测,2011, 27(1):72~74.
[9] Chen Y, Zhao C, Zhang Q, et al. Aircraft study of mountain chimney effect of Beijing, china. Journal of Geophysical Research, 2009, 114, D08306, doi:10.1029/2008jd010610.
[10] Liu P F, Zhao C S, Gobel T, et al. Hygroscopic properties of aerosol particles at high relative humidity and their diurnal variations in the North China Plain. Atmospheric Chemistry and Physics, 2011, 11: 3479~3494.
[11] Ran L, Zhao C S, Xu W Y, et al. VOC reactivity and its effect on ozone production during the HaChi summer campaign. Atmospheric Chemistry and Physics, 2011, 11: 4657~4667.
[12] Xu W Y, Zhao C S, Ran L, et al. Characteristics of pollutants and their correlation to meteorological conditions at a suburban site in the North China Plain. Atmospheric Chemistry and Physics, 2011, 11: 7113–7154, doi:10.5194/acpd-11-7113-2011.
[13] Deng Z Z, Zhao C S, Ma N, et al. Size-resolved and bulk activation properties of aerosols in the North China plain: the importance of aerosol size distribution in the prediction of CCN number concentration. Atmospheric Chemistry and Physics, 2011, 11: 3835~3846.
[14] 王跃思.减轻雾霾不能光靠政府. http://special.caixin.com/2013-12-16/100617731.html, 2013-12-16.
[15] 吴 兑,毛节泰,邓雪娇等.珠江三角洲黑碳气溶胶及其辐射特性的观测研究.中国科学(D辑):地球科学,2009, 39(11): 1542~1553.
[16] 谭浩波,吴 兑,邓雪娇等.珠江三角洲气溶胶光学厚度的观测研究.环境科学学报,2009, 29(6): 1146~1155.
[17] Wang Y, Zhuang G S, Zhang X Y, et al. The ion chemistry, seasonal cycle, and sources of PM2.5 and TSP aerosol in Shanghai. Atmospheric Environment, 2006, 40: 2935~2952.
[18] 唐文苑,赵春生,耿福海等.上海地区臭氧周末效应研究.中国科学(D辑):地球科学,2009, 39(1): 99~105.
[19] 范新强,孙照渤. 1953-2008年厦门地区的灰霾天气特征.大气科学学报,2009, 32(5): 604~609.
[20] 范雪波,吴伟伟,王广华等. 上海市灰霾天大气颗粒物浓度及富集元素的粒径分布.科学通报,2010, 55(13): 1221~1226.
[21] 潘 鹄,耿福海,陈勇航等.利用微脉冲激光雷达分析上海地区一次灰霾过程.环境科学学报,2010, 30(11): 2164~2173.
[22] 杨卫芬,银 燕,魏玉香等. 霾天气下南京PM2.5中金属元素污染特征及来源分析. 中国环境科学,2010, 30(1): 12~17.
[23] 毛敏娟,刘厚通,徐宏辉等. 多元观测资料融合应用的灰霾天气关键成因研究. 环境科学学报,2013, 33(3):806~813.
[24] 张 浩,石春娥,邱明燕等. 合肥市霾天气变化特征及其影响因子. 环境科学学报,2010, 30(4): 714~721.
[25] White W H, Roberts P T. On the nature and origins of visibility reducing aerosols in the Los Angeles air basin. Atmospheric Environment, 1977, 11: 803~812.
[26] Malm W C. Characteristics and origins of haze in the continental United States. Earth Science Reviews, 1992, 33 (1): 1~36.
[27] Watson J G. Visibility: Science and regulation. Journal of the Air & Waste Management Association, 2002, 52: 628~713.
[28] Schichtel B A,Barna M G,Gebhart K A, et al. Evaluation of a Eulerian and Lagrangian air quality model using perfluorocarbon tracers released in Texas for the BRAVO haze study. Atmospheric Environment, 2005, 39: 7044~7062.
[29] Tie X X, Brasseur G P, Zhao C S, et al. Chemical characterization of air pollution in eastern China and the eastern United States. Atmospheric Environment, 2006, 40: 2607~2625.
[30] Morris R E,Koo B Y,Guenther A, et al. Model sensitivity evaluation for organic carbon using two multi-pollutant air quality models that simulate regional haze in the southeastern United States. Atmospheric Environment, 2006, 40: 4960~4972.
[31] Park R J,Jacob D J,Kumar N, et al. Regional visibility statistics in the United States: Natural and transboundary pollution influences, and implications for the Regional Haze Rule. Atmospheric Environment, 2006, 40: 5405~5423.
[32] Anttila T. Sensitivity of cloud droplet formation to the numerical treatment of the particle mixing state. Journal of Geophysical Research, 2010, 115, D21205, doi:10.1029/2010jd013995.
[33] National Research Council. Rethinking the Ozone Problem in Urban and Regional Air Pollution. Washington, DC: National Academy Press, 1991.
[34] Odman M T,Hu Y T,Russell A G, et al. Quantifying the sources of ozone, fine particulate matter, and regional haze in the Southeastern United States. Journal of Environmental Management, 2009, 90: 3155~3168.
[35] 赵普生,张小玲,孟 伟等. 京津冀区域气溶胶中无机水溶性离子污染特征分析. 环境科学,2011,32(6): 1546~1549.
[36] 薛立杰,苏领彦,吴少伟等. 北京市大气PM2.5中四种水溶性阴离子的水平变化比较. 生态环境学报, 2011,20(8-9) : 1315~1319.
[37] 陶 俊,张仁健,董 林等. 夏季广州城区细颗粒物PM2.5和PM10中水溶性无机离子特征. 环境科学,2010,31(7): 1417~1424.
No related articles found!
Viewed
Full text


Abstract

Cited

  Shared   
  Discussed   
No Suggested Reading articles found!