欢迎登录材料期刊网

材料期刊网

高级检索

为研究国家大气背景点颗粒物质量浓度与水溶性离子组成特征,于2013年2月、7月、9月、12月分别对4个国家大气背景点进行了PM2.5及PM10的采样,通过超声萃取?IC法测定了样品中的9种水溶性离子(F-、Cl-、NO-3、SO2-4、Na+、NH+4、K+、Mg2+、Ca2+)质量浓度,结果表明:(1)可吸入颗粒物浓度水平一、二季度重于三、四季度,PM2.5、PM10年均值分别为17μg·m-3、32μg·m-3,与其他主要国家和地区背景区域浓度相当,背景点大气状况良好;(2)PM2.5中水溶性离子比重全年波动不大,为35.5%—42.2%,浓度排序为SO2-4、NH+4、NO-3> Ca2+、Cl-、K+、Na+>F-、Mg2+,第一季度PM10中Ca2+浓度显著升高,控制风沙尘将有效降低PM10的浓度;PM2.5及PM10中的9种水溶性离子在不同季节的浓度分布规律与颗粒物浓度类似,一季度较高,三、四季度较低;(3)二次离子是背景点区域的主要水溶性离子,浓度值与其他主要国家和地区相当.NO-3、SO2-4的物质的量浓度与NH+4存在显著相关性,相关系数r为0.7539,斜率小于1,水溶性离子中酸性离子的量比铵根离子略占优势,对气溶胶酸度产生重要贡献.

To investigate the mass concentratation of fine particles and component characteristic of water?soluble ions in National Atmospheric Background, PM2.5 and PM10 samples were collected at 4 sites in four seasons of 2013. The mass concentrations of nine inorganic water?soluble ions were analyzed by ion chromatograph ( IC ) . The results show that the mass concentrations of inhalable particles were higher in the first season than those in the third and fourth seasons. The average annual value of PM2.5 and PM10 was 17μg·m-3 and 32μg·m-3, respectively, which are comparable to those in other major regions and countries. All of above results indicate that the atmospheric quality is good. Second, the contents of the water soluble ions wrer PM2.5 were between 35. 5%—42?2%. The concentration order of these ions is SO2-4 ,NH+4 ,NO-3>Ca2+,Cl-,K+,Na+>F-,Mg2+. The concentration of Ca2+in PM10 was higher in the first season, which indicates that controlling the dust concentration is of great importance to decrease the concentration of PM10. The concentration characteristic of the nine water soluble ions in PM2.5 and PM10 in different seasons is similar to that of fine particles, higher in the first season and lowers in the third and fourth seasons. Third, the secondary ions are the main water soluble ions in the background, whose concentrations are comparable to those in other major regions and countries. The concentrations of NO-3 and SO2-4 are obviously related to that of NH+4 , with the correlation coefficient ( r) of 0.754 and the slope less than 1, which shows the acidic ions are dominant in water soluable ions and affects a lot on the acidity of the aerosol.

参考文献

[1] Guojie Xu;Yuan Gao;Qi Lin;Wei Li;Liqi Chen .Characteristics of water-soluble inorganic and organic ions in aerosols over the Southern Ocean and coastal East Antarctica during austral summer[J].Journal of Geophysical Research, D. Atmospheres: JGR,2013(23):13303-13318.
[2] Yin L Q;Niu Z C;Chen X Q .Characteristics of water-soluble inorganic ions in PM2.5 and PM2.5-10 in the coastal urban agglomeration along the Western Taiwan Strait Region[J].China Environ Sci Pollut Res,2014,21:5141-5156.
[3] 孙韧,张文具,董海燕,边玮瓅,陈魁.天津市PM10和PM2.5中水溶性离子化学特征及来源分析[J].中国环境监测,2014(02):145-150.
[4] 高晓梅,王韬,周杨,薛丽坤,张庆竹,王新锋,聂玮,王文兴,王德众.泰山春、夏两季大气颗粒物及其水溶性无机离子的粒径分布特征[J].环境化学,2011(03):686-692.
[5] 赵金平,张福旺,徐亚,陈进生.滨海城市不同粒径大气颗粒物中水溶性离子的分布特征[J].生态环境学报,2010(02):300-306.
[6] 杨勇杰,刘俊卿,狄一安,于跃,周瑞,徐薇,卜晓辉,马志强,李玉武,任立军.青藏高原不同粒径大气颗粒物元素分析?[J].环境化学,2013(06):968-973.
[7] 狄一安,杨勇杰,刘俊卿,周瑞,于跃,刘岩,徐薇,卜晓辉,湛福祥.青藏日喀则大气颗粒物水溶性无机离子粒径分布特征初探[J].环境化学,2014(02):355-356.
[8] 姚檀栋,朱立平.青藏高原环境变化对全球变化的响应及其适应对策[J].地球科学进展,2006(05):459-464.
[9] 王泽斌,徐建中,余光明,崔晓庆,任贾文.祁连山大雪山地区大气PM2.5细粒子中可溶性离子特征[J].冰川冻土,2013(02):336-344.
[10] 刀谞,滕恩江,吕怡兵,张霖琳,梁宵,许秀艳,李建军,杜丽.离子色谱法测定 PM2.5中可溶性阳离子的探讨[J].环境监测管理与技术,2013(05):44-47.
[11] World Health Organization.Urban outdoor air pollution database[M].Department of Public Health and Environment . Geneva, Switzerland,2011
[12] 刀谞,张霖琳,王超,陈烨,吕怡兵,滕恩江.京津冀冬季与夏季PM2.5/PM10及其水溶性离子组分区域性污染特征分析?[J].环境化学,2015(1):60-69.
[13] 于艳科,尹丽倩,牛振川,陈进生,张福旺.中国海峡西岸城市群冬季PM2.5和PM10中水溶性离子的污染特征[J].中国环境科学,2012(09):1546-1553.
[14] 韩月梅,沈振兴,曹军骥,李旭祥,赵景联,刘萍萍,王云海,周娟.西安市大气颗粒物中水溶性无机离子的季节变化特征[J].环境化学,2009(02):261-266.
[15] 徐宏辉,王跃思,温天雪,何新星.北京大气气溶胶中水溶性离子的粒径分布和垂直分布[J].环境科学,2007(01):14-19.
[16] Kong L D;Yang Y W;Zhang S Q.Observations of linear dependence between sulfate and nitrate in atmospheric particles[J].Journal of Geophysical Research:Atmospheres,2013:119,341-361.
[17] 岳玎利,胡敏,吴志军.北京夏季大气主要含氮无机化合物的变化规律与相互作用[J].中国环境监测,2013(03):9-14.
[18] Pope CA;Dockery DW .Health effects of fine particulate air pollution: Lines that connect[J].Journal of the Air & Waste Management Association,2006(6):709-742.
[19] Zhuang Hong;Fang Ming;Wexler Anthony S;Chan Chak K .Size distributions of particulate sulfate, nitrate, and ammonium at a coastal site in Hong Kong[J].Atmospheric environment,1999(6):843-853.
[20] Pio C A;Harrison R M .Vapor-pressure of ammoniumchloride aerosol-Effect of temperature and humidity[J].Atmospheric Environment,1987,21(12):2711-2715.
[21] Taehyoung Lee;Xiao-Ying Yu;Sonia M. Kreidenweis;William C. Malm;Jeffrey L. Collett .Semi-continuous measurement of PM_(2.5) ionic composition at several rural locations in the United States[J].Atmospheric environment,2008(27):6655-6669.
[22] Michael Lewandowski;Mohammed Jaoui;Tadeusz E. Kleindienst;John H. Offenberg;Edward O. Edney .Composition of PM_(2.5) during the summer of 2003 in Research Triangle Park, North Carolina[J].Atmospheric environment,2007(19):4073-4083.
[23] Maenhaut W;Raes N;Chi XG;Cafmeyer J;Wang W .Chemical composition and mass closure for PM2.5 and PM10 aerosols at[J].X-Ray Spectrometry: An International Journal,2008(2):193-197.
上一张 下一张
上一张 下一张
计量
  • 下载量()
  • 访问量()
文章评分
  • 您的评分:
  • 1
    0%
  • 2
    0%
  • 3
    0%
  • 4
    0%
  • 5
    0%