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太原大气颗粒物中水溶性无机离子质量浓度及粒径分布特征
摘要点击 2998  全文点击 1262  投稿时间:2016-03-02  修订日期:2016-04-22
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中文关键词  水溶性无机离子  季节变化  粒径分布  来源  太原
英文关键词  water-soluble inorganic ions  seasonal variation  size distribution  source  Taiyuan
作者单位E-mail
王璐 中国科学院大气物理研究所大气边界层物理和大气化学国家重点实验室, 北京 100029
中国科学院大学, 北京 100049 
wanglu@dq.cern.ac.cn 
温天雪 中国科学院大气物理研究所大气边界层物理和大气化学国家重点实验室, 北京 100029 wtx@dq.cern.ac.cn 
苗红妍 中国科学院大气物理研究所大气边界层物理和大气化学国家重点实验室, 北京 100029
中国气象局气象干部培训学院辽宁分院, 沈阳 110166 
 
高文康 中国科学院大气物理研究所大气边界层物理和大气化学国家重点实验室, 北京 100029  
王跃思 中国科学院大气物理研究所大气边界层物理和大气化学国家重点实验室, 北京 100029  
中文摘要
      为研究太原大气颗粒物中水溶性无机离子的质量浓度水平、季节变化和粒径分布特征,于2012年6月~2014年5月使用惯性撞击式分级采样器采集大气颗粒物样品,并用离子色谱分析了其中的水溶性无机离子组成.结果表明,PM1.1、PM2.1和PM9中总水溶性无机离子浓度平均值分别为(15.39±9.91)、(21.10±15.49)和(36.34±18.51)μg·m-3.PM1.1和PM2.1中,二次离子(SO42-、NO3-和NH4+)占总水溶性无机离子质量分数最高;PM9中SO42-和Ca2+占比较高.各粒径段中SO42-和NH4+季节变化特征相似,均为冬夏季节高、春秋季节低;NO3-、K+和Cl-季节变化特征一致:冬季 >秋季 >春季 >夏季;Ca2+和Mg2+季节变化特征一致:春季 >冬季 >秋季 >夏季.SO42-和NH4+为细模态单峰分布,春秋季节在0.43~0.65 μm处出现峰值,而夏季出现在0.65~1.1 μm处,细粒径段峰值出现由凝结模态向液滴模态转移的现象.NO3-为双模态离子,冬季在0.43~2.1 μm出现明显细粒径段峰值,夏季在4.7~5.8 μm出现明显粗模态峰值.K+、Na+和Cl-为双模态离子,分别在0.43~1.1和4.7~5.8 μm出现峰值;Ca2+、Mg2+和F-呈粗模态单峰分布,在4.7~5.8 μm出现峰值.主成分分析结果显示,水溶性无机离子来源主要是二次源、燃煤、工业源、生物质燃烧和土壤尘或降尘.
英文摘要
      Size-resolved filter samples were collected in Taiyuan every other week from June 2012 to May 2014. The mass concentrations of water-soluble ions (Na+, NH4+, K+, Mg2+, Ca2+, F-, Cl-, NO3- and SO42-) were measured by ion chromatography. The results showed that the total concentrations of measured water-soluble ions were (15.39±9.91), (21.10±15.49) and (36.34±18.51) μg·m-3 in PM1.1, PM2.1 and PM9, respectively. In PM1.1 and PM2.1, secondary water-soluble ions (SO42-, NO3- and NH4+) comprised 87.59% and 86.30% of all water-soluble ions, respectively, while in PM9, SO42- and Ca2+ comprised 32.78% and 28.54% of all water-soluble ions, respectively. SO42- and NH4+ had higher concentrations in winter and summer, and lower in spring and autumn. NO3-, K+and Cl- presented similar seasonal variation with a descending order of winter >autumn >spring >summer, and Ca2+ and Mg2+ followed the sequence of spring >winter >autumn >summer. SO42- and NH4+ showed a unimodal size distribution and the peak in the fine mode shifted from 0.43-0.65 μm in spring and autumn to 0.65-1.1 μm in summer. NO3- showed a bimodal size distribution. NO3- and NH4+ were dominated by the fine mode peaking at 0.43-2.1 μm in winter, and NO3- was dominated by the coarse mode peaking at 4.7-5.8 μm in summer. K+, Na+and Cl- also showed a bimodal size distribution with the fine mode at 0.43-1.1 μm and the coarse mode at 4.7-5.8 μm. Ca2+, Mg2+ and F- were unimodal with the peak in the coarse mode of 4.7-5.8 μm. On heavily polluted days, the mass concentrations of secondary water-soluble ions and Cl- accumulated, and secondary water-soluble ions were unimodal with the peak in the fine mode of 1.1-2.1 μm. However, on clear days, secondary water-soluble ions showed a bimodal size distribution with the fine mode at 0.43-0.65 μm and the coarse mode at 4.7-5.8 μm. The peak of secondary water-soluble ions in the fine mode shifted. PCA analysis showed that the sources of water-soluble ions were dominated by the secondary formation, coal combustion, industrial emission, biomass burning, and soil particles or falling dust.

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