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中国科学院大学学报 ›› 2015, Vol. 32 ›› Issue (4): 490-497.DOI: 10.7523/j.issn.2095-6134.2015.04.010

• 环境科学与地理学 • 上一篇    下一篇

兰州大气细颗粒物中有机碳与元素碳的污染特征

李英红1,2, 段菁春3, 郑乃嘉2, 谭吉华2,4, 饶志国1, 马永亮4, 贺克斌4   

  1. 1. 兰州大学 西部环境教育部重点实验室/西部环境与气候变化研究院, 兰州 730000;
    2. 中国科学院大学资源与环境学院, 北京 100049;
    3. 中国环境科学研究院 环境基准与 风险评估国家重点实验室, 北京 100012;
    4. 清华大学环境学院 环境模拟与污染控制国家重点联合实验室, 北京 100084
  • 收稿日期:2014-08-14 修回日期:2015-01-02 发布日期:2015-07-15
  • 通讯作者: 谭吉华
  • 基金资助:
    国家自然科学基金(41475116,41275134)、国家环境保护大气复合污染来源与控制重点实验室基金(SCAPC201401)和中国环境科学研究院中央级公益性科研院所基本科研业务专项(2012ysky09)资助

Characteristics of organic and element carbon in fine particles in Lanzhou

LI Yinghong1,2, DUAN Jingchun3, ZHENG Naijia2, TAN Jihua2,4, RAO Zhiguo1, MA Yongliang4, HE Kebin4   

  1. 1. Key Laboratory of Western China's Environmental Systems(MOE), Research School of Arid Environment & Climate Change, Lanzhou University, Lanzhou 730000, China;
    2. College of Resources and Environment, University of Chinese Academy of Sciences, Beijing 100049, China;
    3. State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;
    4. State Key Joint Laboratory of Environment Simulation and Pollution Control, School of Environment, Tsinghua University, Beijing 100084, China
  • Received:2014-08-14 Revised:2015-01-02 Published:2015-07-15

摘要: 采集兰州冬季采暖期及夏季PM2.5样品共60个,通过DRI 测定有机碳(OC)和元素碳(EC). 结果显示:冬季OC和EC平均质量浓度分别为(35.39±13.88)μg/m3和(13.80±5.41)μg/m3,夏季分别为(9.74±3.30)μg/m3和(4.44±2.00)μg/m3,冬季污染远高于夏季. 冬夏季OC和EC相关系数分别为0.91和0.76,表明冬季兰州PM2.5中OC和EC的来源相似. 二次有机碳质量浓度冬夏季分别为(8.48±6.10)μg/m3和(3.07±2.20)μg/m3,约占OC含量的(22.46±11.93)%和(31.29±18.51)%,表明兰州冬夏季PM2.5中OC的来源均以一次排放为主,夏季二次源贡献高于冬季. 对8种不同温度段碳质组分分析表明,兰州冬季生物质燃烧较夏季有所增加,夏季可能主要为机动车尾气.

关键词: PM2.5, 有机碳, 元素碳, 二次有机碳, 季节变化

Abstract: A total of 60 PM2.5 samples were collected during winter and summer seasons in Lanzhou city. OC and EC were measured by the thermal/optical method using DRI-2001A. The results indicated that carbonaceous aerosol in winter was significantly higher than that in summer. The average concentrations of OC and EC were (35.39±13.88) μg/m3 and (13.80±5.41) μg/m3 in winter and (9.74±3.30) μg/m3 and (4.44±2.00) μg/m3 in summer, respectively. The correlation between OC and EC was 0.91 in winter and 0.76 in summer, which revealed that OC and EC had similar sources. The concentrations of SOC were (8.48±6.10)μg/m3 and (3.07±2.20)μg/m3 in winter and summer, and they were about (22.46±11.93)% and (31.29 + 18.51)% of OC in PM2.5, respectively, which manifested that OC was mainly from primary sources and the contribution of secondary transformation was higher in summer than in winter. Analysis on the eight fractions of carbonaceous aerosol within the different temperature ranges showed that biomass burning had a high contribution for carbonaceous aerosol in PM2.5 in winter, but vehicle emissions might be the major source in summer.

Key words: PM2.5, OC, EC, SOC, seasonal variation

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