南京市秋季大气颗粒物中有机碳和元素碳的浓度水平及分布特征

袁思宇, 沈国锋, 赵秋月. 南京市秋季大气颗粒物中有机碳和元素碳的浓度水平及分布特征[J]. 环境化学, 2014, 33(5): 724-730. doi: 10.7524/j.issn.0254-6108.2014.05.021
引用本文: 袁思宇, 沈国锋, 赵秋月. 南京市秋季大气颗粒物中有机碳和元素碳的浓度水平及分布特征[J]. 环境化学, 2014, 33(5): 724-730. doi: 10.7524/j.issn.0254-6108.2014.05.021
YUAN Siyu, SHEN Guofeng, ZHAO Qiuyue. Concentrations and distribution characteristics of organic carbon and element carbon in ambient particulate matter (PM10 and PM2.5) during autumn in Nanjing[J]. Environmental Chemistry, 2014, 33(5): 724-730. doi: 10.7524/j.issn.0254-6108.2014.05.021
Citation: YUAN Siyu, SHEN Guofeng, ZHAO Qiuyue. Concentrations and distribution characteristics of organic carbon and element carbon in ambient particulate matter (PM10 and PM2.5) during autumn in Nanjing[J]. Environmental Chemistry, 2014, 33(5): 724-730. doi: 10.7524/j.issn.0254-6108.2014.05.021

南京市秋季大气颗粒物中有机碳和元素碳的浓度水平及分布特征

  • 基金项目:

    江苏省自然科学基金(BK20131031);中国博士后科学基金(2013M531322)资助.

Concentrations and distribution characteristics of organic carbon and element carbon in ambient particulate matter (PM10 and PM2.5) during autumn in Nanjing

  • Fund Project:
  • 摘要: 在2011年秋季,连续24 h采集南京市区大气粗颗粒物(PM10)和细颗粒物(PM2.5)样品,采用IMPROVE-热光反射法(TOR),分析样品中的有机碳(OC)和元素碳(EC)的浓度水平和分布特征.研究表明,南京秋季观测期间PM10中OC和EC的平均浓度水平分别在23.3±11.0 μg·m-3和7.7±3.2 μg·m-3,PM2.5中,OC和EC的浓度分别是18.1±9.6 μg·m-3和6.6±2.9 μg·m-3.与国内其他城市相比,南京市秋季的碳组分浓度处于较低水平,但与发达国家的城市相比,浓度水平很高.观测期内PM10和PM2.5中的OC和EC的日变化规律与颗粒物的相似,趋势相近.OC和EC主要分布于细粒子PM2.5中,且EC比OC更倾向于在细颗粒物上的分布.基于8碳组分(OC1,OC2,OC3,OC4,OPC,EC1,EC2和EC3)分析结果初步判断,南京市秋季机动车汽油燃烧排放污染是EC1的主要来源,对南京市碳气溶胶贡献最大;生物质燃烧、工业燃煤,道路和施工扬尘是OC的主要来源,对南京市大气中碳气溶胶贡献较大;柴油燃烧是EC2和EC3的主要来源,对南京市碳气溶胶的贡献最小.
  • 加载中
  • [1] Wolff G T. Particulate elemental carbon in the atmosphere[J]. Journal of Air Pollution Control Association, 1981, 31: 935-938
    [2] 段风魁, 贺克斌, 刘咸德, 等.含碳气溶胶研究进展: 有机碳和元素碳[J]. 环境工程学报, 2007, 1(8): 1-8
    [3] Gao J, ZhaY. Meteorological influence on predicting air pollution from MODWAS-derived aerosol optical thickness: a case study in Nanjing China[J]. Remote Sensing, 2010, 2(9): 2136-2147
    [4] 杨卫芬. 南京地区霾天气下大气细粒子污染特征的初步研究. 南京: 南京信息工程大学硕士学位论文, 2010
    [5] Cao J J, Lee S C, Ho KF, et al. Characterization of roadside fine particulate carbon and its eight fractions in Hong Kong[J]. Aerosol and AirQuality Research, 2006,6(2): 106-122
    [6] Cao J J, Lee S C, Ho K F, et al. Characteristics of carbonaceous aerosol in Pearl River Delta Region,China during 2001 winter period [J].Atmospheric Environment, 2003, 37:145l-1460
    [7] Duan F, He K, Ma Y, et al. Characteristics of carbonaceous aerosols in Beijing, China[J]. Chemosphere, 2005, 60:355-364
    [8] Gu J, Bai Z, Liu A, et al. Characterization of atmospheric organic carbon and element carbon of PM2.5 and PM10 at Tianjin, China[J]. Aerosol and Air Quality Research, 2010, 10: 167-176
    [9] 曹军骥, 李顺诚, 李杨, 等.2003年秋冬季西安大气中有机碳和元素碳的理化特征及其来源解析[J]. 自然科学进展, 2005, 15(12): 1460-1466
    [10] Wang X, Bi X, Sheng G, et al. Chemical composition and sources of PM10 and PM2.5 aerosols in Guangzhou, China[J]. Environmental Monitoring and Assessment, 2006, 119: 425-439
    [11] Höller R, Tohno S, Kasahara M, et al. Long-term characterization of carbonaceous aerosol in Uji, Japan[J]. Atmospheric Environment, 2002, 36(8): 1267-1275
    [12] Aymoz G, Jaffrezo J L, Chapuis D, et al. Seasonal variation of PM10 main constituents in two valleys of the French Alps. Ⅰ: EC/OC fractions[J]. Atmospheric Chemistry and Physics, 2007, 7: 661-675
    [13] Plewka A, Gnauk T, Brüggemann E, et al. Size-resolved aerosol characterization for a polluted episode at the IfT research station melpitz in autumn 1997[J]. Atmospheric Chemistry, 2004, 48(2): 131-156
    [14] Castro L M, Pio C A, Harrison M, et al. Carbonaceous aerosol in urban and rural European atmospheres: Estimation of secondary organic carbon concentrations[J]. Atmospheric Environment, 1999, 33, 2771-2781
    [15] Yttri K E, Bjerke A, Cape JN, et al. Elemental and organic carbon in PM10: A one year measurement campaign within the European Monitoring and Evaluation Programme EMEP[J]. Atmospheric Chemistry and Physics, 2007, 7: 5711-5725
    [16] Kam W, Liacos J W, Schauer J J, et al. Size-segregated composition of particulate matter (PM) in major roadways and surface streets[J].Atmospheric Environment, 2012, 55: 90-97
    [17] Zhou J, Zhan R, Cao J J, et al. Carbonaceous and ionic components of atmospheric fine particles in Beijing and their impact on atmospheric visibility[J].Aerosol and Air Quality Research, 2012, 12: 492-502
    [18] Feng Y, Chen Y, Guo H, et al. Characteristics of organic and elemental carbon in PM2.5 samples in Shanghai, China[J]. Atmospheric Research, 2009, 92: 434-442
    [19] Cao J J, Huang H, Lee S C, et al. Indoor/outdoor relationships for or ganic and elemental carbon in PM2.5 at residential homes in Guangzhou, China[J]. Aerosol and Air Quality Research, 2012, 12: 902-910
    [20] He Z, Kim Y J, Ogunjobi K O, et al. Carbonaceous aerosol characteristics of PM2.5 particles in Northeastern Asia in summer 2002[J]. Atmospheric Environment, 2004, 38(12): 1795-1800
    [21] Gnauk T, Brüggemann E, Müller K, et al. Aerosol characterisation at the FEBUKO upwind station Goldlauter (I): Particle mass, main ionic components, OCEC, and mass closure[J]. Atmospheric Environment, 2005, 39(23/24): 4209-4218
    [22] Rattigan O V, Felton H D, Felton M, et al. Multi-year hourly PM2.5 carbon measurements in New York: diurnal, day of week and seasonal patterns[J]. Atmospheric Environment, 2010, 44: 2043-2053
    [23] 钱凌. 南京大气气溶胶的污染特征及其影响因素观测研究. 南京:南京信息工程大学硕士学位论文,2008
    [24] 黄虹,李顺诚,曹军骥,等. 广州市夏季室内外PM2.5中有机碳、元素碳的分布特征[J]. 环境科学学报, 2005, 25(9): 1242-1249
    [25] Chen S, Liao S, Jian W, et al. Particle size dwastribution of aerosol carbons in ambient Air[J].Environment International, 1997, 23(4): 475-488
    [26] Larson T, Gould T, Simpson C, et al. Source apportionment of indoor, outdoor, and personal PM2.5 in Seattle, Washington, using positive matrix factorization[J]. Air and Waste Manag Assoc, 2004, 54(9): 1175-87
    [27] Chow, J C, Watson J G, Kuhns H D, et al. Source profiles for industrial, mobile, and area sources in the big bend regional aerosol visibility and observational (BRAVO)study[J]. Chemosphere, 2004, 54: 185-208
  • 加载中
计量
  • 文章访问数:  1214
  • HTML全文浏览数:  1214
  • PDF下载数:  810
  • 施引文献:  0
出版历程
  • 收稿日期:  2013-10-10
袁思宇, 沈国锋, 赵秋月. 南京市秋季大气颗粒物中有机碳和元素碳的浓度水平及分布特征[J]. 环境化学, 2014, 33(5): 724-730. doi: 10.7524/j.issn.0254-6108.2014.05.021
引用本文: 袁思宇, 沈国锋, 赵秋月. 南京市秋季大气颗粒物中有机碳和元素碳的浓度水平及分布特征[J]. 环境化学, 2014, 33(5): 724-730. doi: 10.7524/j.issn.0254-6108.2014.05.021
YUAN Siyu, SHEN Guofeng, ZHAO Qiuyue. Concentrations and distribution characteristics of organic carbon and element carbon in ambient particulate matter (PM10 and PM2.5) during autumn in Nanjing[J]. Environmental Chemistry, 2014, 33(5): 724-730. doi: 10.7524/j.issn.0254-6108.2014.05.021
Citation: YUAN Siyu, SHEN Guofeng, ZHAO Qiuyue. Concentrations and distribution characteristics of organic carbon and element carbon in ambient particulate matter (PM10 and PM2.5) during autumn in Nanjing[J]. Environmental Chemistry, 2014, 33(5): 724-730. doi: 10.7524/j.issn.0254-6108.2014.05.021

南京市秋季大气颗粒物中有机碳和元素碳的浓度水平及分布特征

  • 1. 江苏省环境科学研究院, 南京, 210029
基金项目:

江苏省自然科学基金(BK20131031);中国博士后科学基金(2013M531322)资助.

摘要: 在2011年秋季,连续24 h采集南京市区大气粗颗粒物(PM10)和细颗粒物(PM2.5)样品,采用IMPROVE-热光反射法(TOR),分析样品中的有机碳(OC)和元素碳(EC)的浓度水平和分布特征.研究表明,南京秋季观测期间PM10中OC和EC的平均浓度水平分别在23.3±11.0 μg·m-3和7.7±3.2 μg·m-3,PM2.5中,OC和EC的浓度分别是18.1±9.6 μg·m-3和6.6±2.9 μg·m-3.与国内其他城市相比,南京市秋季的碳组分浓度处于较低水平,但与发达国家的城市相比,浓度水平很高.观测期内PM10和PM2.5中的OC和EC的日变化规律与颗粒物的相似,趋势相近.OC和EC主要分布于细粒子PM2.5中,且EC比OC更倾向于在细颗粒物上的分布.基于8碳组分(OC1,OC2,OC3,OC4,OPC,EC1,EC2和EC3)分析结果初步判断,南京市秋季机动车汽油燃烧排放污染是EC1的主要来源,对南京市碳气溶胶贡献最大;生物质燃烧、工业燃煤,道路和施工扬尘是OC的主要来源,对南京市大气中碳气溶胶贡献较大;柴油燃烧是EC2和EC3的主要来源,对南京市碳气溶胶的贡献最小.

English Abstract

参考文献 (27)

返回顶部

目录

/

返回文章
返回