南京大学学报(自然科学版) ›› 2015, Vol. 51 ›› Issue (3): 517–.

• • 上一篇    下一篇

基于在线监测的上海郊区冬季PM2.5来源解析

王晓浩*,赵倩彪,崔虎雄   

  • 出版日期:2015-04-23 发布日期:2015-04-23
  • 作者简介:(上海市环境监测中心,上海,200235)
  • 基金资助:
    上海市环境保护局青年基金(沪环科2014-98,沪环科2014-56),上海市环境保护局2012年环境保护系列课题任务书 (shcg12-00058)

PM2.5 source apportionment at suburb of shanghai in winter based on real time monitoring

Wang Xiaohao1, Zhao Qianbiao1, Cui Huxiong1   

  • Online:2015-04-23 Published:2015-04-23
  • About author:( Shanghai Environmental Monitoring Center, Shanghai,200235, China)

摘要: 利用1405F、Marga和Xact625在线监测仪于2013年12月23日至2014年2月18日期间对上海市青浦淀山湖地区PM2.5的质量浓度和化学组分进行了测定。结果显示:淀山湖地区冬季PM2.5平均质量浓度为85.1 μg?m-3,高于国家环境空气质量年均二级浓度限值1.4倍,高出同期全市PM2.5平均浓度(65.5 μg?m-3)30%。无机离子组分占PM2.5的比重为58.4%,其中二次离子NO3-、SO42-和NH4+的含量最高,总体均值分别为(17.13±15.70)μg?m-3、(13.45±11.10)μg?m-3和(12.09±10.37)μg?m-3,分别占PM2.5浓度的20.1%、15.8%和14.2%。利用PMF方法对淀山湖地区PM2.5的来源解析结果显示:二次气溶胶、燃油、生物质燃烧/海盐、扬尘/建筑尘、燃煤/冶炼尘的贡献率分别为50.8%、17.5%、17.2%、7.7%和6.9%。

Abstract: PM2.5 mass concentration and chemical speciation were monitored at Dianshan Lake, a western Suburb of Shanghai by real time analyzers (1405F, Marga and Xact625 ) from 23rd Dec. 2013 to 18th Feb. 2014. The result showed that the average concentration of PM2.5 at Dianshan Lake was 85.1 μg?m-3, 1.4 times higher than the PM2.5 annual limit of the national ambient air quality standards of china, 30% higher than the PM2.5 average concentration of Shanghai (65.5 μg?m-3) . Total inorganic ions accounts for 58.4% of PM2.5 mass concentration, secondary inorganic ions (NO3-, SO42- and NH4+) were (17.13±15.70)μg?m-3、(13.45±11.10)μg?m-3 and(12.09±10.37)μg?m-3, accounting for 20.1%、15.8% and 14.2% of PM2.5 mass concentration, respectively. Positive Matrix Factorization (PMF) model was performed to identify the source of PM2.5 at Dianshan Lake. Five significant sources contributing to the observed PM2.5were: secondary aerosols, oil combustion, biomass burning/sea salt, fugitive dust and coal combustion/smelting dust, with the contribution of 50.8%, 17.5%, 17.2%, 7.7% and 6.9% of PM2.5 mass concentration, respectively.

[1].Gold D R, Litonjua A A, Zanobetti A, et al. Air pollution and ST-segment depression in elderly subjects. Environmental Health Perspectives, 2005, 113(7): 883~887.
[2].吴 兑, 邓雪娇, 毕雪岩等. 细粒子污染形成灰霾天气导致广州地区能见度下降. 热带气象学报, 2007(1): 1~6.
[3].吴 兑, 刘啟汉, 梁延刚等. 粤港细粒子(PM2.5)污染导致能见度下降与灰霾天气形成的研究. 环境科学学报, 2012, (11): 2660~2669.
[4].陈 涛. 成都市中心城区细粒子来源解析研究. 硕士学位论文.成都:西南交通大学, 2009.
[5].李剑东. 长沙市郊区大气可吸入颗粒物化学组分特性及源解析. 硕士学位论文.长沙:中南大学, 2009.
[6].宋 宇, 唐孝炎, 方 晨等. 北京市大气细粒子的来源分析. 环境科学, 2002(6): 11~16.
[7].Sun Y L, Zhang Q, Schwab J J, et al. Characterization of the sources and processes of organic and inorganic aerosols in New York city with a high-resolution time-of-flight aerosol mass apectrometer. Atmospheric Chemistry and Physics, 2011, 11(4): 1581~1602.
[8].郑 玫, 张延君, 闫才青等. 中国PM2.5来源解析方法综述. 北京大学学报(自然科学版), 2014(6): ~ .
[9].Reff A, Eberly S I, Bhave P V. Receptor modeling of ambient particulate matter data using positive matrix factorization: Review of existing methods. Journal of the Air & Waste Management Association, 2007, 57(2): 146~154.
[10].Paatero P. Least squares formulation of robust non-negative factor analysis. Chemometrics and Intelligent Laboratory Systems, 1997, 37(1): 23~35.
[11].杨凌霄. 济南市大气PM2.5污染特征、来源解析及其对能见度的影响.济南:山东大学, 2008.
[12].张懿华. 上海市典型霾污染过程二次无机气溶胶组分特征研究. 环境监测管理与技术, 2011 (S1): 7~13.
[13].张智胜, 陶 俊, 谢绍东等. 成都城区PM2.5季节污染特征及来源解析. 环境科学学报, 2013(11): 2947~2952.
[14].Kong S F, Han B, Bai Z P, et al. Receptor modeling of PM2.5, PM10 and TSP in different seasons and long-range transport analysis at a coastal site of Tianjin, China. Science of the Total Environment, 2010, 408(20): 4681~4694.
[15].Warneck P. The relative importance of various pathways for the oxidation of sulfur dioxide and nitrogen dioxide in sunlit continental fair weather clouds. Physical Chemistry Chemical Physics, 1999, 1(24): 5471~5483.
[16].胡大伟. 大气中亚微米颗粒物吸湿性及光学特性的实验室模拟研究. 博士学位论文. 上海:复旦大学, 2012.
[17].Guo H, Ding A J, So K L, et al. Receptor modeling of source apportionment of Hong Kong aerosols and the implication of urban and regional contribution. Atmospheric Environment, 2009, 43(6): 1159~1169.
[18].Ho K F, Cao J J, Lee S C, et al. Source apportionment of PM2.5 in urban area of Hong Kong. Journal of Hazardous Materials, 2006, 138(1): 73~85.
[19].Sun Y L, Zhuang G S, Ying W, et al. The air-borne particulate pollution in Beijing - concentration, composition, distribution and sources. Atmospheric Environment, 2004, 38(35): 5991~6004.
[20].杨天智. 长沙市大气颗粒物PM2.5化学组分特征及来源解析. 硕士学位论文. 长沙:中南大学, 2010.
[21].Watson J G, Chow J C. Source characterization of major emission sources in the Imperial and Mexicali Valleys along the US/Mexico border. Science of the Total Environment, 2001, 276(1-3): 33~47.
[22].Behera S N, Betha R, Balasubramanian R. Insights into Chemical Coupling among Acidic Gases, Ammonia and Secondary Inorganic Aerosols. Aerosol and Air Quality Research, 2013, 13(4): 1282~U414.
[23].朱先磊, 张远航, 曾立民等. 北京市大气细颗粒物PM2.5的来源研究. 环境科学研究, 2005, (05): 1~5.
[24].Han B, Kong S F, Bai Z P, et al. Characterization of Elemental Species in PM2.5 Samples Collected in Four Cities of Northeast China. Water Air and Soil Pollution, 2010, 209(1-4): 15~28.
No related articles found!
Viewed
Full text


Abstract

Cited

  Shared   
  Discussed   
No Suggested Reading articles found!