img

官方微信

  • CN 62-1070/P
  • ISSN 1000-694X
  • 双月刊 创刊于1981年
高级检索
天气与气候

乌鲁木齐霾天气PM10单颗粒物理化学特征

  • 王江 ,
  • 洪雯 ,
  • 吴新萍 ,
  • 陆辉
展开
  • 1. 新疆维吾尔自治区气象台, 新疆 乌鲁木齐 830002;
    2. 乌鲁木齐市环境保护科学研究所, 新疆 乌鲁木齐 830000;
    3. 塔中气象站, 新疆 塔中 841000;
    4. 塔城地区气象局, 新疆 塔城 834700
王江(1981-),男,湖南汨罗人,工程师,主要从事短时和短期预报。Email:andsen68@163.com

收稿日期: 2015-04-06

  修回日期: 2015-05-20

  网络出版日期: 2015-11-20

基金资助

国家自然科学基金项目(41405141);中央级公益性科研院所基本科研业务费专项(IDM201201);中国气象局预报员专项(CMAYBY2013-079)

Physical and Chemical Characteristics of Individual Particle during a Typical Haze Episode in Urumqi, Xinjian, China

  • Wang Jiang ,
  • Hong Wen ,
  • Wu Xinping ,
  • Lu Hui
Expand
  • 1. Xinjiang Meteorological Observatory, Urumqi 830002, China;
    2. Urumqi Institute of Environmental Protection, Urumqi 830000, China;
    3. Tazhong Meteorological Station, Tazhong 841000, Xinjiang, China;
    4. Tacheng Meteorological Burean, Tacheng 834700, Xinjiang, China

Received date: 2015-04-06

  Revised date: 2015-05-20

  Online published: 2015-11-20

摘要

为了解乌鲁木齐冬季污染天气形成过程中大气颗粒物化学组分的变化,探讨霾天气快速形成的主要原因,应用扫描电镜/X射线能谱仪(SEM/EDX)对2013年2月乌鲁木齐东南郊一次典型霾天和正常天气所采集的大气颗粒物(PM10)样品进行了微观形貌和化学组成的对比分析。结果表明:伴随着霾形成过程细粒子浓度呈现急剧上升趋势,PM1.0/PM10比值高达0.77。SEM/EDX观测显示,霾天形成前后,PM10的形态结构和元素组成存在较明显的差异,霾天规则的石膏颗粒占规则颗粒的71.1%,明显高于正常天气,表明大气颗粒物的硫化现象比较普遍,大量硅铝酸盐飞灰说明采样点周边有较明显的燃煤源输送;二次无机颗粒组成主要为硫酸盐颗粒,由正常天气的16.1%增加到24.6%,高浓度硫酸盐与乌鲁木齐东南郊此次霾形成有密切的联系。

本文引用格式

王江 , 洪雯 , 吴新萍 , 陆辉 . 乌鲁木齐霾天气PM10单颗粒物理化学特征[J]. 中国沙漠, 2015 , 35(6) : 1652 -1658 . DOI: 10.7522/j.issn.1000-694X.2015.00136

Abstract

In order to understand the chemical composition of atmospheric particulates during the winter haze espsode in Urumqi, and to explore the causes of haze formation, the scanning electron microscopy and energy dispersive X-ray spectroscopy(SEM/EDX) were used to study the chemical composition and microscopic morphology of aerosol PM10 samples collected during the typical haze and no-haze episodes in February 2013. The results indicated that the fine particle concentration showed a sharp rise in the haze formation process, and the PM1.0/PM10 ratio could reach 0.77. There exists significant difference in chemical composition and microscopic morphology of PM10 between haze and no-haze episodes. Regular gypsum particles could account for 71.1% in haze weather, a percentage obviously higher than that in no-haze episode. This fact showed that the surface sulfuration of aerosol particles was extremely severe, and the large amount of aluminosilicate particles in fly ash came from coal combustion pollution. As the main component of secondary inorganic particles, sulfate particles accounted for 24.6% in haze episode, but it only accounted for 16.1% on no-haze day. Sulfate was the primary factor contributing to this heavy haze formation in Urumqi.

参考文献

[1] Chan C K,Yao X H.Air pollution in mega cities in China[J].Atmospheric Environment,2008,42:1-42.
[2] 朱彤,尚静,赵德峰.大气复合污染及灰霾形成中非均相化学过程的作用[J].中国科学(B),2010,40:1731-1740.
[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[J].环境科学学报,32(11):2660-2669.
[4] 王跃思,姚利,王莉莉,等.2013年元月我国中东部地区强霾污染成因分析[J].中国科学(D),2014,44(1):15-26.
[5] 陈秋方,孙在,谢小芳.杭州灰霾天气超细颗粒浓度分布特征[J].环境科学,2014,35(8):2851-2856.
[6] 李娟.中亚地区沙尘气溶胶的理化特性、来源、长途传输及其对全球变化的可能影响[D].上海:复旦大学,2009.
[7] 邵龙义,杨书申,李卫军,等.大气颗粒物单颗粒分析方法的应用现状及展望[J].古地理学报,2005,7(4):535-548.
[8] Vecchi R,Bernardoni V,Cricchio D,et al.The impact of fireworks on airborne particles[J].Atmospheric Environment,2008,42(6):1121-1132.
[9] Shi Y,Zhang N,Gao J,et al.Effect of fireworks display on perchlorate in air aerosols during the Spring Festival[J].Atmospheric Environment,2011,45(6):1323-1327.
[10] 徐鸣,徐峰.乌鲁木齐市采暖季首要污染物污染特征初探[J].干旱环境监测,2004,18(1):36-38.
[11] Ge X L,Zhang Q,Sun Y L,et al.Effect of aqueous-phase processing on aerosol chemistry and size distributions in Fresno,California,during wintertime[J].Environmental Chemistry,2012,9:221-235.
[12] 郑玉萍,李景林.乌鲁木齐近31年大雾天气气候特征分析[J].气象,2008,34(8):2-28.
[13] 肖正辉.兰州市大气PM10的物理和化学特征及生物活性研究[D].北京:中国矿业大学,2007.
[14] Shi Z B,Shao L Y,Jones T P,et al.Characterization of airborne individual particles collected in an urban area,a satellite city and a clean air site in Beijing,2001[J].Atmospheric Environment,2003,37(29):4097-4108.
[15] 宋晓众.煤矿区城市大气PM10的物理化学特征及毒性研究[D].北京:中国矿业大学,2009.
[16] Takahashi Y,Miyoshi T,Yabuki S,et al.Observation of transformation of calcite to gypsum in mineral aerosols by Ca K-edge X-ray absorption near-edge structure(XANES)[J].Atmospheric Environment,2008,42(26):6535-6541.
[17] Mori I,Nishikawa M,Iwasaka Y.Chemical reaction during the coagulation of ammonium sulphate and mineral particles in the atmosphere[J].Science of the Total Environment,1998,224(1):87-91.
[18] 刘彦飞,邵龙义,程晓霞.大气可吸入颗粒物(PM10) 单颗粒硫化特征[J].环境科学,2010,31(11):2555-2562.
[19] Li W,Shao L,Wang Z,et al.Size,composition,and mixing state of individual aerosol particles in a South China coastal city[J].Journal of Environmental Sciences,2010,22(4):561-569.
[20] Zhuang H,Chan C K,Fang M,et al.Size distributions of particulate sulfate,nitrate,and ammonium at a coastal site in Hong Kong[J].Atmospheric Environment,1999,33(6):843-853.
[21] Cabada J C,Rees S,Takahama S,et al.Mass size distributions and size resolved chemical composition of fine particulate matter at the Pittsburgh supersite[J].Atmospheric Environment,2004,38(20):3127-3141.
[22] He K,Yang F,Ma Y,et al.The characteristics of PM2.5 in Beijing,China[J].Atmospheric Environment,2001,35(29):4959-4970.
[23] 热比古丽·达木拉,阿布力孜·伊米提,迪丽努尔·塔力甫.乌鲁木齐冬季雾天可吸入颗粒物透射电子显微镜研究[J].中国环境监测,2013,29(4):107-110.
[24] Li J,Zhuang G,Huang K,et al.Characteristics and sources of air-borne particulate in Urumqi,China,the upstream area of Asia dust[J].Atmospheric Environment,2008,42(4):776-787.
[25] 赵克蕾,刘新春,陆辉,等.乌鲁木齐冬季大气细颗粒物水溶性离子特征及来源[J].中国沙漠,2015,35(3):707-714.
[26] Stockwell W R,Watson J G,Robinson N F,et al.The ammonium nitrate particle equivalent of NOx emissions for wintertime conditions in Central California's San Joaquin Valley[J].Atmospheric Environment,2000,34(27):4711-4717.
[27] Lee T,Yu X Y,Ayres B,et al.Observations of fine and coarse particle nitrate at several rural locations in the United States[J].Atmospheric Environment,2008,42(11):2720-2732.
[28] Beilke S,Gravenhorst G.Heterogeneous SO2-oxidation in the droplet phase[J].Atmospheric Environment,1978,12(1):231-239.
[29] Wang Y,Zhuang G,Tang A,et al.The ion chemistry and the source of PM2.5 aerosol in Beijing[J].Atmospheric Environment,2005,39(21):3771-3784.
[30] Wang Y,Zhuang G,Zhang X,et al.The ion chemistry,seasonal cycle,and sources of PM2.5 and TSP aerosol in Shanghai[J].Atmospheric Environment,2006,40(16):2935-2952.
[31] 李卫军.极端污染天气条件下气溶胶单颗粒特性和非均相转化[D].北京:中国矿业大学,2009.
[32] 肖正辉,邵龙义,张宁,等. 兰州市冬季大气PM10的微观形貌和粒度分布[J].辽宁工程技术大学学报,2007,26(1):147-150.
[33] 段菁春,潭吉华,王淑兰,等.兰州市大气单颗粒来源识别及应用[J].环境工程技术学报,2012,2(3):234-239.
文章导航

/