兰州生物质燃烧VOCs排放特征及其大气环境影响
详细信息    查看全文 | 推荐本文 |
  • 英文篇名:The characteristics of VOCs emission from biomass burning and its influence on atmospheric environment in Lanzhou City
  • 作者:郭文 ; 刘镇 ; 刘文博 ; 刘晓 ; 朱玉凡 ; 陈强
  • 英文作者:GUO Wen-kai;LIU Zhen;LIU Wen-bo;LIU Xiao;ZHU Yu-fan;CHEN Qiang;Key Laboratory for Semi-Arid Climate Change of the Ministry of Education, College of Atmospheric Sciences, Lanzhou University;Gansu Jingheyuan Environmental Protection Technology Co.Ltd;
  • 关键词:生物质燃烧 ; 挥发性有机物 ; 排放特征 ; 臭氧生成潜势 ; SOA生成潜势
  • 英文关键词:biomass burning;;volatile organic compounds;;emission characteristics;;ozone formation potential;;SOA formation potential
  • 中文刊名:ZGHJ
  • 英文刊名:China Environmental Science
  • 机构:兰州大学大气科学学院半干旱气候变化教育部重点实验室;甘肃静和源环保科技有限公司;
  • 出版日期:2019-01-20
  • 出版单位:中国环境科学
  • 年:2019
  • 期:v.39
  • 基金:干旱半干旱教育部重点实验室(兰州大学)中央高校基本科研业务费开放课题基金资助项目(lzujbky-2017-kb02)
  • 语种:中文;
  • 页:ZGHJ201901006
  • 页数:10
  • CN:01
  • ISSN:11-2201/X
  • 分类号:42-51
摘要
采用排放因子法建立了2016年兰州市生物质燃烧源挥发性有机物(VOCs)排放清单,并分析了污染物的时空排放特征,利用排放清单对生物质燃烧源的臭氧生成潜势(OFP)和二次有机气溶胶(SOA)生成潜势进行了估算,研究其排放对大气环境的影响.结果表明:2016年兰州市生物质燃烧源排放VOCs总量为6626.2t,排放高值区在榆中东南及东北部、永登中部和七里河南部,经济水平落后、秸秆产量大的地区污染物排放量更大.污染物排放集中在采暖季(11~3月)及农作物收割期(7~8月);兰州市生物质燃烧源的OFP总量为13880.3t,煨炕为OFP贡献最大的子源,占比46.1%,含氧挥发性有机物(OVOCs)为OFP贡献最大的关键组分,占比51.4%;OFP贡献排名前10的物种有乙酸、丙烯、2-丁酮、甲苯、甲醛、乙醛、间/对-二甲苯、1-丁烯、丙酸和异戊二烯.煨炕是SOA生成潜势贡献最大的子源,占比46.5%,芳香烃为SOA生成潜势贡献最大的关键组分,占比62.2%,SOA生成潜势贡献排名前10的物种有苯酚、甲苯、α-蒎烯、间/对-二甲苯、苯、邻二甲苯、茚、1,2,4-三甲基苯、乙苯和1,2,3-三甲基苯;以降低区域O3和SOA浓度为目标时,应优先管控煨炕和秸秆露天燃烧(玉米)两类子源.
        The emission inventory of volatile organic compounds(VOCs) from biomass burning was established by using the emission factor approach in Lanzhou City in 2016. Besides, the temporal and spatial distribution of VOCs was analyzed. Then the ozone formation potential(OFP) and the secondary organic aerosols(SOA) formation potential were estimated to assess the influence of VOCs emission from biomass burning on the atmospheric environment. The results showed that the total emissons of VOCs emitted by biomass burning was 6626.2t in Lanzhou City in 2016. The emission areas of high value were concentrated in the northeast and southeast of Yuzhong, central Yongdeng and south of Qilihe. The emission amounts were greater in regions with poor economic levels and large crop yields. Emissions were mainly concentrated in the heating season(November to March) and the harvest time of crops(July to August). The total OFP of biomass burning was 13880.3t in Lanzhou City in 2016. The smoldering Chinese kangs was the largest source of OFP contribution, accounting for 46.1%. Oxygenated volatile organic compounds(OVOCs) contributed the most to the OFP, accounting for 51.4%. The top 10 OFP species were acetic acid, propylene, 2-butanone, toluene, formaldehyde, acetaldehyde, m/p-xylene, 1-butene, propionic acid and isoprene. The smoldering Chinese kangs was also the largest contributor to SOA, accounting for 46.5%. The aromatic hydrocarbons were the key components of SOA contribution, accounting for 62.2%. The top 10 species of SOA formation potential were phenol, toluene, alpha-pinene, m/p-xylene, benzene, 1-xylene, indene, 1,2,4-trimethylbenzene, ethylbenzene, and 1,2,3-trimethylbenzene. To reduce the concentrations of ozone and SOA in the region, smoldering Chinese kangs and crop residue burning(maize) should be given more attention.
引文
[1]Zhang Y N,Xiang Y R,Chan L Y,et al.Procuring the regional urbanization and industrialization effect on ozone pollution in Pearl River Delta of Guangdong,China[J].Atmospheric Environment,2011,45(28):4898-4906.
    [2]Guo S,Hu M,Zamora M L,et al.Elucidating severe urban haze formation in China[J].Proceedings of the National Academy of Sciences of the United States of America,2014,111(49):17373.
    [3]Atkinson R.Atmospheric chemistry of VOCs and NOx[J].Atmospheric Environment,2000,34(12-14):2063-2101.
    [4]Yuan B,Hu W W,Shao M,et al.VOC emissions,evolutions and contributions to SOA formation at a receptor site in Eastern China[J].Atmospheric Chemistry&Physics,2013,13(17):8815-8832.
    [5]Bo Y,Cai H,Xie S D.Spatial and temporal variation of historical anthropogenic NMVOCs emission inventories in China[J].Atmospheric Chemistry&Physics,2008,8(23):11519-11566.
    [6]韩丽,王幸锐,何敏,等.四川省典型人为污染源VOCs排放清单及其对大气环境的影响[J].环境科学,2013,34(12):4535-4542.Han L,Wang X R,He M,et al.Inventory and Environmental Impact of VOCs Emission from the Typical Anthropogenic Sources in Sichuan Province[J].Environmental Science,2013,34(12):4535-4542.
    [7]曹国良,张小曳,王丹,等.中国大陆生物质燃烧排放的污染物清单[J].中国环境科学,2005,25(4):389-393.Cao G L,Zhang X Y,Wang D,et al.Inventory of atmospheric pollutants discharged from biomass burning in China continent[J].China Environmental Science,2005,25(4):389-393.
    [8]Wu R,Xie S.Spatial distribution of ozone formation in China derived from emissions of speciated volatile organic compounds[J].Environmental Science&Technology,2017,51(5):2574.
    [9]彭立群,张强,贺克斌.基于调查的中国秸秆露天焚烧污染物排放清单[J].环境科学研究,2016,29(8):1109-1118.Peng L Q,Zhang Q,He K B.Emission inventory of atmospheric pollutants from open burning of crop residues in China based on a national questionnaire[J].Research of Environmental Sciences,2016,29(8):1109-1118.
    [10]王书肖,张楚莹.中国秸秆露天焚烧大气污染物排放时空分布[J].中国科技论文在线,2008,3(5):329-333.Wang S X,Zhang C Y.Spatial and temporal distribution of air pollutant emissions from open burning of crop residues in China[J].Sciencepaper Online[J].2008,3(5):329-333.
    [11]闫东杰,苏航,黄学敏,等.西安市人为源挥发性有机物排放清单及研究[J].环境科学学报,2017,37(2):446-452.Yan D J,Su H,Huang X M,et al.VOCs emission inventory of anthropogenic sources in Xi'an[J].Acta Scientiae Circumstantiae,2017,37(2):446-452.
    [12]张凯,于周锁,高宏,等.兰州盆地人为源大气污染物网格化排放清单及其空间分布特征[J].环境科学学报,2017,37(4):1227-1242.Zhang K,Yu Z S,Gao H,et al.Gridded emission inventories and spatial distribution characteristics of anthropogenic atmospheric pollutants in Lanzhou valley[J].Acta Scientiae Circumstantiae,2017,37(4):1227-1242.
    [13]庄智.中国炕的烟气流动与传热性能研究[D].大连:大连理工大学,2009.
    [14]郭文凯,刘晓,朱玉凡,等.兰州市煨炕污染物排放清单及其对PM_(2.5)浓度贡献[J].环境科学,2018,39(11):4849-4857.Guo W K,Liu X,Zhu Y F,et al.Emission inventory of smoldering Chinese Kangs and its contribution to PM_(2.5) pollution in Lanzhou City[J].Environmental Science,2018,39(11):4849-4857.
    [15]中华人民共和国生态环境部.生物质燃烧源大气污染物排放清单编制技术指南(试行)[EB/OL].http://www.mee.gov.cn/gkml/hbb/bgg/201501/W020150107594588071383.pdf.Ministry of Ecology and Environment of the People's Republic of China.Technical guidelines for developing atmospheric pollutants emission inventory form biomass burning(Trial)[EB/OL].http://www.mee.gov.cn/gkml/hbb/bgg/201501/W020150107594588071383.pdf.
    [16]中华人民共和国生态环境部.大气挥发性有机物源排放清单编制技术指南(试行)[EB/OL].http://www.mee.gov.cn/gkml/hbb/bgg/201408/W020140828351293705457.pdf.Ministry of Ecology and Environment of the People's Republic of China.Technical guidelines for developing the atmospheric volatile organic compounds emission inventory(Trial)[EB/OL].http://www.mee.gov.cn/gkml/hbb/bgg/201408/W020140828351293705457.pdf.
    [17]兰州市统计局,国家统计局兰州调查队.兰州市统计年鉴2017[M].北京:中国统计出版社,2017:133-150.Lanzhou Municipal Bureau of Statistics,National Bureau of Statistics Lanzhou Investigation Team.Lanzhou statistical yearbook 2017[M].Beijing:China Statistics Press,2017:133-150.
    [18]毕于运.秸秆资源评价与利用研究[D].北京:中国农业科学院,2010.Bi Y Y.Study on straw resources evaluation and utilization in China[D].Beijing:Chinese Academy of Agricultural Sciences,2010.
    [19]毕于运,高春雨,王亚静,等.中国秸秆资源数量估算[J].农业工程学报,2009,25(12):211-217.Bi Y Y,Gao C Y,Wang Y J,et al.Estimation of straw resources in China[J].Transactions of the Chinese Society of Agricultural Engineering,2009,25(12):211-217.
    [20]中华人民共和国国家统计局.中国统计年鉴2017[EB/OL].http://www.stats.gov.cn/tjsj/ndsj/2017/indexch.htm.National Bureau of Statistics of China.China statistical yearbook 2017[EB/OL].http://www.stats.gov.cn/tjsj/ndsj/2017/indexch.htm.
    [21]Miller S D,Hawkins J D,Kent J,et al.NexSat:Previewing NPOESS/VIIRS imagery capabilities[J].Bulletin of the American Meteorological Society,2006,87(4):433-446.
    [22]Liao L B,Weiss S,Mills S,et al.Suomi NPP VIIRS day-night band on-orbit performance[J].Journal of Geophysical Research:Atmospheres,2013,118(22):12,705-12,718.
    [23]李旭文,牛志春,姜晟,等.环境监测卫星Suomi NPP业务特性及生态环境监测应用[J].环境监控与预警,2014,6(3):1-6.Li X W,Niu Z C,Jiang S,Operational characteristics of environmental monitoring satellite Suomi NPP and usage in ecological environment monitoring[J].Environmental Monitoring and Forewarning,2014,6(3):1-6.
    [24]NASA-FIRMS[EB/OL].https://firms.modaps.eosdis.nasa.gov/download.
    [25]Andreae M O.Emission of trace gases and aerosols from biomass burning[J].Global Biogeochemical Cycles,2001,15(4):955-966.
    [26]Li X H,Wang S X,Duan L,et al.Characterization of non-methane hydrocarbons emitted from open burning of wheat straw and corn stover in China.[J].Environmental Research Letters,2009,4(4):044015.
    [27]李兴华,王书肖,郝吉明.民用生物质燃烧挥发性有机化合物排放特征[J].环境科学,2011,32(12):3515-3521.Li X H,Wang S X,Hao J M.Characteristics of volatile organic compounds(VOCs)emitted from biofuel combustion in China[J].Environmental Science,2011,32(12):3515-3521.
    [28]Ciccioli P,Brancaleoni P,Frattoni M,et al.Determination of volatile organic compounds(voc)emitted from biomass burning of mediterranean vegetation species by GC-MS[J].Analytical Letters,2001,34(6):937-955.
    [29]郑君瑜,王水胜,黄志炯,等.区域高分辨率大气排放清单建立的技术方法与应用[M].北京:科学出版社,2014:162-187.Zheng J Y,Wang S S,Huang Z J,et al.Technical methods and applications for the establishment of regional high-resolution atmospheric emission inventories[M].Beijing:Science Press,2014:162-187.
    [30]Mccarty J L,Korontzi S,Justice C O,et al.The spatial and temporal distribution of crop residue burning in the contiguous United States.[J].Science of the Total Environment,2009,407(21):5701-5712.
    [31]何敏,王幸锐,韩丽,等.四川省秸秆露天焚烧污染物排放清单及时空分布特征[J].环境科学,2015,36(4):1208-1216.He M,Wang X R,Han L,et al.Emission inventory of crop residues field burning and its temporal and spatial distribution in Sichuan Province[J].Environmental Science,2015,36(4):1208-1216.
    [32]He M,Zheng J Y,Yin S S,et al.Trends,temporal and spatial characteristics,and uncertainties in biomass burning emissions in the Pearl River Delta,China.[J].Atmospheric Environment,2011,45(24):4051-4059.
    [33]卢学强,韩萌,冉靓,等.天津中心城区夏季非甲烷有机化合物组成特征及其臭氧产生潜力分析[J].环境科学学报,2011,31(2):373-380.Lu X Q,Han M,Ran L,et al.Characteristics of nonmethane organic compounds and their ozone formation potentials indowntown Tianjin in summer[J].Acta Scientiae Circumstantiae,2011,31(2):373-380.
    [34]Lam S H M,Saunders S M,Guo H,et al.Modelling VOC source impacts on high ozone episode days observed at a mountain summit in Hong Kong under the influence of mountain-valley breezes[J].Atmospheric Environment,2013,81(2):166-176.
    [35]Carter W P L.Development of ozone reactivity scales for volatile organic compounds[J].Journal of the Air and Waste Management Association,1994,44(7):881-899.
    [36]Zheng J Y,Shao M,Che W W,et al.Speciated VOC emission inventory and spatial patterns of ozone formation potential in the Pearl River Delta,China.[J].Environmental Science&Technology,2009,43(22):8580-8586.
    [37]徐敬,马建中.北京地区有机物种人为源排放量及O3生成潜势估算[J].中国科学:化学,2013,43(1):104-115.Xu J,Ma J Z.Estimation of anthropogenic emissions and ozone formation potential of speciated VOCs in Beijing area[J].Scientia Sinica(Chimica),2013,43(01):104-115.
    [38]Carter W P L.Updated maximum incremental reactivity scale and hydrocarbon bin reactivities for regulatory applications[R].California:Reported to California Air Resources Board Contract.2010.
    [39]Grosjean D.In situ,organic aerosol formation during a smog episode:Estimated production and chemical functionality[J].Atmospheric Environment,1992,26(6):953-963.
    [40]Grosjean D,Seinfeld J H.Parameterization of the formation potential of secondary organic aerosols[J].Atmospheric Environment,1989,23(8):1733-1747.
    [41]林旭,朱彬,安俊琳,等.南京北郊VOCs对臭氧和二次有机气溶胶潜在贡献的研究[J].中国环境科学,2015,35(4):976-986.Lin X,Zhu B,An J L,et al.Potential contribution of secondary organic aerosols and ozone of VOCs in the Northern Suburb of Nanjing[J].China Environmental Science,2015,35(4):976-986.
    [42]陈小方,张嘉妮,张伟霞,等.化工园区挥发性有机物排放清单及其环境影响[J].中国环境科学,2017,37(11):4062-4071.Chen X F,Zhang J N,Zhang W X,et al.VOCs emission inventory of a chemical industry park and its influence on atmospheric environment[J].China Environmental Science,2017,37(11):4062-4071.
    [43]Christian T J,Kleiss B,Yokelson R J,et al.Comprehensive laboratory measurements of biomass‐burning emissions:1.Emissions from Indonesian,African,and other fuels[J].Journal of Geophysical Research Atmospheres,2003,108(D23):4719.
    [44]Inomata S,Tanimoto H,Pan X L,et al.Laboratory measurements of emission factors of nonmethane volatile organic compounds from burning of Chinese crop residues[J].Journal of Geophysical Research,2015,120(10):5237-5252.
    [45]Kudo S,Tanimoto H,Inomata S,et al.Emissions of nonmethane volatile organic compounds from open crop residue burning in the Yangtze River Delta region,China[J].Journal of Geophysical Research Atmospheres,2014,119(12):7684-7698.
    [46]Yokelson R J,Burling I R,Gilman J B,et al.Coupling field and laboratory measurements to estimate the emission factors of identified and unidentified trace gases for prescribed fires[J].Atmospheric Chemistry&Physics,2013,13(1):89-116.
    [47]Yokelson R J,Burling I R,Urbanski S P,et al.Trace gas and particle emissions from open biomass burning in Mexico[J].Atmospheric Chemistry&Physics,2011,11(11):7321-7374.
    [48]吕子峰,郝吉明,段菁春,等.北京市夏季二次有机气溶胶生成潜势的估算[J].环境科学,2009,30(4):969-975.LüZ F,Hao J M,Duan J C,et al.Estimate of the formation potential of secondary organic aerosol in Beijing summertime[J].Environmental Science,2009,30(4):969-975.
    [49]陈文泰,邵敏,袁斌,等.大气中挥发性有机物(VOCs)对二次有机气溶胶(SOA)生成贡献的参数化估算[J].环境科学学报,2013,33(1):163-172.Chen W T,Shao M,Yuan B,et al.Parameterization of contribution to secondary organic aerosol(SOA)formation from ambient volatile organic compounds(VOCs)[J].Acta Scientiae Circumstantiae,2013,33(1):163-172.

© 2004-2018 中国地质图书馆版权所有 京ICP备05064691号 京公网安备11010802017129号

地址:北京市海淀区学院路29号 邮编:100083

电话:办公室:(+86 10)66554848;文献借阅、咨询服务、科技查新:66554700