大气气溶胶含量及其透过率初步研究
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
随着人们生活水平的提高,公众的环境意识逐渐增强。可吸入颗粒物PM10已经成为我国城市的首要污染物,PM2.5的监测数据在部分城市已经开始对公众公布。这主要是可吸入颗粒物的对人体健康的影响和对城市视觉质量的影响造成的。可吸入颗粒物对人体健康的影响主要取决于颗粒物的粒径和相应的成分;同时可吸入颗粒物能吸收和散射大部分太阳辐射,降低空气质量。
     本文研究了2011年南京北郊生活区冬季不同粒径可吸入颗粒物的含量及其透过率。首先,利用两台Anderson九级粒子撞击采样器分别于2011年11月至12月在南京北郊生活区采集可吸入颗粒物样品,再利用称重法测量不同粒径上颗粒物的含量。结果显示:大气中可吸入颗粒物的质量浓度平均值是228.65μg/m3,是国家日平均二级标准值(100μg/m。)的2.28倍左右。小于5.8μm的颗粒物占可吸入的83.03%,小于2.1μm的颗粒物占可吸入颗粒物的59.88%,小于1.1μm的颗粒物所占比例为41.74%,小于0.43μm的颗粒物所占比例为12.26%,这表明空气中细粒子污染严重。l0μm以下的颗粒物可进入鼻腔,小于7μm的微粒能进入咽喉,小于3μm的可达支气管,小于1μm的在肺泡的沉积率最高。长期居住在那里的人们将可能有大量的细小颗粒物进入肺泡、支气管和咽喉;可吸入颗粒物质量浓度在0.65-1.10m和5.80-9.0m之间有峰值,在0.65-1.10μm之间达到了最大值;而5.8-9.0μm粒径段有点不太明显。其原因是亚微米粒子数浓度较大,而粗粒子的体积正比于其尺度三次方,才导致了这两个粒径范围累积的质量浓度较大。PM10、PM2.1、PM1.1两两之间有很好的相关性。
     利用实验室组装的光学测量系统分析样品的透过率。分析得出不同粒径的透过率的结果如下:(1)细颗粒物(粒径r<2.1μm)相比于粗颗粒物(2.1     基于实验室组装的带有FLA4000+的微型光纤光谱仪测量粗颗粒物透过率,得到了粗颗粒物的透过率光谱图;同时,基于测出的透过率估算粗颗粒物的消光系数,结果表明:(1)粗颗粒物粒径越大,透过率随波长变化幅度越小,即粒径较大粗颗粒物对波长的选择性不强,对可见光的敏感性差。(2)粗颗粒物的消光系数的数量级在10-5-10-4之间,这一数值比大气中一般出现的气溶胶消光系数值在10-4-10-3之间要小一个数量级,这也说明了粗颗粒气溶胶的消光作用弱,主要原因是粗颗粒物的数浓度较小造成。
With improvement of living standards, the environmental awareness of the public is gradually increased. Particulate matter (PM10) has become the primary pollutant of our city and the monitoring data of PM2.5have begun to the public. This is mainly caused by the impact of inhalable particulate matter on human health and the urban visual quality. Inhalable particulate matter on human health effects depends on the particle size and the corresponding component. It absorbs and scatters lots of solar radiation and reduces air quality.
     This paper had surveyed the different size of inhalable particle content and its transmittance at Nanjing northern suburb of living area in winter,2011. First, FA-3impingement sampler was used to measure aerosol particle size distribution to collect the information of the atmospheric particles and the weight method was adopted to measure its content. Results showed that the average mass concentration reading was228.65μg/m3, which was about2.28times for the national two standard value (100μg/m3). On average83.03%of urban mass concentration of the inhalable particle was<5.8μm,59.88%below approximately2.1μm, and12.26%of PM10was<0.43μm, suggested that fine particle was serious in air pollution. Particulate matter less than10μm can enter the nasal cavity, less than7μm particles can enter the throat, less than3μm up to bronchial, less than1μm had the highest deposition rate in the alveoli, suggested that long-term residents have serious health effects. There existed double peaks,0.65-1.1μm and5.8-9.0μm respectively, and reached a maximum between0.65-1.1μm. The reason was that the sub-micron particle had higher number concentration and that the volume of coarse particle was proportional to the cube of the scale, which leaded to higher mass concentration. Good correlation between PM10、PM2.1and PM1.0.
     The transmittance of different size of inhalable particle was conducted by the laboratory assembly of the optical measurement system. Results showed that fine particles (particle size r<2.1μm) had smaller value than the coarse particles (2.1     The laboratory-based assembly with FLA4000+Miniature Fiber Optic Spectrometer was used to measure the transmittance of the coarse particulates, and estimated its extinction coefficient. Results showed that the greater of the coarse particulates, variation amplitude of its transmittance with the wavelength was smaller, that means the larger particle size on the wavelength selectivity lower. The magnitude of its extinction coefficient was between10-5-10-4, which was lower than the generally value between10-4-10-3, this was also explained the roles of extinction of the coarse particle aerosol weakly.
引文
[1]Harrison RM, Yin J, Mark D, et al. Studies of the coarse particle (2.5-10 μm) component in UK urban atmospheres[J]. Atmospheric Environment,2001,35(21):3667-3679.
    [2]Florig HK, Sun G, Song G. Evolution of particulate regulation in China-prospects and challenges of exposure-based control [J]. Chemosphere,2002,49(9):1163-1174.
    [3]Nam-Jun B, Yong Pyo K, Kil Choo M. Visibility study in Seoul,1993[J]. Atmospheric Environment,1996,30(13):2319-2328.
    [4]Kim KW, Kim YJ, Oh SJ. Visibility impairment during Yellow Sand periods in the urban atmosphere of Kwangju, Korea[J]. Atmospheric Environment,2001,35(30):5157-5167.
    [5]Marth E, Haselbacher-marko S, Schaffler K. A cohort study with children living in an air-polluted region-a model for public health[J]. Toxicology Letters,1996,88(1-3):155-159.
    [6]Pryor SC, Barthelmie RJ. PM10 in Canada[J]. Science of The Total Environment, 1996,177(1-3):57-71.
    [7]Maenhaut W, Francois F, Cafmeyer J, et al. Size-fractionated aerosol composition at Gent, Belgium. Results from a one-year study[J]. Nuclear Instruments and Methods in Physics Research Section B: Beam Interactions with Materials and Atoms,1996,109-110(0):476-481.
    [8]Borbely-Kiss Ⅰ, Koltay E, Szabo G. Elemental composition of rural aerosol collected in Hortobagy National Park, Hungary[J]. Journal of Aerosol Science,1996,27, Supplement 1(0): S91-S92.
    [9]Querol X, Alastuey A, Rodriguez S, et al. Monitoring of PM10 and PM2.5 around primary particulate anthropogenic emission sources[J]. Atmospheric Environment,2001,35(5): 845-858.
    [10]Wang G, Huang L, Gao S, et al. Characterization of water-soluble species of PM10 and PM2.5 aerosols in urban area in Nanjing, China[J]. Atmospheric Environment,2002,36(8): 1299-1307.
    [11]邱洪斌,王跃新,王建杰.城市街道大气颗粒物有害成分及来源的研究[J].佳木斯医学院学报,1997,(01):12-14.
    [12]唐小玲,毕新慧,陈颖军,et al.广州市空气颗粒物中烃类物质的粒径分布[J].地球化学, 2005,(05):508-514.
    [13]原福胜,马亚萍,武忠诚.不同粒径大气颗粒物中金属元素含量及其对人双核淋巴细胞微核率的影响[J].卫生研究,1999,(01):23-24.
    [14]丁文家,王稳,贾树松.空气中可吸入颗粒物及其有害成份的调查[J].中国公共卫生,1986,(01):1-4.
    [15]杨三明,张大元,陈刚才.重庆市主城区空气中颗粒物污染分析[J].重庆环境科学,2001,(05):18-20+34.
    [16]张贵英,倪邦发,田伟之,et al.粒子激发X荧光分析研究良乡大气可吸入颗粒物PM2.5的来源[J].中国原子能科学研究院年报,2005,(00):143-145.
    [17]王玉婕,强天伟.室内可吸入颗粒物的来源及其防治措施探讨[J].洁净与空调技术,2011,(04):70-72+77.
    [18]黄鹂鸣,王格慧,王荟,et al.南京市空气中颗粒物PM10、PM2.5污染水平[J].中国环境科学,2002,(04):47-50.
    [19]王荟,王格慧,黄鹂鸣,et al.南京市大气中PM(10)、PM_(2.5)日污染特征[J].重庆环境科学,2003,(05):54-56+62.
    [20]谢鸣捷,王格慧,胡淑圆,et al.南京夏秋季大气颗粒物和PAHs组成的粒径分布特征[J].中国环境科学,2008,(10):867-871.
    [21]林俊,刘卫,李燕,et al.大气气溶胶粒径分布特征与气象条件的相关性分析[J].气象与环境学报,2009,(01):1-5.
    [22]吕森林,邵龙义,TimJones, et al北京PM_(10)中矿物颗粒的微观形貌及粒度分布[J].环境科学学报,2005,(07):863-869.
    [23]赵厚银,邵龙义,王延斌,et al.北京市冬季室内空气PM_(10)微观形貌及粒度分布[J].中国环境科学,2004,(04):122-125.
    [24]邵龙义,时宗波.北京西北城区与清洁对照点夏季大气PM_(10)的微观特征及粒度分布[J].环境科学,2003,(05):11-16.
    [25]Che H, Zhang X, Li Y, et al. Relationship between horizontal extinction coefficient and PM10 concentration in Xi'an, china, during 1980-2002[J]. China Particuology,2006,4(6):327-329.
    [26]刘新罡,张远航,曾立民,et a1.广州市大气能见度影响因子的贡献研究[J].气候与环境研究,2006,(06):733-738.
    [27]张涛,陶俊,王伯光,et al.广州市春季大气颗粒物的粒径分布及能见度研究[J].中国科学院研究生院学报,2010,(03):331-337.
    [28]Keywood MD, Ayers GP, Gras JL, et al. The use of a micro-orifice uniform deposit impactor (MOUDI) to investigate relationships between PM10, PM2.5, PM1 and ultrafine particles in urban Australia[J]. Journal of Aerosol Science,1998,29, Supplement 1(0):S99-S100.
    [29]Malm WC, Day DE. Optical properties of aerosols at Grand Canyon National Park[J]. Atmospheric Environment,2000,34(20):3373-3391.
    [30]Monn C, Fuchs A, Hogger D, et al. Particulate matter less than 10μm (PM10) and fine particles less than 2.5μm (PM2.5):relationships between indoor, outdoor and personal concentrations[J]. Science of The Total Environment,1997,208(1-2):15-21.
    [31]Noordijk H. The variability of PM-10 concentrations in the Netherlands; implications for a smog warning system[J]. Journal of Aerosol Science,1996,27, Supplement 1(0):S683-S684.
    [32]Corbett SW. Asthma exacerbations during Santa Ana winds in southern California[J]. Wilderness & amp; Environmental Medicine,1996,7(4):304-311.
    [33]Lim S, Kim J, Kim T, et al. Personal exposures to PM2.5 and their relationships with microenvironmental concentrations[J]. Atmospheric Environment,2012,47(0):407-412.
    [34]Sahin UA, Onat B, Stakeeva B, et al. PM10 concentrations and the size distribution of Cu and Fe-containing particles in Istanbul's subway system[J], Transportation Research Part D: Transport and Environment,2012,17(1):48-53.
    [35]Kaur S, Nieuwenhuijsen M, Colvile R. Personal exposure of street canyon intersection users to PM2.5, ultrafine particle counts and carbon monoxide in Central London, UK[J], Atmospheric Environment,2005,39(20):3629-3641.
    [36]Kahn ME. Growing car ownership in LDCs:The impact on the environment and trade[J]. The Columbia Journal of World Business,1994,29(4):12-19.
    [37]Kim K-H, Shon Z-H. Long-term changes in PM10 levels in urban air in relation with air quality control efforts[J]. Atmospheric Environment,2011,45(19):3309-3317.
    [38]Grivas G, Chaloulakou A, Kassomenos P. An overview of the PM10 pollution problem, in the Metropolitan Area of Athens, Greece. Assessment of controlling factors and potential impact of long range transport[J]. Science of The Total Environment,2008,389(1):165-177.
    [39]Querol X, Minguillon MC, Alastuey A, et al. Impact of the implementation of PM abatement technology on the ambient air levels of metals in a highly industrialised area[J]. Atmospheric Environment,2007,41(5):1026-1040.
    [40]Amato F, Pandolfi M, Viana M, et al. Spatial and chemical patterns of PM 10 in road dust deposited in urban environment[J]. Atmospheric Environment,2009,43(9):1650-1659.
    [41]Hoek G, Mennen MG, Allen GA, et al. Concentrations of acidic air pollutants in The Netherlands[J]. Atmospheric Environment,1996,30(18):3141-3150.
    [42]Clarke AG, Azadi-Boogar GA, Andrews GE. Particle size and chemical composition of urban aerosols[J]. Science of The Total Environment,1999,235(1-3):15-24.
    [43]Pryor SC, Barthelmie RJ. REVEAL Ⅱ: Seasonality and spatial variability of particle and visibility conditions in the Fraser Valley[J]. Science of The Total Environment,2000,257(2-3): 95-110.
    [44]王永生.大气物理学[M].北京:气象出版社,1985.
    [45]刘长盛.大气辐射学[M].南京:南京大学出版社,1990.
    [46]邹进上.大气物理基础[M].北京:气象出版社,1982.
    [47]E.J.麦卡特尼.大气光学[M].北京:科学出版社,1988.
    [48]盛裴轩.大气物理学[M].北京:北京大学出版社,2003.
    [49]胡庆轩,徐秀芝,陈梅玲,et al.不同级数的ANDERSEN生物粒子采样器采样效果的比较[J].贵州环保科技,2003,(03):33-38.
    [50]周光超,赵永凯,韩杰,et al.一种基于惯性冲击原理的亚微米粒子采样器研究[J].仪器仪表学报,2010,(06):1381-1386.
    [51]章澄昌.大气气溶胶教程[M].北京:气象出版社,1995.
    [52]韩瑞梅,布仁托娅,包农建.利用全程序空白滤膜控制TSP测定误差的探讨[J].内蒙古环境保护,1998,(04):13-15.
    [53]王成云,杨左军,张伟亚,et al.用红外水分仪快速测定饲料中的水分[J].粮食与饲料工业,2003,(02):47-48.
    [54]唐洪云.投影光源ABC[J].视听技术,2005,(10):56-58.
    [55]宋佳霖,赵纪伟,应立娟,et al.具有温度控制功能的复合光物理治疗系统[J].北京生物医学工程,2008,(02):182-185.
    [56]郝沛明,兰举生,魏明冲,郝沛华.光照治疗仪的光学系统设计[J].光电子技术与信息,1995,(05):10-12.
    [57]张芳,高教波,王军,et al.光纤光谱仪绝对光谱辐射定标新技术[J].应用光学,2011,(01):101-105.
    [58]张倩,王兆均,姚其,et al.可见光光谱透雾性研究:proceedings of the中国照明论坛——绿色照明与照明节能科技研讨会,中国北京,2008[C].
    [59]沈正宪浙.一款教学用投影仪启动方式的改进[N].2008-07-06.
    [60]Pittman TB, Shih YH, Strekalov DV, et al. Optical imaging by means of two-photon quantum entanglement[J]. Physical Review A,1995,52(5):R3429-R3432.
    [61]高忠明.关于透镜的几个问题[J].延安教育学院学报,1999,(01):68-69.
    [62]Jacquez JA, Kuppenheim HF. Theory of the Integrating Sphere[J]. J Opt Soc Am,1955,45(6): 460-466.
    [63]Goebel DG. Generalized Integrating-Sphere Theory[J]. Appl Opt,1967,6(1):125-128.
    [64]Finkel MW. Integrating sphere theory[J]. Optics Communications,1970,2(1):25-28.
    [65]高学燕,周殿华,周山,et al.积分球的光功率波形变换理论[J].光学学报,2002,(04):465-469.
    [66]韩永辉,徐可欣,贺忠海,et al.单积分球测量牛奶光学参数[J].仪器仪表学报,2003,(S 1):437-438+444.
    [67]杨臣华.激光与红外技术手册[M].北京:国防工业出版社,1990.
    [68]王瑞斌,王明霞,安华.我国环境空气质量标准与国外相应标准的比较[J].环境科学研究,1997,(06):38-42.
    [69]Pless-Mulloli T, King A, Howel D, et al. PM10 levels in communities close to and away from opencast coal mining sites in Northeast England[J]. Atmospheric Environment,2000,34(19): 3091-3101.
    [70]McMurry PH. A review of atmospheric aerosol measurements[J]. Atmospheric Environment, 2000,34(12-14):1959-1999.
    [71]Tearle SP, Sanderson WJH. Monitoring of PM10 by near forward light scattering photometry[J]. Journal of Aerosol Science,1998,29(1-2):229.
    [72]杨复沫,贺克斌,马永亮,et al.北京PM_(2.5)浓度的变化特征及其与PM_(10),TSP的关 系[J].中国环境科学,2002,(06):27-31.
    [73]王淑英,张小玲.北京地区PM10污染的气象特征[J].应用气象学报,2002,(S1):177-184.
    [74]于建华,虞统,魏强,et al.北京地区PM_(10)和PM_(2.5)质量浓度的变化特征[J].环境科学研究,2004,(01):45-47.
    [75]蔡旭晖,张睿,宋宇,et al.北京地区大气PM10和SO_2的背景浓度分析[J].气候与环境研究,2004,(03):445-453.
    [76]赵越,潘钧,张红远,et al.北京地区大气中可吸入颗粒物的污染现状分析[J].环境科学研究,2004,(01):67-69.
    [77]刘阳生,陈睿,沈兴兴,et al.北京冬季室内空气中TSP,PM_(10),PM_(2.5)和PM 1污染研究[J].应用基础与工程科学学报,2003,(03):255-265.
    [78]李金娟,肖正辉,杨书中,et al.北京和部分奥运城市可吸入颗粒物污染特征分析[J].环境科学动态,2004,(03):26-28.
    [79]王淑兰,柴发合,张远航,et al.成都市大气颗粒物污染特征及其来源分析[J].地理科学,2004,(04):488-492.
    [80]马雁军,刘宁微,王扬锋.辽宁冬季城市空气质量分布状况综合研究[J].气象与环境学报,2007,(03):15-18.
    [81]冯茜丹,党志,王焕香,et al. PM_(10)中重金属的分布及其在模拟酸雨中的释放[J].环境科学,2006,(12):2386-2391.
    [82]李建军,沈振兴,同帜,et al.西安冬春季PM_(10)中碳气溶胶的昼夜变化特征[J].环境科学,2009,(05):1506-1513.
    [83]吴国平,胡伟,滕恩江,et al.我国四城市空气中PM_(2.5)和PM_(10)的污染水平[J].中国环境科学,1999,(02):133-137.
    [84]Monn C, Fuchs A, Kogelschatz D, et al. Comparison of indoor and outdoor concentrations of PM-10 and PM-2.5[J]. Journal of Aerosol Science,1995,26, Supplement 1(0):S515-S516.
    [85]Junker C, Jennings SG, Kleefeld S, et al. PM10 concentration measurements in two urban centres and at two remote sites in Ireland[J]. Journal of Aerosol Science,2000,31, Supplement 1(0):516-517.
    [86]Kleefeld S, Jennings SG. Analysis of PM2.5 particulate mass concentrations during 1999 at Mace Head[J]. Journal of Aerosol Science,2000,31, Supplement 1(0):731-732.
    [87]Yli-Tuomi T, Raunemaa T. PM10 concentrations in urban sites in Finland[J]. Journal of Aerosol Science,1997,28, Supplement 1(0):S233-S234.
    [88]Mark D, Yin J, Harrison RM, et al. Measurements of PM10, PM2.5 particles at four outdoor sites in the UK[J]. Journal of Aerosol Science,1998,29, Supplement 1(0):S95-S96.
    [89]王广华,位楠楠,刘卫,et al.上海市大气颗粒物中有机碳(OC)与元素碳(EC)的粒径分布[J].环境科学,2010,(09):1993-2001.
    [90]Pakkanen TA, Kerminen V-M, Ojanen CH, et al. Atmospheric black carbon in Helsinki[J]. Atmospheric Environment,2000,34(9):1497-1506.
    [91]Man CK, Shih MY. Identification of sources of PM10 aerosols in Hong Kong by wind trajectory analysis [J]. Journal of Aerosol Science,2001,32(10):1213-1223.

© 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