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1.
Ozone layer depletion implies the enhancement of solar ultraviolet radiation at the earth's surface. However, aerosol contributes to the scattering of solar radiation and leads to the reduction of UV-B radiation on the ground. In this paper, the model calculation shows that due to effects of atmospheric ozone and aerosol UV-B radiation in Beijing in the past decade has decreased with the annual change rate of 0.7%, which is probably approximate to the measured values. The effects of three scenarios for long-term changes in atmospheric ozone and aerosol concentrations on UV-B radiation reaching the ground in are also discussed.  相似文献   

2.
Sulfate, nitrate and ammonium(SNA) are the dominant species in secondary inorganic aerosol, and are considered an important factor in regional haze formation. Size-fractionated aerosol particles for a whole year were collected to study the size distribution of SNA as well as their chemical species in Shanghai. SNA mainly accumulated in fine particles and the highest average ratio of SNA to particulate matter(PM) was observed to be 47% in the fine size fraction(0.49–0.95 μm). Higher sulfur oxidation ratio and nitrogen oxidation ratio values were observed in PM of fine size less than 0.95 μm. Ion balance calculations indicated that more secondary sulfate and nitrate would be generated in PM of fine size(0.49–0.95 μm). Sulfur K-edge X-ray absorption near-edge structure(XANES) spectra of typical samples were analyzed. Results revealed that sulfur mainly existed as sulfate with a proportion(atomic basis) more than 73% in all size of PM and even higher at 90% in fine particles. Sulfate mainly existed as(NH4)2SO4 and gypsum in PM of Shanghai. Compared to non-haze days, a dramatic increase of(NH4)2SO4 content was found in fine particles on haze days only, which suggested the promoting impact of(NH4)2SO4 on haze formation. According to the result of air mass backward trajectory analysis, more(NH4)2SO4 would be generated during the periods of air mass stagnation. Based on XANES, analysis of sulfate species in size-fractionated aerosol particles can be an effective way to evaluate the impact of sulfate aerosols on regional haze formation.  相似文献   

3.
The role of atmospheric aerosol composition in climate change   总被引:1,自引:0,他引:1  
The chemical composition of atmospheric aerosols has been investigated. Contributions ofsulfate and soot in aerosols to the atmospheric extinction are studied. Discussions are made on the problems of aerosol emitted from volcano, forest fires in northern China, 1987 and oil field fires in Kuwait, 1991. It is indicated that the changes in concentration, particle size, and chemical composition of aerosol after those events could have impacts on the climate change either regionally or globally and that the impact of aerosol particles on climate change could compensate for some temperature increase caused by greenhouse gases and the increase of surface intensity of ultraviolet radiation due to ozone layer depletion.  相似文献   

4.
Pure nano-Al13 and aggregates at various concentrations were prepared to examine the particle size e ect of coagulation with inorganic polymer flocculant. The property and stability of various species formed were characterized using Infrared, 27Al-NMR, photo correlation spectroscopy (PCS), and Ferron assay. Results showed that concentration and temperature exhibited di erent roles on the stability of Al13. The quantity of Alb species analyzed by ferron assay in the initial aging period corresponded well with that of Al13, which has been confirmed in a dimension range of 1–2 nm by PCS. Al13 solutions at high concentrations (0.5–2.11 mol/L) were observed to undergo further aggregation with aging. The aggregates with a wide particle size distribution would contribute to the disappeared/decreased Al13 basis on the 27Al-NMR spectrum, whereas a part of Al13 would still remain as Alb. At low concentrations, Al13 solution was quite stable at normal temperature, but lost its stability quickly when heating to 90°C.  相似文献   

5.
Size-classified daily aerosol mass concentrations and concentrations of water-soluble inorganic ions were measured in Hefei,China,in four representative months between September 2012 and August 2013.An annual average mass concentration of 169.09μg/m~3 for total suspended particulate(TSP)was measured using an Andersen Mark-II cascade impactor.The seasonal average mass concentration was highest in winter(234.73μg/m~3)and lowest in summer(91.71μg/m~3).Water-soluble ions accounted for 59.49%,32.90%,48.62%and 37.08%of the aerosol mass concentration in winter,spring,summer,and fall,respectively,which indicated that ionic species were the primary constituents of the atmospheric aerosols.The four most abundant ions were NO_3~-,SO_4~(2-),Ca~(2+) and NH_4~+.With the exception of Ca~(2+),the mass concentrations of water-soluble ions were in an intermediate range compared with the levels for other Chinese cities.Sulfate,nitrate,and ammonium were the dominant fine-particle species,which were bimodally distributed in spring,summer and fall;however,the size distribution became unimodal in winter,with a peak at 1.1–2.1μm.The Ca~(2+) peak occurred at approximately 4.7–5.8μm in all seasons.The cation to anion ratio was close to 1.4,which suggested that the aerosol particles were alkalescent in Hefei.The average NO_3~-/SO_4~(2-)mass ratio was 1.10 in Hefei,which indicated that mobile source emissions were predominant.Significant positive correlation coefficients between the concentrations of NH_4~+ and SO_4~(2-),NH_4~+ and NO_3~-,SO_4~(2-)and NO_3~-,and Mg~(2+) and Ca~(2+) were also indicated,suggesting that aerosol particles may be present as(NH_4)_2SO_4,NH_4HSO_4,and NH_4NO_3.  相似文献   

6.
Size-resolved aerosol samples were collected by MOUDI in four seasons in 2007 in Beijing. The PM10 and PM1.8mass concentrations were 166.0 ± 120.5 and 91.6 ± 69.7 μg/m~3, respectively,throughout the measurement, with seasonal variation: nearly two times higher in autumn than in summer and spring. Serious fine particle pollution occurred in winter with the PM1.8/PM10 ratio of 0.63, which was higher than other seasons. The size distribution of PM showed obvious seasonal and diurnal variation, with a smaller fine mode peak in spring and in the daytime. OM(organic matter = 1.6 × OC(organic carbon)) and SIA(secondary inorganic aerosol) were major components of fine particles, while OM, SIA and Ca_2+were major components in coarse particles. Moreover, secondary components, mainly SOA(secondary organic aerosol) and SIA,accounted for 46%–96% of each size bin in fine particles, which meant that secondary pollution existed all year. Sulfates and nitrates, primarily in the form of(NH_4)_2SO_4, NH_4NO_3, Ca SO_4, Na_2SO_4 and K_2SO_4, calculated by the model ISORROPIA II, were major components of the solid phase in fine particles. The PM concentration and size distribution were similar in the four seasons on non-haze days, while large differences occurred on haze days, which indicated seasonal variation of PM concentration and size distribution were dominated by haze days. The SIA concentrations and fractions of nearly all size bins were higher on haze days than on non-haze days, which was attributed to heterogeneous aqueous reactions on haze days in the four seasons.  相似文献   

7.
Chemical characteristics of size-resolved aerosols in winter in Beijing   总被引:4,自引:0,他引:4  
Size-resolved aerosols were continuously collected by a Nano Sampler for 13 days at an urban site in Beijing during winter 2012 to measure the chemical composition of ambient aerosol particles. Data collected by the Nano Sampler and an ACSM(Aerodyne Aerosol Chemical Speciation Monitor) were compared. Between the data sets,similar trends and strong correlations were observed,demonstrating the validity of the Nano Sampler. PM10 and PM2.5concentrations during the measurement were 150.5 ± 96.0 μg/m3(mean ± standard variation)and 106.9 ± 71.6 μg/m3,respectively. The PM2.5/PM10 ratio was 0.70 ± 0.10,indicating that PM2.5dominated PM10. The aerosol size distributions showed that three size bins of 0.5–1,1–2.5 and 2.5–10 μm contributed 21.8%,23.3% and 26.0% to the total mass concentration(TMC),respectively. OM(organic matter) and SIA(secondary ionic aerosol,mainly SO42-,NO3-and NH4+) were major components of PM2.5. Secondary compounds(SIA and secondary organic carbon) accounted for half of TMC(about 49.8%) in PM2.5,and suggested that secondary aerosols significantly contributed to the serious particulate matter pollution observed in winter. Coal burning,biomass combustion,vehicle emissions and SIA were found to be the main sources of PM2.5. Mass concentrations of water-soluble ions and undetected materials,as well as their fractions in TMC,strikingly increased with deteriorating particle pollution conditions,while OM and EC(elemental carbon) exhibited different variations,with mass concentrations slightly increasing but fractions in TMC decreasing.  相似文献   

8.
Sources of Pb pollution in the local atmosphere together with Pb species, major ions, and heavy metal concentrations in a size-fractionated aerosol sample from Higashi-Hiroshima(Japan) have been determined by X-ray absorption near-edge structure(XANES) spectroscopy, ion chromatography, and ICP-MS/AES, respectively. About 80% of total Pb was concentrated in fine aerosol particles. Lead species in the coarse aerosol particles were PbC2O4, 2PbCO3·Pb(OH)2, and Pb(NO3)2, whereas Pb species in the fine aerosol particles were PbC2O4, PbSO4, and Pb(NO3)2. Chemical speciation and abundance data suggested that the source of Pb in the fine aerosol particles was different from that of the coarse ones. The dominant sources of Pb in the fine aerosol particles were judged to be fly ash from a municipal solid waste incinerator and heavy oil combustion. For the coarse aerosol particles, road dust was considered to be the main Pb source. In addition to Pb species, elemental concentrations in the aerosols were also determined. The results suggested that Pb species in size-fractionated aerosols can be used to identify the origin of aerosol particles in the atmosphere as an alternative to Pb isotope ratio measurement.  相似文献   

9.
Aerosol samples were collected at Lin'an, a background site of Yangtze River Delta(YRD).Morphology, size, composition, and mixing state of individual aerosol particles were characterized by transmission electron microscopy(TEM) coupled with energy dispersive X-ray spectroscopy(EDS), and the soluble ions of PM_(1.0) were studied by aerosol mass spectrometer(AMS). The daily average AMS mass concentrations of sulfate, nitrate, and ammonium were about 5.8, 8.6, and 5.6 μg/m~3, respectively. Individual aerosol particles were classified into seven types: S-rich, K-rich, organic matter(OM), soot, fly ash, metal, and mineral. S-rich particles were dominant in all size bins, and 51%(by number) of S-rich particles were internally mixed with other particles. The fraction of organic coating particles was 13.7% in morning, 25.2% in afternoon, and 11% in evening, suggesting that the strong photochemical process during afternoon produced more secondary organic aerosols(SOA) on the surface of inorganic particles. Fly ash and metal particles were abundant during the day, suggesting the influence of emissions from coal-fired power plants and steel plants. The results indicate that the intense industrial emissions in the YRD significantly transported to the background areas. PM_(2.5) concentration may be lower in background air than in urban air but complex mixing state of aerosol particles indicates that the long-range transported particles substantially influenced the background air quality.  相似文献   

10.
In order to understand the size distribution and the main kind of heavy metals in particulate matter on the lead and zinc smelting affected area, particulate matter(PM) and the source samples were collected in Zhuzhou, Hunan Province from December 2011 to January 2012 and the results were discussed and interpreted. Atmospheric particles were collected with different sizes by a cascade impactor. The concentrations of heavy metals in atmospheric particles of different sizes, collected from the air and from factories, were measured using an inductively coupled plasma mass spectrometry(ICP-MS). The results indicated that the average concentration of PM, chromium(Cr), arsenic(As), cadmium(Cd) and lead(Pb) in PM was177.3 ± 33.2 μg/m~3, 37.3 ± 8.8 ng/m~3, 17.3 ± 8.1 ng/m~3, 4.8 ± 3.1 ng/m~3 and 141.6 ± 49.1 ng/m~3,respectively. The size distribution of PM displayed a bimodal distribution; the maximum PM size distribution was at 1.1–2.1 μm, followed by 9–10 μm. The size distribution of As, Cd and Pb in PM was similar to the distribution of the PM mass, with peaks observed at the range of1.1–2.1 μm and 9–10 μm ranges while for Cr, only a single-mode at 4.7–5.8 μm was observed. PM(64.7%), As(72.5%), Cd(72.2%) and Pb(75.8%) were associated with the fine mode below 2.1 μm,respectively, while Cr(46.6%) was associated with the coarse mode. The size distribution characteristics, enrichment factor, correlation coefficient values, source information and the analysis of source samples showed that As, Cd and Pb in PM were the typical heavy metal in lead and zinc smelting affected areas, which originated mainly from lead and zinc smelting sources.  相似文献   

11.
降雨过程中气溶胶湿沉降的数值模拟   总被引:8,自引:2,他引:8  
赵海波  郑楚光 《环境科学学报》2005,25(12):1590-1596
为了参数化降雨湿去除气溶胶的过程,首先定量计算了雨滴和气溶胶的碰撞效率与它们尺度之间的依存关系,以及雨滴尺度谱满足对数正态分布时气溶胶的清除系数与其尺度的依存关系;然后利用多重Monte Carlo算法模拟了降雨过程中气溶胶尺度谱的时间演变过程,考察了气溶胶湿沉降过程与降雨类型和雨强的相关性.当雨滴尺度谱和气溶胶尺度谱均满足对数正态分布时,数值模拟的结果表明,典型的小雨、中雨和大雨过程对中等尺度气溶胶的湿去除效果均不理想,但都可以有效地湿去除大尺度气溶胶和小尺度气溶胶;3种降雨类型对大尺度气溶胶的湿去除效果均依次好于小尺度气溶胶和中等尺度气溶胶;对于任何尺度的气溶胶,雨强的增加将有利于其湿沉降.  相似文献   

12.
中国3个AERONET站点气溶胶大小的识别及特征分析   总被引:1,自引:0,他引:1  
AngstrOm波长指数α是判断气溶胶粒子大小的重要参数,但当气溶胶尺度分布不满足Junge分布时,仅用α不能很好的反映气溶胶粒子的尺度信息.利用Mie散射理论和AERONET站点实测资料分析说明在0.75α1.7区间内,结合AOD谱曲率a2可以得到更详细的粒子尺度信息.对SACOL、香河和太湖站,当a2–0.4时,气溶胶以细粒子占主导地位,Vfine/Vtotal0.6;当a20.3时,多以粗粒子为主,Vfine/Vtotal0.4.利用Gobbi气溶胶图解法分析显示SACOL站AOD的大值主要是由于沙尘气溶胶的影响造成的;香河站沙尘和细粒子气溶胶都会产生大值AOD,并且图解法可以很好的区分这两种情况;太湖站受沙尘的影响较小,大值AOD绝大多数是由于细粒子气溶胶造成的.  相似文献   

13.
基于AERONET网站中多个站点2006~2018年的观测数据,利用气溶胶光学厚度和气溶胶相对光学厚度,对中国华北北京、华东太湖、华南香港、西北SACOL多个站点的气溶胶进行分类,研究了中国地区典型站点气溶胶类型的时空变化特征.结果表明,我国华北、华南、华东区域站点以大陆型和城市工业型气溶胶为主,西北区域站点以大陆型气溶胶为主.气溶胶类型占比存在明显的年际变化,我国华北、华东区域站点大陆型气溶胶占比总体呈上升趋势,次大陆型溶胶占比呈下降趋势,其中华东区域站点年际变化较为突出,大陆型气溶胶占比年均上升2.78%,城市工业型气溶胶占比年均下降1.86%;华南区域站点大陆型气溶胶占比年均上升0.78%,且城市工业型气溶胶占比年均下降0.66%;而西北区域作为沙尘的主要源区,沙尘气溶胶变化最为显著,占比年均上升0.51%.我国不同区域气溶胶类型季节变化差异较大,春季华北、华东、西北区域均出现沙尘气溶胶,且西北区域尤为突出(占比19%);华北区域城市工业型和大陆型气溶胶占比分别在夏、冬两季出现大值,华东区域城市工业型气溶胶在夏、秋两季占比较高,华南区域城市工业型气溶胶在春季占比最多(57%),西北区域大陆型气溶胶在夏、秋两季占比高达83%.  相似文献   

14.
半干旱区沙尘天气对0010~10 μm沙尘气溶胶分布的影响   总被引:2,自引:2,他引:0  
利用WPS粒子谱仪对内蒙古朱日和背景天气及沙尘天气的气溶胶数浓度进行了观测,研究了不同天气背景下沙尘气溶胶数浓度及谱分布特征. 结果表明:在背景天气和沙尘天气下,0.010~0.020,0.021~0.100,0.101~1.000,1.001~2.500 μm等粒径段的气溶胶数浓度差别较大;沙尘天气对各粒径段,尤其是大于1.0 μm的气溶胶数浓度影响较大,沙尘暴过程中 1.001~2.500 μm粒径段的气溶胶数浓度约为背景天气的35倍;各粒径段气溶胶数浓度在不同天气背景下的日变化规律有所不同,受气象要素的影响较大. 对沙尘气溶胶谱分布的分析可知,沙尘暴发生前后1 h的沙尘气溶胶谱型均符合Lorentz分布,背景天气下同时段的沙尘气溶胶谱型也符合Lorentz分布;沙尘天气下沙尘气溶胶谱型在沙尘暴发生前1 h的主峰值比背景天气高1个数量级,沙尘暴发生后1 h的峰值半径明显移向大粒子.  相似文献   

15.
马丽新  齐虹  孙霞忠 《环境科学学报》2020,40(10):3549-3558
近年来气溶胶污染被社会各界密切关注.大气气溶胶的粒径分布和污染物组成特征研究是探究大气气溶胶污染成因的基础,同时也是准确评估人体暴露于气溶胶污染导致的健康风险的关键.多级采样器可分粒径采集大气气溶胶,通过模拟人体呼吸系统进而准确量化大气气溶胶组分被吸入后在人体的沉积部位和沉积量,从而被应用至大气气溶胶粒径分布特征和人体健康风险评估的研究中.本文介绍了大气气溶胶粒径分级方法,探讨了应用多级采样器在气溶胶粒径分布研究中存在的主要问题及解决方案,并综述了大气气溶胶粒径分布特征和人体呼吸系统暴露评估的研究进展,最后结合当前的研究现状对大气气溶胶在粒径分级和人体健康风险研究领域的未来发展方向进行了展望.  相似文献   

16.
利用CALIOP数据和SBDART(Santa Barbara DISORT Atmospheric Radiative Transfer)辐射传输模式研究了2013~2016年华北地区8d沙尘天气气溶胶及其直接辐射强迫垂直分布特征,分析了气溶胶垂直分布和光学特性对直接辐射强迫的影响.结果表明,气溶胶集中分布在地表及以上3km范围,其中纯净沙尘型和污染沙尘型气溶胶位于上层,污染大陆型气溶胶和烟雾位于下层.大气层顶、地表和大气层的日均气溶胶直接辐射强迫分别是-38.41~-88.44,-74.03~-225.86,9.06~137.42W/m2.0~8km高度范围气溶胶直接辐射强迫是负值,且随着高度的增加绝对值逐渐减小.气溶胶垂直分布对大气层顶、地表和大气层的直接辐射强迫影响较小,但对直接辐射强迫垂直分布影响较大,由气溶胶廓线差异造成的同一高度层气溶胶直接辐射强迫最大差值能达到31.18W/m2.气溶胶光学厚度和单次散射反照率对直接辐射强迫影响明显.消光能力相同时,吸收性气溶胶对短波太阳光的衰减作用大于散射性气溶胶,后向散射比例大的气溶胶大于后向散射比例小的气溶胶.  相似文献   

17.
华北地区沙尘天气垂直气溶胶直接辐射强迫   总被引:1,自引:0,他引:1  
利用CALIOP数据和SBDART(Santa Barbara DISORT Atmospheric Radiative Transfer)辐射传输模式研究了2013~2016年华北地区8d沙尘天气气溶胶及其直接辐射强迫垂直分布特征,分析了气溶胶垂直分布和光学特性对直接辐射强迫的影响.结果表明,气溶胶集中分布在地表及以上3km范围,其中纯净沙尘型和污染沙尘型气溶胶位于上层,污染大陆型气溶胶和烟雾位于下层.大气层顶、地表和大气层的日均气溶胶直接辐射强迫分别是-38.41~-88.44,-74.03~-225.86,9.06~137.42W/m2.0~8km高度范围气溶胶直接辐射强迫是负值,且随着高度的增加绝对值逐渐减小.气溶胶垂直分布对大气层顶、地表和大气层的直接辐射强迫影响较小,但对直接辐射强迫垂直分布影响较大,由气溶胶廓线差异造成的同一高度层气溶胶直接辐射强迫最大差值能达到31.18W/m2.气溶胶光学厚度和单次散射反照率对直接辐射强迫影响明显.消光能力相同时,吸收性气溶胶对短波太阳光的衰减作用大于散射性气溶胶,后向散射比例大的气溶胶大于后向散射比例小的气溶胶.  相似文献   

18.
上海地区光化学污染中气溶胶特征研究   总被引:7,自引:0,他引:7  
利用上海地区2011~2013年9个大气成分及气象观测站点臭氧(O3)、颗粒物(PM1、PM2.5、PM10)、气溶胶粒子谱观测资料以及气象数据,分析了上海不同功能区臭氧超标时的频率分布及各类污染物浓度特征.结果表明,上海地区夏季光化学污染严重,周边城区臭氧污染要明显高于中心城区,不同功能区污染情况差异较大,金山化工区和崇明生态岛光化学污染较为严重.通过分析光化学污染前后气溶胶变化特征可知,当出现光化学污染时,各站气溶胶浓度明显升高,特别是PM1浓度增加显著,且PM1/PM2.5比未出现臭氧污染时的比例明显升高.表明随着光化学反应的增强,二次气溶胶生成明显增多.因此可将PM1作为光化学污染的判定指标之一.  相似文献   

19.
为探究南京地区雾过程对气溶胶粒子化学组成和尺度分布的影响,在2017年冬季的雾观测中平行收集了3级分档雾水和分粒径气溶胶样品,并对雾微物理量与气溶胶谱分布、3级分档雾水与雾前、雾中、雾后分粒径气溶胶化学组成对比分析。结果表明,2017年冬季南京第1次雾过程的雾滴液态水含量随粒径分布为不对称“V”型,最低值位于7μm处,第2次雾过程的雾滴液态水含量随粒径分布为3峰型,峰值分别位于5,15,21.5μm处。在雾形成、发展阶段,粒径<0.33μm的气溶胶质量浓度降低,粒径0.38μm气溶胶质量浓度升高,雾成熟阶段,气溶胶粒子质量浓度在全粒径段均达到最低,粒径0.38μm的气溶胶质量浓度大幅降低,与雾前相比,雾后气溶胶质量浓度峰值向大粒径方向移动。雾前,气溶胶水溶性离子组分富集在粒径<0.43μm的小粒子中,随着雾过程进行,成核作用和吸湿增长使得水溶性离子向较大粒径段富集。雾中新生成的气溶胶随着雾滴的蒸发被释放,导致雾后NO3-、SO42-和NH4+浓度升高。较小粒径的气溶胶中和率更高,雾形成初期的新生雾滴酸性较强,随着雾过程的进行逐渐中和,雾水pH值逐渐升高。  相似文献   

20.
利用Andersen空气微生物采样器采集青岛市不同空气质量下的可培养生物气溶胶,分析了其浓度和粒径分布特征,并利用Spearman’s相关性分析了可培养生物气溶胶浓度和空气质量指数中的颗粒物质量浓度〔ρ(PM10)、ρ(PM2.5)〕、气体污染物质量浓度〔ρ(O3)、ρ(SO2)、ρ(NO2)〕和气象参数(温度、相对湿度、风速)之间的关系.结果表明:可培养真菌和细菌气溶胶浓度范围分别为133~1 113和13~212 CFU/m3.真菌气溶胶浓度与ρ(SO2)、ρ(PM10)、ρ(PM2.5)均呈正相关,而与相对湿度呈显著负相关(P<0.05).细菌气溶胶浓度与ρ(NO2)、ρ(SO2)呈负相关,而与ρ(O3)、温度呈正相关.风速对可培养生物气溶胶浓度的影响较小.以AQI(空气质量指数)中ρ(PM10)为依据,将研究时间段空气质量划分为4个空气污染等级.在不同污染等级下,真菌气溶胶均呈对数正态分布,粒径主要分布于2.1~4.7 μm.低污染时细菌气溶胶呈偏态分布(粒径>4.7 μm),高污染时粒径分布发生改变.初步推断,随着空气污染等级的升高,可培养生物(真菌+细菌)气溶胶总浓度增加,但单位颗粒物上的浓度变化较稳定.ρ(PM10)是影响可培养生物气溶胶浓度及粒径分布的主要因素.   相似文献   

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