首页 | 本学科首页   官方微博 | 高级检索  
相似文献
 共查询到19条相似文献,搜索用时 62 毫秒
1.
对2008年05至11月淮南市5个采样点大气可吸入颗粒物(PM10)样品进行分析,总结了研究区内PM10及其中16种PAHs的浓度特征、季节变化规律和来源解析。研究区内16种PAHs浓度总和的范围在15.20~111.58ng.m-3之间,平均值为40.40ng.m-3,中位数为33.34ng.m-3。PAHs总量的季节变化与采样时环境温度显示出较好的负相关性,即秋季>春季>夏季;运用多环芳烃比值综合判断,淮南市大气PM10中PAHs主要以燃煤和机动车尾气混合来源为主,石油源和木材燃烧来源的贡献较小。  相似文献   

2.
淮南市秋季大气可吸入颗粒物中多环芳烃的污染特征分析   总被引:4,自引:4,他引:0  
2007年秋季在淮南市五个采样点采集大气可吸入颗粒物样品,用色谱-质谱法分析多环芳烃中16种优控污染物.结果显示,交通区PAHs浓度最高;PAHs以四环为主,二环所占比例最小;PM10与ΣPAHs成显著正相关关系,与苯并[a]芘成显著正相关;采用比值法对准南市PM10中的PAHs进行来源分析,得到PAHs主要来源于交通源及燃煤排放.  相似文献   

3.
重庆市春季不同功能区PM10中多环芳烃的污染特征   总被引:2,自引:2,他引:0  
2012年4月在重庆市4个不同功能区连续10 d同步采集了大气PM10环境样品,利用气相色谱-质谱法分析测定美国环保局16种优控多环芳烃(PAHs).结果显示,在重庆主城区PM10中检测到16种优控PAHs,总浓度(∑PAHs)范围为31.68~ 189.31 ng/m3,平均浓度为108.05 ng/m3.各个功能区大气PM10中PAHs总浓度存在明显差别:交通区(沙坪坝七中)154.47 ng/m3>工业区(大渡口区政府)132.92 ng/m3>居民区(南岸工商大学)105.58 ng/m3>对照区(缙云山风景区)39.16 ng/m3.根据典型污染来源中PAHs的特征比值综合判断,重庆市春季大气中PM10主要来源于燃煤和交通污染的混合源.  相似文献   

4.
在克拉玛依市中心城区布设4个采样点,在供暖期和非供暖期分别同步采集4个点位大气中不同粒径的颗粒物,采用HPLC进行分析并计算2个采样期内PM_(10)和PM_(2.5)中多环芳烃(PAHs)的浓度和种类。结果表明:中心城区供暖期PM_(10)中PAHs浓度为56.19 ng/m3,PM_(2.5)中PAHs浓度为48.85 ng/m3;中心城区非供暖期PM_(10)中PAHs浓度为18.86 ng/m~3,PM_(2.5)中PAHs浓度为14.53 ng/m~3。不同采样期PM_(10)和PM_(2.5)中PAHs浓度变化趋势相同,均为供暖期明显大于非供暖期。中心城区供暖期大气颗粒物吸附的PAHs以4环以下的组份为主,非供暖期则是5~6环的高环数组份偏多。分析结果表明克拉玛依市中心城区供暖期颗粒物中PAHs来源于燃煤排放叠加机动车排放,与中心城区集中供热锅炉关系密切;非供暖期则是以机动车排放污染为主。  相似文献   

5.
焦炉工人PAHs空气日均暴露浓度分析   总被引:5,自引:0,他引:5  
用个体采样器对100名受试者进行了可吸入颗粒物和气态样品的24h跟踪采集,并通过梯度洗脱一反相HPLC/可编程序荧光检测法定量分析了样品中14种多环芳烃。结果表明,不同受试人员多环芳烃空气日均暴露浓度存在很大差异,其中焦炉工人受多环芳烃中BaP空气日均暴露浓度为0.5μg/m^3~1.7μg/m^3,炼纲厂工作人员和清洁区办公人员的BaP空气日均暴露浓度分别为0.02μg/m^3和0.01μg/m^3。不同受试人员多环芳烃空气日均暴露在PM10及气相中的分配比例也略有不同,焦炉工人的BaP空气日均暴露浓度有近99%来自PM10,一般人群为93%左右。指出2环、3环多环芳烃主要以气态形式存在,4环至6环多环芳烃主要分布在PM10中。  相似文献   

6.
杭州市大气细颗粒物PM_(2.5)中多环芳烃含量特征研究   总被引:5,自引:0,他引:5  
按季节对杭州市大气细颗粒物PM2.5中16种多环芳烃(PAHs)的含量在2006年进行了为期一年(样本数n=47)的测定分析.研究表明,杭州市大气PM2.5中PAHs总浓度为40.66ng/m3,以中环或高环为主,分别占总PAHs的32.23%和47.6%;云栖点位(位于风景名胜区内)PM2.5中PAHs浓度高于朝晖点位(位于商业居民混合区);季节变化呈现春季高,秋季低的特点;PM2.5中苯并[a]芘等效毒性(BEQ)为4.50;PM2.5中PAHs的来源不是单一的.  相似文献   

7.
通过采集了2004~2006年北京市昌平区四个季节中大气PM10样品,采用超声抽提方法,使用GC/MS分析了该区PAHs含量和组成.结果显示,三年中四个季度的18种PAHs总量范围分别为21.64~656.39ng/m3、31.94~164.33ng/m3和7.294~209.3ng/m3,其中致癌性极强的苯并[a]芘含量范围为2.69~36.95 ng/m3、1.44~6.6ng/m3和0.256~8.625ng/m1,其变化趋势与PAHs总量有较好的相关性.PAHs的浓度是冬季>秋季>夏季>春季,这与夏季时雨水冲刷和阳光照射强度大导致PAHs光解,冬季时燃煤排放大等影响因素有关.文章还使用多种方法判断昌平区大气PM10中的PAHs主要来源于燃煤和汽车尾气,其它污染源贡献较小.  相似文献   

8.
采用气相色谱-质谱联用仪定量分析2016年沈阳市PM_(2.5)中16种多环芳烃(PAHs)的质量浓度,探讨其时空分布特征,并解析PAHs的来源。结果表明:沈阳市PAHs的平均质量浓度为71. 5 ng/m3,其中3环、4环PAHs分别占31. 3%和48. 8%;采暖期PAHs浓度明显高于非采暖期,中心城区高于周边。总毒性当量浓度平均值为8. 05 ng/m3。特征比值法和主成分分析法解析的PAHs来源基本一致,主要为燃烧源、石油挥发源和工业生产源,贡献率分别为70. 11%、14. 19%和10. 74%。  相似文献   

9.
通过采集淮南市6个功能区四季的PM_(2.5)样品,运用GC-MS仪测定样品中PAHs含量并分析其主要来源。结果表明:该市PM_(2.5)中PAHs质量浓度年均值为31.06 ng/m~3,呈现冬季污染程度最重,夏季最轻,采矿区商业区工业区文教区居民区对照区的特征;夏季PAHs以3环和4环为主,春、秋、冬季以4环、5环和6环为主;6个功能区均以4环PAHs为主;PAHs主要来源为煤燃烧、机动车尾气排放、生物质燃烧及焦炉挥发,其中燃煤和机动车尾气污染贡献最大。  相似文献   

10.
利用自制被动采样装置,在2011年秋冬季对南京市部分地区室内空气中5种气态多环芳烃(PAHs)(萘、苊烯、苊、芴、菲)进行了为期100d的连续采样检测,被动采样器的采样速率为0.012m3/d,5种PAHs的回收率在63%~105%之间,方法检出限在1.1~2.4ng范围内。结果表明,南京市5处不同室内环境空气中萘的浓度最高,占总量的90%以上。室内环境空气中5种PAHs的总浓度为230~1564ng/m3。住宅内人体对5种PAHs的暴露速率为479~560ng/h。  相似文献   

11.
太原市气悬颗粒物上多环芳烃的测量与分布研究   总被引:6,自引:0,他引:6  
2 0 0 1年 3月下旬 ,在太原市建成区均匀布设 1 5个网格点 ,利用新型便携式仪器 ,连续 5天监测了各点大气颗粒物上多环芳烃 (PPAHs)的浓度。结果表明 ,PPAHs浓度范围为 3 6ng/m3~ 3 1 3 ng/m3;全市上下午平均浓度为 1 3 9ng/m3;上午浓度平均值是下午的 2倍 ;全市空间分布整体上由北向南逐渐降低 ,东北部最重 ,东南部最轻 ;不同功能区的污染程度依次为 :一电厂化工区 >太钢工业区 >桃园商业区 >太行居民区。本文还着重探讨了污染分布的成因 ,并提出了改善大气质量的建议。  相似文献   

12.
Total suspended particulates (TSP) were collected with a high volume sampler from the indoor work environment of 23 industries in Al-Rusayl Industrial Estate in Muscat, Oman. The values measured ranged from 39 microg m(-3) to 1033 microg m(-3). TSP in the ambient air of the area was found to have an average value of 1802 microg m(-3). TSP were analyzed for Pb, Cu, Ni, Zn and Cr. Compared to other metals, Pb emission was high with values ranging from 3 to 15 109 ng m(-3) with the mean value being 1 293 ng m(-3); Cu concentration varied from 3 to 2600 ng m(-3) with a mean value of 131 ng m(-3); Ni concentration ranged from 6 to 46 ng m(-3) with a mean value of 17 ng m(-3); Cr concentration ranged from 1 to 133 ng m(-3) with a mean value of 23 ng m(-3) while that of Zn varied from 0.01 to 1 978 ng m(-3) with the mean value being 464 ng m(-3). The concentrations of Pb, Ni, Cu, Cr, and Zn in the ambient air were also measured and found to have the following values: 122, 18, 16, 5 and 0.01 ng m(-3), respectively. These values indicate that the industries in the area do not contribute significantly to heavy metal air pollution.  相似文献   

13.
通过对鞍山市(1个工业区、2个工业区周边、3个居住区、1个对照点)2015年1月采暖期大气PM_(2.5)中多环芳烃(PAHs)的监测,采用BaP当量致毒系数TEF,分析了鞍山市大气PM_(2.5)中典型PAHs毒性当量分布特征。研究表明,鞍山市大气PM2.5中工业区及工业区周边Ba P毒性当量浓度要远高于居住区和对照点,污染物主要由4~6环的PAHs组成,很强致癌BaP当量浓度为9.351~38.59 ng/m3。  相似文献   

14.
Resin acids are constituents of natural and technical products of widespread use. Exposure is known to cause health effects in the airways and on the skin. Liquid chromatography/positive ion electrospray-mass spectrometry (HPLC/pos ESI-MS) was investigated for determination of 7-oxodehydroabietic (7-OXO), dehydroabietic (DHAA) and abietic acid (AA) in wood dust-containing air samples as a derivatisation-free alternative to the GC/FID HSE method 83/2, developed by the Health and Safety Executive UK. The resin acid 7-OXO was measured as a marker for oxidised resin acids, which are known to be the main contact allergens in colophonium. The found detection limits were 0.42 ng m(-3) for 7-OXO, 5.2 ng m(-3) for DHAA and 9.4 ng m(-3) for AA, respectively, which are considerably lower than with the GC/FID method (24, 115 and 89 ng m(-3)). The two methods correlated well, although consistently and significantly lower concentrations of 7-OXO were detected with LC/MS. The higher concentration of this compound with MDHS 83/2 is suggested to be an artefact from the derivatisation step in the presence of soluble wood dust remains.  相似文献   

15.
In order to investigate the spatial and temporal variability of atmospheric mercury (Hg) in Chongqing, China, gaseous elemental mercury (GEM) was measured from August 2006 to September 2007, using Lumex multifunctional mercury analyzer RA-915(+) (Lumex Ltd., Russia). The mean GEM concentration was 6.74 +/- 0.37 ng m(-3) in Chongqing, much higher than the accepted global background values (1.5-2 ng m(-3)). The GEM concentrations were different in different function areas. GEM in transport, industrial and commercial areas were 7.07 +/- 1.04, 7.05 +/- 0.96 and 6.71 +/- 1.10 ng m(-3), respectively, while GEM was 6.14 +/- 1.30 and 4.32 +/- 1.04 in the educational/recreational and nature conservation areas, suggesting that Hg emissions from mobile vehicles and industrial sources (specially coal combustion) were the most important contributors to atmospheric Hg in Chongqing. Mean Hg concentrations also had monthly variations with highest in November (8.24 +/- 0.50 ng m(-3)) and lowest values in August (5.36 +/- 0.70 ng m(-3)). Additionally, the diurnal variation of GEM concentrations was dependent on the local/regional atmospheric conditions. At Jinyun Mountain site (natural conservation area), hourly GEM concentrations had much higher values in daytime than at night. At Power Plant site, however, the hourly GEM concentrations were lower in daytime than at night. GEM concentrations in the air were correlated significantly with meteorological parameters except for barometric pressure.  相似文献   

16.
Continuous measurements of black carbon (BC) aerosol mass concentration were performed at a background site Preila (55°55'N, 21°00'E, 5 m a.s.l., Lithuania) during the period 2008-2009. The data were used to characterize the BC mass concentration distribution over the East Baltic region. High increase in aerosol BC concentration was associated with the change in air mass characteristics and biomass burning during the winter heating season and spring wildfires. Monthly means of BC concentration ranged from 212 to 1268 ng m(-3) and the highest hourly means of concentration were from 4800 to 6300 ng m(-3), predominantly in spring and winter months. During the October-April period the BC mass concentrations were about twice as high as those in the summertime. The BC diurnal pattern in winter was typically different from that in spring indicating the seasonal variation of the atmospheric boundary layer height. The weekday/weekend difference was not strongly pronounced because the BC concentrations in Preila are mainly affected by long-range transport or local sources. Typical periodicities caused by anthropogenic and meteorological influences have been identified using Fourier analysis. It was shown that domestic heating appears as a 365 day periodicity; traffic slightly contributes 5-7 day peaks in the spectrum and elevated long-range BC can be identified as characteristic peaks with periodicities in the range from 16 to 29 days.Temporal evolution and transport of BC aerosols were interpreted by the air mass backward trajectory analysis in conjunction with the examination of the wavelength dependence on the aethalometer data. Air masses originated from the North Atlantic Ocean and Scandinavia were favourable for lower BC concentrations (350 ng m(-3)), while the BC level associated with the Western Europe airflows was significantly higher (970 ng m(-3)). The mean values of ?ngstr?m exponent of the absorption coefficient (monthly means 1.45 ± 0.25 and 0.84 ± 0.50 over January and June, respectively) revealed that the BC concentration observed over the East Baltic is influenced by submicron sized particles as a result of incomplete biomass combustion during the winter season.  相似文献   

17.
Vapour (T-Hg(v)) and particulate (T-Hg(p)) mercury were measured in the lower atmosphere at a ground station in Kuwait Bay. The concentration of T-Hg(v) varied from 0-86 ng m(-3) with a mean of 3.8 +/- 5.5 ng m(-3)(n= 13 326). About 40% of the measured T-Hg(v) values over Kuwait Bay are higher than the global range (1-3 ng m(-3)). Car exhausts contributed to the increase of T-Hg(v) during the rush hours. However the contribution of T-Hg(v) from air crossing Kuwait Bay exceeds that T-Hg(v) produced by traffic probably because of the effects of the substantial load of industrially-derived mercury in the sediments of this shallow region. Thermal inversions have a major impact on the levels during the evening hours. The concentration of T-Hg(p) varied from 0.00-0.22 ng m(-3) with a mean of 0.03 +/- 0.03 ng m(-3)(n= 175). The T-Hg(p)/T-Hg(v)% ratio varied from 0-11.1 (n= 171) with a mean of 1.0 +/- 1.5%. Meteorological parameters influence the T-Hg(v) and T-Hg(p) concentrations with dust storms having a major impact on T-Hg(p) concentrations.  相似文献   

18.
The air quality over the Toulouse urban area (France) is recorded daily by the regional "Midi-Pyrénées" atmospheric pollution measurements network (ORAMIP). Relevant data is collected from about 100 analysers spread over more than thirty stations. The regulations covering major indicators of atmospheric pollution (ozone, nitrogen dioxide, sulphur dioxide) have been updated in recent years to include additional compounds like polycyclic aromatic hydrocarbons (PAHs). The ORAMIP, in partnership with the ENSIACET has undertaken background PAH average concentration measurements over the urban agglomeration of Toulouse during spring 2006 for various types of sites (traffic, urban, industrial). The sampling was performed using a low volume air sampler equipped with quartz fiber filters and polyurethane foams For the two urban sites, total atmospheric concentrations between 12 and 20 ng/m(3) have been obtained, whereas for the industrial site the values averaged 22 ng/m(3). In addition, and regardless of site, the average concentrations of benzo[a]pyrene, at present the only regulated PAH, were always less than the 1 ng/m(3) limit.  相似文献   

19.
马鞍山市大气环境中苯并(a)芘分布与变化规律研究   总被引:1,自引:0,他引:1       下载免费PDF全文
研究了马鞍山市大气环境中苯并(a)芘的分布与变化规律,监测了马鞍山市各功能区,新老市区的居民区及交通要道大气环境中苯并(a)芘的含量,该市功能区内的工业区大气中苯并(a)芘污染严重,最高质量浓度达50.31ng/m^3,居民区内老市大气中的苯并(a)芘污染明显高于新市区,究其原因,老市区是马鞍山,市工业发源地,属居民,商业及工业混合区,研究中发现,大气中苯并(a)芘含量高低有季节性的昼夜变化现象,时空分布和迁移变化规律明显,并且大气中总悬浮颗粒物与苯并(a)芘的相关性显著。  相似文献   

设为首页 | 免责声明 | 关于勤云 | 加入收藏

Copyright©北京勤云科技发展有限公司  京ICP备09084417号