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1.
于2006年4月到2007年8月在泰安市城北设立采样点收集降水样品,对样品中的13种美国环保署(US EPA)优控多环芳烃(PAHs)及NO3-、SO42-等无机阴、阳离子进行了定量分析.测定结果表明,雨水样品中∑13PAHs含量范围在11.3~179.4ng/L之间,平均浓度为89.8ng/L;NO3-、SO42-分别在16.35~186.4ueq/L及53.83~721.9ueq/L之间;样品中无机阴、阳离子总和之比∑(+)/∑(-)的平均值为0.93.相关分析表明,样品中菲、芴、萤蒽等3、4环多环芳烃化合物含量较高;样品中的PAHs浓度与季节存在一定的相关性,但与样品中的NO3-、SO42-浓度间无明显的相关性;样品中的多环芳烃主要来源于煤炭、木材及石油的不完全燃烧.  相似文献   

2.
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   

3.
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   

4.
用玻璃纤维滤膜采集PM_(2.5)样品,乙腈超声提取-高效液相色谱法分析测量多环芳烃浓度。结果表明:PAHs的浓度变化受到大气降水的影响,夏季浓度最低,冬季浓度最高,PM_(2.5)中PAHs总量月平均变化趋势呈"凹"形变化;PAHs的结构以2~3环、5~6环为主;比值法显示PAHs来源与稳定的排放源相关,机动车排放不容忽视,与北方城市燃煤污染有着较大区别。  相似文献   

5.
对贵阳市不同功能区在不同季节大气PM_(2.5)中多环芳烃(PAHs)进行了采样观测,利用UVD和FLD双检测器串联HPLC法分析了16种优控PAHs。结果显示,在贵阳市主城区PM_(2.5)中PAHs有检出,5个采样点全年ρ(∑PAHs)为4. 44~114 ng/m~3,平均值为24. 96 ng/m~3,其值呈现出夏季最低冬季最高的特征,各个功能区在不同季节ρ(PAHs)不同,大小趋势也不同;四季PAHs单体中均以4-6环为主,占ρ(∑PAHs)的68%以上; PAHs来源解析结果显示,贵阳市大气PM_(2.5)中PAHs来源具有明显的季节特征,春、夏和秋季主要来源是石油燃烧排放,兼有少量的生物质燃烧排放,冬季PAHs主要来源是燃煤和石油燃烧排放。PM_(2.5)中PAHs毒性评价结果表明,贵阳市大气中PAHs的春季、夏季和秋季健康风险较小,冬季健康风险较大。四季各功能区ρ(Ba P)大部分均低于《环境空气质量标准》(GB 3095—2012)规定限值(2. 50 ng/m~3),但冬季除背景点外,其他监测点均超标,最大超标倍数为3. 80倍。  相似文献   

6.
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   

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.
南京市大气颗粒物中多环芳烃变化特征   总被引:4,自引:2,他引:2  
逐月采集南京市大气中不同粒径的颗粒物,采用HPLC分析了2010年每个月PM_(10)和PM_(2.5)颗粒物样品中的多环芳烃(PAHs)的种类和浓度水平。结果表明:PM_(10)中PAHs年均值为25.07 ng/m~3,范围为11.03~53.56 ng/m3;PM_(2.5)中PAHs年均值为19.04 ng/m~3,范围为10.82~36.43 ng/m~3。PM_(10)和PM_(2.5)中PAHs总体浓度有着相似的变化趋势,呈现凹形变化曲线;在南京市大气颗粒物中吸附的PAHs大部分以5~6环的高环数组分为主,大部分PAHs和∑PAHs的相关性较好,年度变化幅度不大,分析结果表明,颗粒物中PAHs的来源与稳定的排放源相关,机动车排放不容忽视,与北方城市燃煤污染有着较大的区别。  相似文献   

9.
淮南市春季大气PM 10 中多环芳烃的污染特征及来源   总被引:3,自引:0,他引:3       下载免费PDF全文
2008年4月-2008年6月对淮南市的5个采样点PM10连续采样,分析了其中多环芳烃(PAHs)。PAHs质量浓度的最大值和最小值分别为112ng/m^3和15.2ng/m^3,PAHs春季质量浓度均值为40.2ng/m^3;PAHs组成以4环和5环为主;春季不同采样点PAHs质量浓度与环境温度呈负相关关系,运用PAHs比值综合判断,淮南市春季大气PM10中PAHs主要来源于燃煤和机动车尾气。  相似文献   

10.
于非采暖季和采暖季分别采集某石化化工行业聚集城市中心城区室内外PM_(2.5)样品,采用高效液相色谱法分析PM_(2.5)上载带的16种PAHs,对其分布特征、来源以及室外PAHs污染对室内污染的贡献进行了初步探讨。结果表明,研究区域非采暖季和采暖季室外PM_(2.5)中ΣPAHs浓度日均值分别为36.3、294 ng/m~3,室内PM_(2.5)中ΣPAHs浓度分别为14.8、84.6 ng/m~3,均以4、5环PAHs为主;室内PAHs主要来自室外渗透污染,但同时明显存在室内排放源贡献;PAHs来源分析进一步证实研究区域PAHs主要来自煤炭、石油等不完全燃烧,采暖季煤炭燃烧源贡献更突出。  相似文献   

11.
天津城郊土壤中PAHs含量特征及来源解析   总被引:4,自引:1,他引:3  
以天津市郊环城四区为研究对象,系统采集了环城四区95个表层土壤样品,利用高效液相色谱仪对16种PAHs进行分析测定,结果表明,西青、东丽、津南和北辰土壤中16种PAHs的总量范围分别为62.6~1 994.9、36.1~4 074.7、20.1~2 502.5、22.1~707.7μg/kg;平均含量分别为445.8、841.8、509.5、242.5μg/kg。四区中都以高环多环芳烃为主,西青、东丽、北辰和津南高环多环芳烃分别占多环芳烃总比例的45.4%、42.2%、38.8%和38.7%。空间分析的结果表明,靠近天津市市区样点土壤中多环芳烃的含量要明显高于远离市区土壤中多环芳烃的含量。利用环数PAHs的相对丰度和比值法对天津市郊环城四区土壤中多环芳烃的污染来源进行了解析,研究区土壤监测样点的PAHs主要来自燃烧源,少部分来自石油类来源或几种污染源的共同复合累加的作用。  相似文献   

12.
Polycyclic aromatic hydrocarbons (PAHs) have been determined in blue mussels (Mytilus galloprovincialis) from several Iberian Mediterranean coastal areas through the implementation of a monitoring programme from Spain in the framework of the Mediterranean Pollution Programme (MED POL). The selected areas correspond to sites with differing degrees of exposure to the main pollution sources (hot spots, coastal and reference areas). The sampling campaigns were performed from 2004 to 2009, with samples being taken from May to June, the non-spawning period for mussels in this area. Thirteen PAHs were determined by high-performance liquid chromatography with specific fluorescence detection. In general, total PAHs concentration was lower than 50 μg kg?1 d.w., except in areas close to the principal ports and cities (Barcelona, Tarragona, Valencia and Algeciras) where it varies from 75 to 390 μg kg?1 d.w. Background concentrations have been proposed for PAHs in mussels (23.8 μg kg?1 d.w.) from Western Mediterranean area. Temporal trends were not statistically significant for PAHs concentrations from 2004 to 2009. Longer monitoring periods would be required to detect a continuous tendency, especially for PAHs because although the efficiency of combustion engines has reduced PAHs emissions, their increasing use could alter this potential reduction. The predominant PAHs were three and four ring congeners in all cases, with the predominance of phenanthrene in mussels sited far from the main PAHs sources. The phenanthrene/anthracene (lower than 10) and fluoranthene/pyrene (higher than 1) ratios indicate that PAHs detected in Spanish Mediterranean coastal mussels are mainly of pyrolytic origin.  相似文献   

13.
Concentration, composition profile, spatial distribution, sources, and health risk of 16 polycyclic aromatic hydrocarbons (PAHs) were analyzed in 69 surface soil samples collected from Hangzhou urban districts. ∑PAHs ranged from 180.77 to 1,981.45 μg kg?1 with a mean of 611.28 μg kg?1. Among different functional areas, a higher level of PAHs was found in the roadsides, followed by commercial districts, residential areas, parks, and greenbelts. The composition of PAHs was characterized by high molecular weight PAHs (4?~?6 rings). Principal component analysis (PCA) and PAH isomeric ratios indicated that PAHs mainly originated from combustion, especially vehicle exhaust. The incremental lifetime cancer risks (ILCRs) associated with exposures to PAHs in soil were calculated separately for children and adults under normal and extreme conditions. The results showed that ILCRs for urban soil of Hangzhou were acceptable. However, attentions should be attracted on the sites of high PAH concentrations because the ILCRs were closed to 10?4 under extreme conditions, especially for children.  相似文献   

14.
Polycyclic aromatic hydrocarbons (PAHs) and their health risks in surface soils (n?=?31) collected from coastal and estuarine areas of the northern Bohai and Yellow Seas (CEANBYS), China, were investigated. Total concentrations of PAHs ranged from 6.6?×?101 to 9.2?×?102?ng?g?1 dry weight, with an average of 3.1?×?102?ng?g?1 dw. The locations where greater concentrations of PAHs were observed were all near factories emitting black smoke or on the edge of the urban areas. These observations are consistent with concentrations of PAHs in soils being influenced by human activities, especially industrialization and urbanization. Concentrations of PAHs were significantly correlated with concentrations of organic carbon in soils. The patterns of relative concentrations and types of PAHs observed as well as knowledge of the potential sources were consistent with the primary sources of PAHs in soils of the CEANBYS being derived from the pyrolytic processes such as combustion of fossil fuel. The incremental lifetime cancer risks of exposing to PAHs for child, youth, and adult were 1.6?×?10?6, 1.2?×?10?6, and 1.9?×?10?6.  相似文献   

15.
Surface soil (0-5 cm) samples from 17 sampling sites including different functional areas at Ji'nan city in Shandong Province of China were collected and analyzed for 16 EPA priority polycyclic aromatic hydrocarbons (PAHs). The total PAH concentrations were in the range from 1.31 mg kg(-1) to 254.08 mg kg(-1) (dry weight), and the average level of total PAHs was 23.25 mg kg(-1). The highest total PAHs concentrations were found in steel and iron plant at industrial areas. The total PAHs concentrations in industrial areas were markedly higher than those in other different functional areas. According to comparing total PAHs concentration in Ji'nan city to that of other urban areas, it was found that total PAHs concentrations were 6 to 137 times higher than other areas because of some specific sampling sites such as steel and iron plant and one main roadside. The results showed that PAHs in topsoil of Ji'nan city were suffered from strong pyrogenic influence, especially in industrial areas. However about 52.9% soil samples were mainly originated from both pyrogenic and petrogenic mixed sources based on Flu/Pyr ratios and Phe/Ant ratios. Furthermore, It was found that all individual PAHs except Fle were significantly correlated (P < 0.01) with LMW, HMW, total PAHs and SOM, and individual PAHs except Fle in soils were significantly correlated (P < 0.01) with each other. The nemerow composite index to assess the environmental quality showed that the soil sample of steel and iron plant in industrial areas and one main roadside were heavy pollution of PAHs, and about 47% soil sampling sites were safety, about 53% soil sampling sites were got different grades of PAHs pollution.  相似文献   

16.
Concentrations of 16 priority polycyclic aromatic hydrocarbons (PAHs) were measured in 28 surface soils samples collected from Urumqi, northwest China, for examination of distributions, source contributions, and potential health effects. The results indicated that the sum of 16 PAHs concentration ranged from 331 to 15,799 μg?kg?1 (dw) in soils, with a mean of 5,018?±?4,896 μg?kg?1 (n?=?28). The sum of seven carPAHs concentration ranged from 4 to 1,879 μg?kg?1 (dw; n?=?28). The highest ∑PAHs concentrations were found at roadsides and industrial sites, followed by those at parks, rural areas, and business/residential areas. Coal combustion, emission of diesel and gasoline from vehicles, and petroleum source were four sources of PAHs as determined by PMF analysis, which contributed 51.19, 19.02, 18.35, and 11.42 % to the PAH sources, respectively. Excellent coefficients of correlation between the measured and predicted PAHs concentrations suggested that the PMF model was very effective to estimate sources of PAHs in soils. Incremental lifetime cancer risk values at the 95th percentile due to human exposure to surface soils PAHs in Urumqi were 2.02?×?10?6 for children and 2.72?×?10?5 for adults. The results suggested that the current PAHs levels in soils from Urumqi were pervasive and moderately carcinogenic to children and adults.  相似文献   

17.
常州市秋季大气PM2.5中多环芳烃污染水平及来源   总被引:2,自引:0,他引:2  
为了研究常州市秋季大气PM2.5中多环芳烃的污染水平及其来源,在常州市布设了6个采样点,分别代表交通干道区、商业混合区、居民文教区、远郊区、工业区和对照点,于2013年10月进行大气PM2.5的采样,采用微波萃取-高效液相色谱法测定其中16种USEPA优控多环芳烃的浓度值,并分别通过比值法和因子分析法判断其主要来源。结果表明,常州市秋季大气PM2.5中多环芳烃的主要来源为煤燃烧和机动车排放。  相似文献   

18.
Seventeen polycyclic aromatic hydrocarbons (PAHs) were studied in surface waters (including particulate phase) from the Chenab River, Pakistan and ranged from 289-994 and 437-1290 ng l(-1) in summer and winter (2007-09), respectively. Concentrations for different ring-number PAHs followed the trend: 3-rings > 2-rings > 4-rings > 5-rings > 6-rings. The possible sources of PAHs are identified by calculating the indicative ratios; appropriating petrogenic sources of PAHs in urban and sub-urban regions with pyrogenic sources in agricultural region. Factor analysis based on principal component analysis identified the origins of PAHs from industrial activities, coal and trash burning in agricultural areas and municipal waste disposal from surrounding urban and sub-urban areas via open drains into the riverine ecosystem. Water quality guidelines and toxic equivalent factors highlighted the potential risk of low molecular weight PAHs to the aquatic life of the Chenab River. The flux estimated for PAHs contaminants from the Chenab River to the Indus River was >50 tons/year.  相似文献   

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