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1.
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   

2.
为深入了解邢台市PM_(10)、PM_(2.5)浓度变化情况和气流后向轨迹,对邢台市2013—2016年环境大气颗粒污染物监测数据进行了分析,同时利用HYSPLIT模型计算出逐日72 h后向气流轨迹。结果表明:邢台市的PM_(10)和PM_(2.5)质量浓度在2013—2016年间呈逐年下降趋势,PM_(10)和PM_(2.5)质量浓度高值出现在冬季(296μg/m~3和192μg/m~3),最低值出现在夏季(140μg/m~3和80μg/m~3),PM_(10)和PM_(2.5)质量浓度在日变化上均呈"双峰双谷"型分布;后向轨迹的季节聚类分析表明,春季大气颗粒物污染以粒径2.5~10μm的颗粒污染物为主,夏季、秋季和冬季的大气颗粒物污染以PM_(2.5)为主;逐日聚类分析表明,在路径为西北偏西向的、途经多个沙源地的气流影响下,邢台市的PM_(10)和PM_(2.5)质量浓度处于一个相对高值;来源于偏南向的气流由于化合反应,污染物积聚导致PM_(10)、PM_(2.5)质量浓度也处于相对高值;在来源于西北向和偏北向的、水汽含量相对较低的气流影响下,邢台市的PM_(10)、PM_(2.5)质量浓度出现一个明显的下降。  相似文献   

3.
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   

4.
为了解采暖期大气PM_(1.0)和PM_(2.5)中水溶性离子污染特征,采集哈尔滨市2014年11月至2015年3月采暖期PM_(1.0)和PM_(2.5)的样品,进而分析其中的水溶性离子(F-、Cl-、NO-3、SO2-4、Na+、NH+4、K+、Mg2+、Ca2+)的质量浓度。结果表明:PM_(1.0)和PM_(2.5)中的水溶性离子具有相同的变化趋势。采暖期间PM_(1.0)和PM_(2.5)中9种水溶性离子质量浓度总和分别为25.4~60.7μg/m~3和38.8~78.0μg/m~3。在PM_(1.0)和PM_(2.5)中NH+4、NO-3、SO2-4占比较高,而F-、Mg2+占比较低。PM_(1.0)和PM_(2.5)中9种水溶性离子质量浓度均为夜间大于白天。在PM_(1.0)和PM_(2.5)中,Mg2+和NH+4、F-和Cl-呈显著相关,说明它们来自相似的污染源,在PM_(1.0)中的K+和Ca2+显著相关,故它们受相似的污染源的影响。根据酸度与各离子的相关性,得出SO2-4和NH+4是控制大气颗粒物酸碱性的主要离子。另外,气象因素对PM_(1.0)和PM_(2.5)的浓度有影响。  相似文献   

5.
对2014—2016年齐齐哈尔市PM_(2.5)与PM_(10)质量浓度的时间变化特征进行简要分析,并探究PM_(2.5)/PM_(10)以及PM_(2.5)与PM_(10)的相关性。结果表明:2014—2016年齐齐哈尔的PM_(2.5)与PM_(10)的年均质量浓度分别为36.7、62.9μg/m~3,且呈逐渐下降趋势;冬季的PM_(2.5)与PM_(10)浓度最高,秋季次之,春季与夏季相对较低;2014—2016年PM_(2.5)与PM_(10)质量浓度月变化趋势基本相同,整体呈现2—6月逐渐下降,9—11月逐渐上升的规律;PM_(2.5)与PM_(10)质量浓度的日变化均呈双峰现象;对PM_(2.5)与PM_(10)进行线性拟合,相关系数为0.896 3。同时,残差分析也说明两者拟合情况良好,四季相关系数为r_(秋季)(0.982 2)r_(冬季)(0.964 4)r_(夏季)(0.943 9)r_(春季)(0.829 6);2014—2016年PM_(2.5)/PM_(10)平均值为55.27%,大气颗粒物PM_(2.5)的贡献率高达一半以上。  相似文献   

6.
超低排放下燃煤电厂颗粒物排放特征分析研究   总被引:4,自引:0,他引:4  
选取6家经过超低排放改造的燃煤电厂,对湿法脱硫(WFGD)和湿式电除尘器(WESP)进出口烟气中TPM、PM_(10)、PM_(2.5)、PM_1进行测试,分析研究超低排放下燃煤电厂颗粒物的排放特征及电除尘器后净化设备对颗粒物的脱除效果。结果表明,6家电厂TPM、PM_(10)、PM_(2.5)、PM_1排放浓度分别为0.75~2.36、0.71~2.12、0.65~1.96、0.51~1.57 mg/m~3。分析烟气中颗粒物粒径分布可知,除尘器后,PM10占TPM质量比低于40%,且比例随烟气经过WFGD和WESP而逐渐降低。WFGD对PM2.5有较好的脱除效果,而WESP对PM1脱除效果显著。为满足超低排放标准,6家电厂除尘器后脱除设备综合除尘效率大多在85%以上。计算得到6家电厂TPM、PM_(10)、PM_(2.5)、PM_1排放因子,与超低排放改造之前同等级燃煤电厂相比,6家电厂不同粒径颗粒物排放因子均显著降低,也远低于西方发达国家燃煤电厂颗粒物排放因子。  相似文献   

7.
北京地区不同季节PM2.5和PM10浓度对地面气象因素的响应   总被引:1,自引:0,他引:1  
利用2013年1月—2014年12月北京地区PM_(2.5)和PM_(10)监测数据和同期近地面气象观测数据,采用非参数分析法(Spearman秩相关系数)研究了北京地区PM_(2.5)和PM_(10)的浓度对不同季节地面气象因素的响应。结果表明:北京地区大气颗粒物浓度水平具有明显的季节特征,冬季大气颗粒物污染最严重,夏季最轻。不同季节影响颗粒物浓度水平的气象因素各不相同,其中风速和日照时数为主要影响因素。PM_(2.5)和PM_(10)质量浓度对气象因素变化的响应程度也有较大区别,PM_(2.5)/PM_(10)比值冬季最高,PM_(2.5)影响最大,春季最低,PM_(10)影响最大。这些结论可对制订科学有效的大气污染控制策略提供参考。  相似文献   

8.
以和田市城区2014年采集的大气PM_(2.5)样品为实验对象,将0.1 g的PM_(2.5)样品膜与2-硫代巴比妥酸(0.2%)和三氯乙酸(20%)混合显色液反应,用可见光分光光度计测定反应产物的吸光度,通过正交实验来优化PM_(2.5)膜中丙二醛(MDA)的提取及测定条件,结果表明,在反应温度90℃、超声和加热时间40 min、显色剂用量为45 mL时,反应产物在532 nm处具有稳定的最大吸收峰。对和田市城区PM_(2.5)及MDA质量浓度的变化特征分析结果表明,和田市城区4个季节PM_(2.5)平均质量浓度由高到低顺序分别为春季(1 096.67±369.60)μg/m~3、夏季(1 016.16±708.00)μg/m~3、秋季(686.88±525.00)μg/m~3和冬季(214.54±94.70)μg/m~3。MDA平均质量浓度的变化范围为1.10~7.75 ng/m~3,其平均值最高为夏季(4.43±1.80)ng/m~3,最低为春季(1.42±0.60)ng/m~3,冬季与秋季相当,分别为(2.93±0.70)ng/m~3和(2.83±0.80)ng/m~3;最终,将PM_(2.5)膜中MDA的质量浓度与相应的TD_(30)(体外DNA氧化损伤达到30%的剂量)进行相关性分析得出,无论是全样还是水样的TD_(30)值均随MDA浓度的升高而呈降低的趋势。其中,全样与MDA质量浓度的相关性更为显著(r=-0.597,显著性P0.01)。  相似文献   

9.
选取荒漠草原无林地的PM_(2.5)、PM_(10)浓度以及气象因子数据,对颗粒物浓度的时间变化特征及其与气象因子的关系进行分析。结果表明:(1)1月的PM_(2.5)、PM_(10)月平均浓度最高,7月的PM_(2.5)与PM_(10)达到最低。季节尺度上PM_(2.5)、PM_(10)浓度变化为由大到小顺序依次为冬季秋季春季夏季。(2)风速≤4.0 m/s时,随着风速增加,PM_(2.5)、PM_(10)浓度不断降低;当风速4.0 m/s时,PM_(2.5)、PM_(10)浓度随风速增加而增加。PM_(2.5)、PM_(10)浓度与温度负相关。相对湿度≤50%时,随着相对湿度增加,PM_(2.5)、PM_(10)浓度呈增加趋势;相对湿度50%时,随着空气湿度增加,PM_(2.5)、PM_(10)浓度呈降低趋势。随着大气气压上升,PM_(2.5)与PM_(10)浓度随之增加。(3)不同季节的气象因子对PM_(2.5)、PM_(10)影响存在差异。  相似文献   

10.
西宁市非采暖季和采暖季PM2.5中14种金属元素特征   总被引:1,自引:0,他引:1  
于2012年11月采暖季和2013年9月非采暖季,在青藏高原典型城市西宁市4个采样点采集细颗粒物(PM_(2.5))样品,共获得40个有效样品。用微波消解-ICP-MS法、原子荧光法分析了样品中14种重点防控金属。结果表明:14种重点防控金属中Ag、Tl平均质量浓度为0.10~0.50 ng/m~3,Co、Sb、Hg平均质量浓度为0.50~4.00 ng/m~3,V、Cd、Cr、Ni、Cu、As平均质量浓度为4.00~50.0 ng/m~3,Mn、Pb、Zn平均质量浓度为50.0~2 000 ng/m~3。采样期间,采暖季相比非采暖季,PM_(2.5)质量浓度有下降趋势,不同采样区金属元素浓度有增有减。富集因子分析结果表明,重点防控金属元素在非采暖季主要来源于土壤风沙扬尘、机动车尾气和工业排放,采暖季主要来源于土壤风沙扬尘、燃煤、燃油、机动车尾气和工业排放。非采暖季Zn、Ag、Cd、Hg、Tl和Pb富集因子较高,采暖季Zn、As、Ag、Cd、Sb、Hg、Tl、Pb富集因子较高,更容易受到人为源的影响。  相似文献   

11.
This research paper aims at establishing baseline PM10 and PM2.5 concentration levels, which could be effectively used to develop and upgrade the standards in air pollution in developing countries. The relative contribution of fine fractions (PM2.5) and coarser fractions (PM10-2.5) to PM10 fractions were investigates in a megacity which is overcrowded and congested due to lack of road network and deteriorated air quality because of vehicular pollution. The present study was carried out during the winter of 2002. The average 24h PM10 concentration was 304 μg/m3, which is 3 times more than the Indian National Ambient Air Quality Standards (NAAQS) and higher PM10 concentration was due to fine fraction (PM2.5) released by vehicular exhaust. The 24h average PM2.5 concentration was found 179 μg/m3, which is exceeded USEPA and EU standards of 65 and 50 μg/m3 respectively for the winter. India does not have any PM2.5 standards. The 24 h average PM10-2.5 concentrations were found 126 μg/m3. The PM2.5 constituted more than 59% of PM10 and whereas PM10-PM2.5 fractions constituted 41% of PM10. The correlation between PM10 and PM2.5 was found higher as PM2.5 comprised major proportion of PM10 fractions contributed by vehicular emissions.  相似文献   

12.
Roadside PM10 has been monitored by Partisol® at three sitesin Sunderland between August 1997 and February 1998. The sites chosen were an inner city kerbside site; a roadside site adjacentto a dual carriageway on the outskirts of Sunderland with an openaspect; and a rural site.The results indicate that there is a seasonal variation in the relationship between the sites in terms of monitored PM10.In the winter there is a poor correlation between the sites whereas in the summer significant correlations are obtained. Of the sites monitored PM10 is consistently highest at the inner city roadside site. During the summer, exceedances of theU.K. 50 g m-3 standard (DETR, 2000) are associated with conditions suitable for the build-up of photochemical pollutionhowever during the winter period exceedances are recorded duringa variety of weather conditions.At the dual carriageway site PM2.5 has also been recorded and contributions to measured PM10 are 77% in summer and68% in winter. The results illustrate a number of inconsistencies between this study utilising the Partisol® andothers reporting results where PM10 has been monitored by TEOM®.  相似文献   

13.
建立了超声提取-气相色谱质谱法测定大气PM2.5中32种正构烷烃方法,经离子温度优化、前处理比较、空白滤膜考察等获得了最佳的实验条件。研究发现,高、中、低3种浓度标准曲线的相关系数均在0.995以上,3种浓度的空白样品加标回收率分别为72.2%~117.8%、73.5%~104.4%、73.8%~109.5%,精密度均小于10%,实际样品加标回收率为75.7%~108.9%。当采样体积为24 m3时,各目标化合物的方法检出限为0.046~2.6 ng/m~3;经正构烷烃浓度范围为0.17~64.3 ng/m~3的1月及浓度范围为0.53~7.67 ng/m~3的6月的实际样品验证,该方法的检出限和测量范围也可较好的满足实际样品的测定。  相似文献   

14.
宁波市区冬季大气颗粒物及其主要组分的污染特征分析   总被引:7,自引:4,他引:3  
为了更好地研究影响宁波市区环境空气质量的污染物变化特征,于2010年1月20—30日进行了加强监测。研究结果表明,宁波市区大气中PM10和PM2.5质量浓度较高,其中PM2.5/PM10为0.5~0.85。对PM10和PM2.5采样膜分析,水溶性粒子和含碳组分分别占PM10和PM2.5质量浓度的56.7%和66.9%,其中二次污染的水溶性离子SO42-、NO3-和NH4+是PM10和PM2.5中浓度较高的离子组分;PM2.5样品中OC与EC的相关性较好,表明OC与EC的来源相对一致,可能主要来自机动车尾气的贡献;但PM10样品中OC与EC的相关性较差,表明其来源相对复杂;其中SOC的浓度占OC的13%~35%,说明宁波市区冬季导致二次污染的光化学反应不活跃。  相似文献   

15.
Ambient concentrations of PM2.5 and PM10 are of concern with respect to effects on human health and environment. Increased levels of mortality and morbidity have been associated with respirable particulate air pollution. In India, it is not yet mandatory to monitor PM2.5 levels therefore very limited information is available on PM2.5 levels. To understand the fine particle pollution and also correlate with PM10 which are monitored regularly in compliance with ambient air quality standards. This study was carried out to monitor PM2.5, PM10, and NO2 for about one year in a residential cum commercial area of Mumbai city with a view to understand their correlation. The average PM2.5 concentration at ambient and Kerbsite was 43 and 69 μg/m3. The correlation coefficients between PM2.5 and PM10 at ambient and Kerbsite were 0.83 and 0.85 respectively thus indicating that most of the PM2.5 and PM10 are from similar sources. TSP, PM10 levels exceeded Central Pollution Control Board(CPCB) standard during winter season. PM2.5 levels also exceeded 24 hourly average USEPA standard during winter season indicating unhealthy air quality.  相似文献   

16.
利用2018—2021年安徽省空气质量监测数据分析了PM2.5和O3时空分布特征及其引发的健康风险。结果表明:从时间分布来看,2018—2021年安徽省PM2.5年均值下降25.5%,而O3-8 h年均值则保持持平;PM2.5和O3-8 h月均值具有明显的季节变化特征,PM2.5月均质量浓度和超标天数均在冬季达到最大值,O3-8 h月均值和超标天数则在夏季达到最大值。从空间分布来看,PM2.5、O3-8 h年均值和超标天数均为皖北最高,其次为皖中,最后为皖南。夏季O3是主要的健康风险因子,冬季PM2.5是主要的健康风险因子。当PM2.5超标时,除2021年皖北地区外(PM10是主要的健康风险因子),PM2.5均是主要的健康风险因子;当O3-8 h超标时,O3是主要的健康风险因子。  相似文献   

17.
To analyze polycyclic aromatic hydrocarbons (PAHs) at an urban site in Seoul, South Korea, 24-hr ambient air PM2.5 samples were collected during five intensive sampling periods between November 1998 and December 1999. To determine the PAH size distribution, 3-day size-segregated aerosol samples were also collected in December 1999. Concentrations of the 16 PAHs in the PM2.5 particles ranged from 3.9 to 119.9 ng m−3 with a mean of 24.3 ng m−3.An exceptionally high concentration of PAHs(∼120 ng m−3) observed during a haze event in December 1999 was likely influenced more by diesel vehicle exhaust than by gasoline exhaust, as well as air stagnation, as evidenced by the low carbon monoxide/elemental carbon (CO/EC) ratio of 205 found in this study and results reported by previous studies. The total PAHs associated with the size-segregated particles showed unimodal distributions. Compared to the unimodal size distributions of PAHs with modal peaks at < 0.12 μm measured in highway tunnels in Los Angeles (Venkataraman and Friedlander, 1994), four- to six-ring PAHs in our study had unimodal size distributions, peaking at the larger size range of 0.28–0.53 μm, suggesting the coagulation of freshly emitted ultrafine particles during transport to the sampling site. Further, the fraction of PAHs associated with coarse particles(> 1.8 μm) increased as the molecular weight of the PAHs decreased due to volatilization of fine particles followed by condensation onto coarse particles.  相似文献   

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