高原城市昆明PM2.5中碳组分污染特征及来源分析
Characteristics and source analysis of carbonaceous components in PM2.5 at a plateau city, Kunming
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摘要: 为研究昆明市大气细颗粒物(PM2.5)中碳组分特征,于2014年7月21-27日、2014年10月27-11月2日、2014年1月9-15日、2015年4月14-20日采集了昆明中心城区3个采样点的大气PM2.5四季样品,采用IMPROVE热光分析法准确地测量了样品的有机碳(OC),元素碳(EC)及其中的8个碳组分含量,分析了OC和EC的时空变化特征、相关性关系及其比值特征,并采用因子分析方法研究了主要排放来源对总碳的贡献.结果显示,昆明城区的OC和EC年平均浓度分别为17.83±9.57 μg·m-3、5.11±4.29 μg·m-3,OC浓度显示冬季≈春季 > 秋季 > 夏季的变化趋势,EC浓度显示冬季>春季≈秋季>夏季的变化趋势,OC与EC浓度季节分布的不一致反映了两种不同性质碳组分排放源之间可能存在差异.从空间分布上来说,OC和EC均呈现金鼎山(工业区)> 东风东路(交通密集区)> 西山森林公园(清洁对照区)的特点,与PM2.5的空间分布规律保持一致.OC和EC的相关性在冬、春季较显著,而夏、秋季的相关性较弱.二次有机碳(SOC)对OC的贡献率在金鼎山、东风东路和西山森林公园的3个采样点分别为25.8%、23.7%和47.7%,SOC是总有机碳的重要组成部分.因子分析表明,4个季节燃煤、汽油车、柴油机排放及生物质燃烧对碳气溶胶贡献显著,都是碳组分的重要来源之一.其中,在常年尺度上,机动车排放和燃煤的混合贡献了碳组分的51.3%,是昆明城区碳气溶胶的最主要来源.Abstract: The purpose of this study was to investigate the characteristics of carbonaceous components in PM2.5 at three sites of Kunming. PM2.5 samples were collected during July 21 to 27, 2014 (Summer), October 27 to November 31, 2014 (Autumn), January 9 to 15, 2014 (Winter) and April 14 to 20, 2015 (Spring). Organic carbon (OC), elemental carbon (EC) and the eight carbon components were measured using thermal-optical method. And seasonal variation of OC and EC were investigated, the relationship between OC and EC and characteristics of OC/EC ratio were analyzed and compared. Factor analysis on the eight carbon fractions was performed to assess the main contribution to the total carbon emissions sources. Results show that the annual OC and EC concentrations in Kunming were 17.83±9.57 μg·m-3 and 5.11±4.29 μg·m-3, respectively. OC concentrations displayed seasonal variation as winter≈spring > autumn > summer. EC concentrations decreased in the order of winter>spring≈autumn>summer. The seasonal distribution of OC and EC suggests that there may be different soures of carbonous component. From the spatial distribution, the concentrations of OC and EC decreased as Jinding mountain (JDM) > East Dongfeng road (DR) > West mountain (WM), consistent with the spatial distribution of PM2.5. The OC/EC correlation coefficient is higher in winter and spring, while the correlation between summer and autumn is lower. The average concentrations of (secondary organic carbon) SOC accounted for 25.8%, 23.7% and 47.7% of OC at DR, JDM and WM, respectively. Results suggested that SOC was an important component of OC in PM2.5 in Kunming. In general, vehicle exhaust, coal combustion and biomass burning were the important sources for carbonaceous aerosol in each season. Among them, a combination of vehicle exhaust and coal combustion contributed 51.28%of carbonaceous aerosol on the scale of the year, which were the major sources for carbonaceous aerosol in Kunming.
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Key words:
- PM2.5 /
- organic carbon /
- element carbon /
- secondary organic carbon (SOC) /
- source
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[1] FU X, WANG X, HU Q, et al. Changes in visibility with PM2.5 composition and relative humidity at a background site in the Pearl River Delta region[J]. Journal of Environmental Sciences, 2016, 40(2):10-19. [2] PUI D Y H, CHEN S C, ZUO Z. PM2.5, in China:Measurements, sources, visibility and health effects, and mitigation[J]. Particuology, 2014, 13(2):1-26. [3] SILVA R, WEST J, ANENBERG S, et al. The impact of past and future climate change on global human mortality due to ozone and PM2.5 outdoor air pollution[R]. American Geophysical Union, 2012. [4] ANENBERG S C, SCHWARTZ J, SHINDELL D, et al. Global air quality and health co-benefits of mitigating near-term climate change through methane and black carbon emission controls[J]. Environmental Health Perspectives, 2012, 120(6):831-839. [5] ZHENG S, POZZER A, CAO C X, et al. Long-term (2001-2012) concentrations of fine particulate matter (PM2.5) and the impact on human health in Beijing, China[J]. Atmospheric Chemistry & Physics, 2015, 14(21):28657-28684. [6] SONG Y, ZHANG Y, DAI W. PM2.5 sources and their effects on human health in China:Case report[J]. Encyclopedia of Environmental Health, 2011:606-613. [7] KENDALL M. Fine airborne urban particles (PM2.5) sequester lung surfactant and amino acids from human lung lavage[J]. American Journal of Physiology Lung Cellular & Molecular Physiology, 2007, 293(4):1053-1058. [8] HO K F, LEE S C, CHAN, C K, et a1. Characterization of chemical species in PM2.5 and PM10 aerosols in HongKong[J]. Atmospheric Environment, 2003. 37:31-39. [9] 黄虹,李顺诚,曹军骥等.广州市夏季室内外PM2.5中有机碳、元素碳的分布特征[J].环境科学学报,2005,25(9):1242-1249. HUANG H, LEE S C, CAO J J, et al. Characterization of indoor/outdoor organic and elemental carbon in PM2.5 during summer in Guangzhou city[J]. Acta Scientiae Circumstantiae, 2005, 25(9):1242-1249(in Chinese).
[10] RAM K, SARIN M M. Day-night variability of EC, OC, WSOC and inorganic ions in urban environment of Indo-Gangetic Plain:Implications to secondary aerosol formation[J]. Atmospheric Environment, 2011, 45(2):460-468. [11] TIWARI S, SRIVASTAVA A K, BISHT D S, et al. Diurnal and seasonal variations of black carbon and PM2.5, over New Delhi, India:Influence of meteorology[J]. Atmospheric Research, 2013, 125-126(3):50-62. [12] LIOUSSE C, PENNER J E, CHUANG C, et al. A global three-dimensional model study of carbonaceous aerosols[J]. Journal of Geophysical Research Atmospheres, 1996, 1011(14):19411-19432. [13] 毕丽玫,郝吉明,宁平,等.昆明城区大气PM2.5中PAHs的污染特征及来源分析[J]中国环境科学,2015,35(3):659-667. BI L M, HAO J M, NING P, et al. Characteristics and sources apportionment of PM2.5-bound PAHs in Kunming[J]. China Environmental Science, 2015,35(3):659-667(in Chinese).
[14] 施择,毕丽玫,史建武,等. 昆明多风季节大气PM2.5污染特征及来源分析[J]. 环境科学与技术,2014,37(12):143-147. SHI Z, BI L M, SHI J W, et al. Characterization and source identification of PM2.5 in ambient air of Kunming in windy spring[J]. Environmental Science & Technology, 2014, 37(12):143-147(in Chinese).
[15] CHOW J C, WATSON J G,CHEN L W,et al. The IMPROVE_A temperature protocol for thermal/optical carbon analysis:Maintaining consistency with a long-term database[J]. Journal of the Air & Waste Management Association, 2007, 57(9):1014-1023. [16] ZHU J, XIA X, CHE H, et al. Study of aerosol optical properties at Kunming in southwest China and long-range transport of biomass burning aerosols from North Burma[J]. Atmospheric Research, 2016, 169:237-247. [17] TURPIN B J, LIM H J. Species contributions to PM2.5 mass concentrations:revising common assumptions for estimating organic mass[J] Aerosol Science and Technology, 2001, 35(1):602-610. [18] TURPIN B J, HUNT ZICKER J J. Identification of secondary organic aerosol episodes and quantification of primary and secondary organic aerosol concentrations during SCAQS[J].Atmospheric Environment, 1995, 29(23):3527-3544. [19] WANG T, NIE W, GAO J, et al. Air quality during the 2008 Beijing Olympics:Secondary pollutants and regional impact[J]. Atmospheric Chemistry & Physics, 2010, 10(16):7603-7615. [20] AW J, KLEEMAN M J. Evaluating the first-order effect of intraannual temperature variability on urban air pollution[J]. Journal of Geophysical Research Atmospheres, 2003, 108(D12):975-984. [21] ROTVIT L, JACOBSEN D. Temperature increase and respiratory performance of macroinvertebrates with different tolerances to organic pollution[J]. Limnologica-Ecology and Management of Inland Waters, 2013, 43(6):510-515. [22] CHU S H. Stable estimate of primary OC/EC ratios in the EC tracer method[J]. Atmospheric Environment, 2005, 39(8):1383-1392. [23] CHOW J C, WATSON J G, KUHNS H, et al. Source profiles for industrial, mobile, and area sources in the Big Bend Regional Aerosol Visibility and Observational study[J].Chemosphere,2004,54:185-208. [24] CAO J J, WU F, CHOW J C, et al. Characterization and source apportionment of atmospheric organic and elemental carbon during all and winter of 2003 in Xi'an, China[J]. Atmospheric Chemistry & Physics, 2005, 5:3561-3593. [25] CAO J J, LEE S C, HO K F, et al. Characterization of roadside fine particulate carbon and its eight fractions in Hong Kong[J].Aerosol and Air Quality Research,2006,6(2):106-122. -

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