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Characteristics of atmospheric polycyclic aromatic hydrocarbons (PAHs) in gas and particle phase in April and July 2011 in Beijing, China

机译:2011年4月和2011年7月在中国北京市天然气和粒子阶段大气多环芳烃(PAHS)的特征

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Presence of atmospheric PAHs in urban and suburban region (Beijing, China) was studied in April and July 2011. Forty-four pairs of gas and particle (TSP) phase samples were collected every six day by high volume (Hi-Vol) air samplers at four sampling sites, and determined separately by GC/MS based on USEPA Method TO-13A. Average total concentration (gas + particles) of PAHs (T-PAHs) was 135.1±49.0 ng/m~3 and 181.2±40.9 ng/m~3 in April and July, respectively. Gas phase PAHs (G-PAHs) was the major fraction, comprising 63-92% of T-PAHs. Lighter (2-, 3-, 4-ring) and heavier (5-, 6-ring) PAHs were found predominantly in gas and particle phase, respectively. 2- to 6-ring PAHs contributed 10%, 53%, 26%, 7% and 4% of T-PAHs, respectively. Five major PAHs, naphthalene (NAP), fluorene (FLU), PHE, fluoranthene (FLA), and pyrene (PYR) contributed 70 - 90% of T-PAHs. G-PAHs increased significantly while PAHs in particle phase (P-PAHs) decreased from April to July. Volatilization from soil and more emission from power generation increase might explain the increase of G-PAHs, and the washout of P-PAHs along with particles might explain the decrease of P-PAHs. Given particulate organic carbon (OC) and elemental carbon (EC) being well correlated, P-PAHs was moderately correlated with OC and EC, suggesting that there were other mechanisms contributing to P-PAHs different from those of OC/EC. Significant correlation between P-PAHs with SO_2 and NO_2 suggested coal combustion and automobile exhaust to be contamination contributors.
机译:在4月和2011年7月研究了城市和郊区地区大气PAHS(北京,中国)。通过大容量(Hi-Vol)空气采样器每六天收集四十四对气体和颗粒(TSP)相样品在四个采样位点,基于USEPA方法到13A的GC / MS单独确定。 PAHS(T-PAHS)的平均总浓度(气体+颗粒)分别为4月和7月的135.1±49.0 ng / m〜3和181.2±40.9 ng / m〜3。气相PAHS(G-P-PAHS)是主要部分,包含63-92%的T-PAH。较轻(2-,3-,4环)和重度(5-,6环)PAH分别在气体和颗粒相中发现。 2至6环PAHs分别贡献了10%,53%,26%,7%和4%的T-PAH。五个主要的PAH,萘(午睡),芴(流感),pHE,氟(FLA)和芘(PYR)占T-PAH的70-90%。 G-PAHs显着增加,而P-P-P-P-P-P-P-P-PAHS)从4月到7月下降。来自土壤的挥发和发电增加的更多排放可能解释G-PAH的增加,P-PAH和颗粒的冲洗可能解释P-PAHS的降低。给定颗粒状有机碳(OC)和元素碳(EC)具有良好的相关性,P-PAHs与OC和EC中度相关,表明还有其他机制促使P-PAH不同于OC / EC的机制。 P-PAHS与SO_2和NO_2建议的煤燃烧和汽车排气之间的显着相关性成为污染贡献者。

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