Romanías Manolis N, Dagaut Philippe, Bedjanian Yuri, Andrade-Eiroa Auréa, Shahla Roya, Emmanouil Karafas S, Papadimitriou Vassileios C, Spyros Apostolos
Institute de Combustion, Aérothermique, Réactivité et Environnement (ICARE)-CNRS, 1C Avenue de la Recherche Scientifique, 45071, Orléans, France.
J Phys Chem A. 2015 Mar 12;119(10):2006-15. doi: 10.1021/jp511468t. Epub 2015 Feb 25.
In the current study, the heterogeneous reaction of NO2 with soot and biosoot surfaces was investigated in the dark and under illumination relevant to atmospheric conditions (J(NO2) = 0.012 s(-1)). A flat-flame burner was used for preparation and collection of soot samples from premixed flames of liquid fuels. The biofuels were prepared by mixing 20% v/v of (i) 1-butanol (CH3(CH2)3OH), (ii) methyl octanoate (CH3(CH2)6COOCH3), (iii) anhydrous diethyl carbonate (C2H5O)2CO and (iv) 2,5 dimethyl furan (CH3)2C4H2O additive compounds in conventional kerosene fuel (JetA-1). Experiments were performed at 293 K using a low-pressure flow tube reactor (P = 9 Torr) coupled to a quadrupole mass spectrometer. The initial and steady-state uptake coefficients, γ0 and γ(ss), respectively, as well as the surface coverage, N(s), were measured under dry and humid conditions. Furthermore, the branching ratios of the gas-phase products NO (∼80-100%) and HONO (<20%) were determined. Soot from JetA-1/2,5-dimethyl furan was the most reactive [γ0 = (29.1 ± 5.8) × 10(-6), γ(ss)(dry) = (9.09 ± 1.82) × 10(-7) and γ(ss)(5.5%RH) = (14.0 ± 2.8)(-7)] while soot from JetA-1/1-butanol [γ0 = (2.72 ± 0.544) × 10(-6), γ(ss)(dry) = (4.57 ± 0.914) × 10(-7), and γ(ss)(5.5%RH) = (3.64 ± 0.728) × 10(-7)] and JetA-1/diethyl carbonate [γ0 = (2.99 ± 0.598) × 10(-6), γ(ss)(dry) = (3.99 ± 0.798) × 10(-7), and γ(ss)(5.5%RH) = (4.80 ± 0.960) × 10(-7)] were less reactive. To correlate the chemical reactivity with the physicochemical properties of the soot samples, their chemical composition was analyzed employing Raman spectroscopy, NMR, and high-performance liquid chromatography. In addition, the Brunauer-Emmett-Teller adsorption isotherms and the particle size distributions were determined employing a Quantachrome Nova 2200e gas sorption analyzer. The analysis of the results showed that factors such as (i) soot mass collection rate, (ii) porosity of the particles formed, (iii) aromatic fraction, and (iv) pre-existence of nitro-containing species in soot samples (formed during the combustion process) can be used as indicators of soot reactivity with NO2.
在当前研究中,研究了二氧化氮与烟灰和生物烟灰表面在黑暗以及与大气条件相关的光照条件下(J(NO2) = 0.012 s(-1))的非均相反应。使用平焰燃烧器从液体燃料的预混火焰中制备和收集烟灰样品。生物燃料是通过将20% v/v的(i)1-丁醇(CH3(CH2)3OH)、(ii)辛酸甲酯(CH3(CH2)6COOCH3)、(iii)无水碳酸二乙酯((C2H5O)2CO)和(iv)2,5-二甲基呋喃((CH3)2C4H2O)添加剂化合物混入传统煤油燃料(JetA-1)中制备而成。实验在293 K下使用与四极杆质谱仪联用的低压流动管反应器(P = 9 Torr)进行。分别测量了初始和稳态摄取系数γ0和γ(ss)以及表面覆盖率N(s),测量条件为干燥和潮湿条件。此外,还测定了气相产物一氧化氮(约80 - 100%)和亚硝酸(<20%)的分支比。来自JetA-1/2,5-二甲基呋喃的烟灰反应活性最高[γ0 = (29.1 ± 5.8) × 10(-6),γ(ss)(干燥) = (9.09 ± 1.82) × 10(-7),γ(ss)(5.5%相对湿度) = (