FTIR spectroscopic investigation of the mechanism and kinetics of the heterogeneous reactions of NO2 and HNO3 with soot

Citation
U. Kirchner et al., FTIR spectroscopic investigation of the mechanism and kinetics of the heterogeneous reactions of NO2 and HNO3 with soot, J PHYS CH A, 104(39), 2000, pp. 8908-8915
Citations number
32
Categorie Soggetti
Physical Chemistry/Chemical Physics
Journal title
JOURNAL OF PHYSICAL CHEMISTRY A
ISSN journal
10895639 → ACNP
Volume
104
Issue
39
Year of publication
2000
Pages
8908 - 8915
Database
ISI
SICI code
1089-5639(20001005)104:39<8908:FSIOTM>2.0.ZU;2-9
Abstract
Soot samples from a spark generator, a flame, and a diesel passenger car we re either collected on a Teflon filter and transferred to an IR-transparent window or deposited directly from a flame onto the window and investigated by Fourier transform infrared (FTIR) spectroscopy. The soot-covered window s were mounted in a 10 cm vacuum cell connected to a standard flow system w ith He as carrier gas. Reactive gases, such as NO2 and HNO3, were added to the carrier gas flow at a concentration of (0.016 to 2.5) x 10(14) molecule cm(-3). FTIR spectra of soot samples before and after exposure to HNO3, NO 2, and O-3 are presented. Formation of IR absorption bands was analyzed as a function of exposure time. IR bands attributable to soot surface oxidatio n products and nitrogen containing species, e.g. -C=O, R-NO2, R-ONO2, and R -ONO were observed. The observed time dependence of the absorption bands of the spark generator soot can be fitted by two parallel reactions, a slow a nd a fast process. Both processes have a reaction order of n approximate to 0.2 (+/-0.3) for the NO2 + soot reaction and n approximate to 0.5 (+/-0.6) for the HNO3 + soot reaction. The number of active sites, N-max = 2.2 x 10 (14) molecules cm(-2) soot surface, has been estimated from saturation expe riments. Surface reaction probabilities depend on reactant concentration an d reaction time and were in the range of gamma approximate to 10(-6) to 10( -8) for the slow, and gamma approximate to 10(-3) to 10(-6) for the fast pr ocesses. The reaction probability on diesel engine soot was nearly 1 order of magnitude slower. It is concluded that the reaction of NO2, with soot ca nnot account for the HONO levels observed in urban air.