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
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.