Kinetics of the Reaction of SH and SD with NO2
J. Phys. Chem. A, Vol. 110, No. 1, 2006 113
HSOO adduct to be very weak and unlikely to affect the
room temperature measurement of k1. (The upper limit for
∆0H298(association) for the formation of HSOO from HS and
O2, determined in this lab, is ∼6.5 kcal mol-1 and will be
published in a future paper.)
product of the atmospheric oxidation of SH by both O3 and
NO2. A SH radical in the remote clean troposphere has a lifetime
of ∼0.5 s (assuming 20 ppb O3 and 0.1 ppb NO2). This lifetime
assumes that HSO, formed in the reaction of SH with O3, will
not react further with ozone to regenerate SH. In regions with
higher NOx, the lifetime of SH decreases dramatically because
k1 ∼ 20 × k(O3 + SH).
Only one previous study, Fenter and Anderson,22 reported a
temperature dependence of k2. They employed a discharge flow
tube to generate SD using two different sources. One was the
abstraction of a deuterium atom from D2S by a H atom, and
the other was to react a deuterium atom with ethylene sulfide,
which yielded SD and ethene. NO2 was added through a
movable injector at the end of the flow tube. SD was detected
via laser-induced fluorescence. The results of our work are in
excellent agreement with the Fenter and Anderson22 study. The
results of Wang et al.5 on k2 at room temperature also agree
within the combined uncertainties with our value.
The history of k1 measurements is richer than that of SD with
several published studies (see Table 2). The range of measure-
ments is great, from the product study of Bulatov et al., which
reported 2.4 × 10-11 cm3 molecule-1 s-1 to the value of 12 ×
10-11 cm3 molecule-1 s-1 found by Schoenle et al.23 The
Stachnik and Molina study suggests the measurements of Friedl
et al.24 and Black16 suffered from the SH regeneration, as
outlined earlier, and added O2 to the reaction mixture to suppress
those regeneration schemes. The Wang et al.5 study measured
k1 as a function of temperature, using two sources of SH; the H
+ ethylene sulfide, already discussed, and the reaction of F with
H2S. Due to the rapidity of F + H2S relative to the H + H2S
reaction, the regeneration of SH via reactions 8 and 10 can be
minimized. It should be noted that the F atoms generated in
the Wang et al. study were created through the microwave
discharge of a CF4/He mixture. Using F2 creates difficulties, as
it participates in SH regeneration via the F2 + SH reaction. Our
results agree with those of Wang et al. The source chemistry
and regeneration of SH are discussed by Wang et al. and
Stachnik and Molina. Therefore, the following discussion
addresses only the apparent influence of SO on the measured
rate coefficient.
Our discovery of an interference by SO in the detection of
SH suggests that the previous studies of Stachnik and Molina
and of Black may have inadvertently influenced their measured
values. The results of Black et al. were influenced by secondary
SH generation, as noted by others before. When the influence
of the SO interference is not accounted for (see Table 1), we
measured a k1 value which is close to the result of Stachnik
and Molina. It should be stated that a direct comparison of the
influence of SO on the measurement of k1 is not possible because
this technique, like the work of Black and Friedl et al., is based
on LIF of SH, while that of Stachnik and Molina is based on
the absorption of SH. In the absorption measurement, the
influence would depend on the absorption cross section of SO
and SH at 323.7 nm, whereas in the LIF measurements, the
relative detection sensitivity is a convolution of the absorption,
fluorescence strength, and collection efficiency (mostly filler
transmission). These comments regarding the influence SO has
on the measurement of k1 should not be considered as anything
more than another possible difficulty associated with the
measurement of k1, by LIF at the R1 bandhead.
If HSO were removed mostly via its reaction with O3 in the
atmosphere, the conversion of SH to HSO followed by conver-
sion of HSO with O3 to give SH will form a catalytic ozone
destruction cycle. However, given that only a fraction of the
HSO reaction with O3 leads to SH and that the abundances (and
emissions) of H2S to the atmosphere are rather small, we do
not expect SH reaction to be a significant catalytic removal
pathway for ozone. If SH is oxidized in NOx rich regions, the
formed HSO will likely be converted to HSO2 and eventually
to SO2. Thus, in the case of either O3 reaction or NO2 reaction,
we expect SH to be rapidly oxidized to SO2.
Acknowledgment. This work was funded in part by
NOAA’s Air Quality Program.
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Atmospheric Implications
The atmospheric lifetime of SH is determined primarily by
its reaction with O3 and NO2. HSO is believed to be the primary