Kinetics for the reactions of
methyl-2-methyl butanoate (M2MB)
and methyl-3-methyl butanoate (M3MB) with OH radicals were carried
out using the relative rate technique with gas chromatography–flame
ionization detection (RR-GC-FID) in the temperature range of 268–363
K and at 760 Torr of N2. The temperature-dependent rate
coefficients (k in cm3 molecule–1 s–1) for the reaction of M2MB with OH radicals
from 268 to 363 K were measured to be k
268 K
M2MB + OH = (4.62 ± 1.50) × 10–12, k
283 K
M2MB + OH = (4.46 ± 1.41) × 10–12, k
298 K
M2MB + OH = (4.27 ± 1.20) × 10–12, k
313 K
M2MB + OH = (3.99 ± 1.06) × 10–12, k
343 K
M2MB + OH = (3.65 ± 0.94) × 10–12, and k
363 K
M2MB + OH = (3.53 ± 0.80) × 10–12, respectively. Similarly, the temperature-dependent kinetics for
the reaction of M3MB with OH radicals were measured to be k
268 K
M3MB + OH = (4.49 ± 1.46) × 10–12, k
283 K
M3MB + OH = (4.40 ± 1.36) ×
10–12 , k
298 K
M3MB + OH = (4.14 ± 1.18)
× 10–12 , k
313 K
M3MB + OH =
(3.90 ± 1.06) × 10–12 , k
343 K
M3MB + OH = (3.52 ± 0.85) × 10–12, and k
363 K
M3MB + OH = (3.42 ± 0.81) × 10–12 respectively. Furthermore, computational calculations were carried
out for the title reactions using the CVT/SCT/ISPE method. In addition
to this, the product analyses for the studied reactions were elucidated
using gas chromatography–mass spectrometry (GC-MS) and gas
chromatography–infrared spectroscopy (GC-IR) as analytical
tools. Based on the identified products, the possible degradation
mechanisms were proposed. Atmospheric lifetimes, radiative forcings
(RFs), global warming potentials (GWPs), and photochemical ozone creation
potentials (POCPs) were also estimated.