Next Article in Journal
Simulation of Arctic Thin Ice Clouds with Canadian Regional Climate Model Version 6: Verification against CloudSat-CALIPSO
Next Article in Special Issue
Multi-Case Analysis of Ice Particle Properties of Stratiform Clouds Using In Situ Aircraft Observations in Hebei, China
Previous Article in Journal
How Effective and Prerequisite Are Electromagnetic Extremely Low Frequency (ELF) Recordings in the Schumann Resonances Band to Function as Seismic Activity Precursors
Previous Article in Special Issue
How Much Green Is Really “Cool”? Target Setting for Thermal Comfort Enhancement in a Warm, Humid City (Jakarta, Indonesia)
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Rate Constants and Branching Ratios for the Self-Reaction of Acetyl Peroxy (CH3C(O)O2) and Its Reaction with CH3O2

Université Lille, CNRS, UMR 8522-PC2A-Physicochimie des Processus de Combustion et de l’Atmosphère, F-59000 Lille, France
*
Author to whom correspondence should be addressed.
Atmosphere 2022, 13(2), 186; https://doi.org/10.3390/atmos13020186
Submission received: 17 December 2021 / Revised: 16 January 2022 / Accepted: 19 January 2022 / Published: 24 January 2022
(This article belongs to the Special Issue Feature Papers in Atmosphere Science)

Abstract

:
The self-reaction of acetylperoxy radicals (CH3C(O)O2) (R1) as well as their reaction with methyl peroxy radicals (CH3O2) (R2) have been studied using laser photolysis coupled to a selective time resolved detection of three different radicals by cw-CRDS in the near-infrared range: CH3C(O)O2 was detected in the Ã- X ˜ electronic transition at 6497.94 cm−1, HO2 was detected in the 2ν1 vibrational overtone at 6638.2 cm−1, and CH3O2 radicals were detected in the Ã- X ˜ electronic transition at 7489.16 cm−1. Pulsed photolysis of different precursors at different wavelengths, always in the presence of O2, was used to generate CH3C(O)O2 and CH3O2 radicals: acetaldehyde (CH3CHO/Cl2 mixture or biacetyle (CH3C(O)C(O)CH3) at 351 nm, and acetone (CH3C(O)CH3) or CH3C(O)C(O)CH3 at 248 nm. From photolysis experiments using CH3C(O)C(O)CH3 or CH3C(O)CH3 as precursor, the rate constant for the self-reaction was found with k1 = (1.3 ± 0.3) × 10−11 cm3s−1, in good agreement with current recommendations, while the rate constant for the cross reaction with CH3O2 was found to be k2 = (2.0 ± 0.4) × 10−11 cm3s−1, which is nearly two times faster than current recommendations. The branching ratio of (R2) towards the radical products was found at 0.67, compared with 0.9 for the currently recommended value. Using the reaction of Cl-atoms with CH3CHO as precursor resulted in radical profiles that were not reproducible by the model: secondary chemistry possibly involving Cl or Cl2 might occur, but could not be identified.

1. Introduction

The oxidation of volatile organic compounds (VOCs) in the troposphere is mainly driven by hydroxyl radicals (OH) and leads, after the addition of O2, to the formation of organic peroxy radicals (RO2). The fate of these RO2 radicals depends on the chemical composition of the environment: in a polluted atmosphere they react mainly with nitric oxide (NO) to form alkoxy radicals or react with nitrogen dioxide (NO2) to form peroxynitrates (RO2NO2). Subsequent to the reaction with NO, alkoxy radicals react with O2 to form hydroperoxy radicals (HO2). HO2 further oxidises NO into NO2 and thus regenerates OH, closing the quasi-catalytic cycle. The subsequent photolysis of produced NO2 is the only relevant chemical source of tropospheric ozone. In clean environments with low NOx (NOx = NO + NO2) concentrations, the dominant loss of RO2 is due to its reaction with HO2 forming hydroperoxides ROOH and terminating the radical reaction chain. In addition, RO2 radicals can react either with other RO2 as self-(RO2 + RO2) or cross-reaction (RO2 + R’O2), or with OH radicals (RO2 + OH) [1,2,3,4].
The majority of emitted biogenic non-methane hydrocarbons are isoprene (53%) and monoterpene species (16%) [5]. The photooxidation of these highly abundant compounds and their oxidation products form among other products significant amounts of acetylperoxy radicals (CH3C(O)O2). In the reaction with NO2, CH3C(O)O2 form peroxyacetyl nitrate (PAN), which is a toxic secondary air pollutant. In addition, PAN acts as the principal tropospheric reservoir species for NOx [6]. The only relevant source in the troposphere is this photochemical process, so that PAN is an indicator for photochemical oxidation. Its relatively long atmospheric lifetime of approximately two weeks allows for transport over long distances.
Model calculations of measured radical concentrations in different field studies underestimate HOx (HOx = OH + HO2) radical concentrations in remote regions with high emissions of VOCs from biogenic sources [7,8,9,10]. Even though instrumental interferences might be partially responsible for this underestimation by models [11,12], unidentified chemistry, erroneous rate constants, or branching ratios of key reactions might play an important role, too. Because acetylperoxy radicals are formed from biogenic precursors and serve as source for HO2, understanding their properties under low NOx conditions is of importance.
Major pathways for CH3C(O)O2 under low NOx are
  • its self-reaction
    2 CH3C(O)O2 → 2 CH3C(O)O + O2
  • its reaction with CH3O2
    CH3C(O)O2 + CH3O2 → CH3O + CH3C(O)O + O2
    → CH3C(O)OH + HCHO + O2
    whereby (R2a) maintains the radical pool, while (R2b) is a termination reaction. Therefore, a reliable determination of the branching ratio is of importance.
  • its reaction with HO2
    CH3C(O)O2 + HO2 → CH3C(O)OOH + O2
    → CH3C(O)OH + O3
    → CH3C(O)O + OH + O2
The first two pathways lead to radical chain terminating products (R3a) and (R3b), while the third path also regenerates OH (R3c).
Investigation of the CH3C(O)O2 reaction kinetics is not straight forward, because secondary chemistry cannot be avoided: CH3C(O)O, the product of the CH3C(O)O2 self-reaction (R1), rapidly decomposes and leads, after the addition of O2, to the formation of CH3O2 radicals:
CH3C(O)O → CH3 + CO2
CH3 + O2 (+M) → CH3O2 (+M)
Given that the rate constant of both reactions (R1) and (R2) are on the same order of magnitude, the CH3C(O)O2 decay is thus accelerated by (R2). To make things even more complex, (R2) has two pathways, one of which recycles CH3O2 through (R4) and (R5) and simultaneously generates HO2 radicals through (R6):
CH3O + O2 → CH2O + HO2
These HO2 radicals will in turn react with CH3C(O)O2, making it hard to distinguish between all reactions. This is even more true, as most of the former studies have been carried out by flash photolysis coupled to a rather unselective detection of the different peroxy radicals involved in the mechanism by UV absorption spectroscopy: the spectral overlap of different peroxy species in this region is prone to systematic errors in the quantitative detection [13,14,15,16,17]. Therefore, experiments quantifying different RO2 radicals by UV absorption are difficult to evaluate.
(R3) has been studied several times [18,19,20,21,22,23,24,25,26,27], especially since the discovery of the radical maintaining channel (R3c) in 2004 by Hasson et al. [26]. Good agreement on the rate constant and on the branching ratio has now been found. (R1) and (R2) have been studied less often, three times each and always using UV absorption spectroscopy. A good agreement on the rate constant for the CH3C(O)O2 self-reaction (R1) has been found in the three studies [14,16,17]. The same is true for (R2): a good agreement for the overall rate constant has been found in the three studies [16,17,28], which however must be fortuitous, as the authors used very different branching ratios for (R2a), ranging from 0 [17] over 0.65 [28] to 0.9 [16] for k2a/k2. These different branching ratios for (R2) were also used by the authors for the extraction of k1, so the agreement in k1 must also be fortuitous. A semi-empirical study on the rate constants of self- and cross-reactions of peroxy radicals, based on the calculated stabilisation energy of the tetroxide intermediate, predicts 1.4 × 10−11 cm3s−1 for (R1) and 7 × 10−12 cm3s−1 for (R2), which is in good agreement with experiments for (R1) and at the lower end for (R2) [29]. A summary of the available literature data together with the current recommendation by IUPAC [30] (which is very similar to the recommendation by JPL [31]) is given in Table 1.
Given the strong disagreement of the spare literature data, it seems important to investigate reaction (R1) and (R2) again using more selective detection methods. Here, CH3C(O)O2 and CH3O2 radicals were detected by absorption in the Ã- X ˜ electronic transition, and the HO2 radical by absorption in the 2ν1 overtone vibration band, all located in the near infrared region. To make up for the much smaller absorption cross section in this range compared to the UV range, cavity ring down spectroscopy (cw-CRDS) is used.

2. Experimental

2.1. Experimental Setup

The setup has been described in detail before [32,33,34,35,36,37] and is only briefly discussed here. The setup consisted of a 0.79 m long flow reactor made of stainless steel. The beam of a pulsed excimer laser (Lambda Physik LPX 202i) passed the reactor longitudinally. The flow reactor contained two identical continuous wave cavity ring-down spectroscopy (cw-CRDS) absorption paths, which were installed in a small angle with respect to the photolysis path. An overlap with the photolysis beam of 0.288 m is achieved with an excimer beam width delimited to 2 cm. Both beam paths were tested for a uniform overlap with the photolysis beam before experiments were performed. For this purpose, both cw-CRDS instruments were operated to simultaneously measure HO2 concentrations. Deviations between HO2 concentrations were less than 5%, demonstrating that the photolysis laser was well aligned, i.e., both light paths probed a very similar photolysed volume in the reactor. A small helium purge flow prevented the mirrors from being contaminated. Three different distributed feedback (DFB) lasers are used for the detection of the three species (CH3C(O)O2: Alcatel A1905LMI 3CN004 1 0CR, 6497 ± 18 cm−1, HO2; NEL NLK1E5GAAA, 6629 ± 17 cm−1; CH3O2: NEL NLK1B5EAAA, 7480 ± 20 cm−1). They are coupled into one of the cavities by systems of lenses and mirrors. Each probe beam passed an acousto-optic modulator (AOM, AAoptoelectronic, Orsay, France) to rapidly turn off the 1st order beam once a threshold for light intensity in the cavity was reached, in order to measure the ring-down event. One of the cavity mirrors is glued onto a piezo-transducer, which periodically modulates the cavity length in order to bring the cavity into resonance with the wavelength of the DFB lasers. The piezo is controlled by a homemade tracking system [38]. Then, the decay of light intensity is recorded by a fast 16-bit analogue acquisition card (PCI-6259, National Instruments) in a PC. The acquisition card has an acquisition frequency of 1.25 MHz and thus the ring-down signal is sampled every 800 ns and the data are transferred to the PC in real time via PCI bus. An exponential fit is applied to retrieve the ring-down time. Through synchronisation with the trigger of the photolysis laser, the delay between the photolysis pulse and the random occurrence of the ring-down event is registered [37]. A typical kinetic decay is obtained by accumulating ring-down events for 50–100 photolysis pulses and consists of several hundred individual ring-down times that have occurred randomly either before or after the photolysis pulse. The absorption coefficient α is derived from Equation (1).
α = [ A ] σ A = R L c ( 1 τ 1 τ 0 )
where τ is the ring-down time with an absorber present (i.e., at a given delay after the photolysis pulse); τ0 is the ring-down time with no absorber present (i.e., before the photolysis pulse); σA is the absorption cross section of the absorbing species A; RL is the ratio between cavity length (0.79 m) and effective absorption path (0.288 m); c is the speed of light. Typical ring-down times of the empty cavity were up to 100 µs, corresponding to the reflectivity of the mirrors of 0.99997.
Acetylperoxy radicals were generated from different precursors by either
  • pulsed 351 nm photolysis of acetaldehyde (CH3CHO)/Cl2/O2 mixtures:
    Cl2 + hν351 nm → 2 Cl
    CH3CHO + Cl → CH3CO + HCl
    CH3CO + O2 (+ M) → CH3C(O)O2 (+ M)
    CH3CO can also react with O2 through other pathways: it has been observed [39,40] that its reaction with O2 can also lead to low concentrations of HO2 and OH, depending on the amount of internal energy of CH3CO:
    CH3CO + O2CH2CO + HO2/CH2C(O)O + OH
    CH3CO might also decompose before reaction with O2:
    CH3CO → CH3 + CO
  • pulsed 351 nm photolysis of biacetyl (CH3C(O)C(O)CH3)/O2 mixtures:
    CH3C(O)C(O)CH3 + hν351 nm → 2 CH3CO
    followed by either (R9) or (R10)
  • Pulsed 248 nm photolysis of biacetyl (CH3C(O)C(O)CH3)/O2 mixtures:
    The same mechanism as above is utilized, but with a higher fraction of subsequent decomposition (R10)
  • Pulsed 248 nm photolysis of acetone (CH3C(O)CH3)/O2 mixtures
    CH3C(O)CH3 + hν248 nm → CH3CO + CH3
    followed by (R5), (R9), and (R10).
Using these different precursors thus allows obtaining different ratios of the initial radical concentrations. Table 2 summarizes the quantum yields such as those obtained from fitting the concentration time profiles for the different species for all precursors at the different wavelengths. It can be seen that the rate of decomposition (R10) is highest following the 248 nm photolysis of CH3C(O)C(O)CH3 and this precursor is also the one leading to the highest yield of initial HO2.
Acetaldehyde and biacetyl were prepared as diluted mixtures in a glass bulb. A small flow of this mixture was added to the main flow through a calibrated flow meter (Brunkhorst, Tylan). Acetone (Sigma Aldrich, France) was added to the mixture by flowing a small fraction of the main flow through a bubbler containing liquid acetone, kept in ice or in a thermostated water bath. All experiments were carried out at 298 K, and most experiments were performed at a total pressure of 100 Torr O2 (Praxair, 4.5). Some experiments were also carried out in 50 Torr helium (Praxair 4.5). The total flow rate was generally 450 cm3 min−1, leading to a flow velocity in the cell of 2.3 cm s−1 at 100 Torr. The photolysis repetition rate was generally 0.3 Hz, leading to a renewal of the gas mixture within the observation volume every second photolysis shot: occasional experiments were performed at lower photolysis rates or higher total flows to check for any possible influence of remaining reaction products.

2.2. Quantification of CH3C(O)O2

The relative spectrum has already been measured by Zalyubovsky et al. [41] in a large wavelength range and the absolute absorption cross section of the strongest band at 5582 cm−1 has been estimated. In a recent work, our group has determined absolute absorption cross sections in two wavelength ranges from 6094 to 6180 cm−1 and from 6420 to 6600 cm−1, corresponding to the C(O)O bend and to the OO stretch transition, respectively [42], whereby the cross sections were determined relative to the absorption cross section of HO2. Based on this work, CH3C(O)O2 was quantified at 6497.94 cm−1, with an absorption cross section σCH3C(O)O2 = 3.3 × 10−20 cm2. The spectrum of CH3C(O)O2 in this range consists of a large peak with FWHM of around 2.5 cm−1 sitting on a broad background, whereby the peak makes up roughly half of the absorption. To assure that the decays measured at the peak wavelength of CH3C(O)O2 are selective for this radical, kinetics have been measured at different wavelengths. In Figure 1, two decays measured on and off the peak wavelength, obtained following the 248 nm photolysis of [CH3C(O)CH3] = 8.5 × 1015 cm−3, are shown. No difference in the shape can be observed, and only the overall intensity varies. Therefore, it can be considered that our measurements at 6497.94 cm−1 are selective for CH3C(O)O2.

2.3. Quantification of HO2

HO2 has been detected on the strongest line of the 2ν1 band at 6638.2 cm−1. Pressure dependant absorption cross sections in helium [43,44] and in synthetic air [45,46,47] have been measured several times, but the cross section in pure O2 has been measured only once for a rather small absorption line [48]. Therefore, in the frame of this work, the absorption cross section at 6638.2 cm−1 and 100 Torr O2 to σ = 2.0 × 10−19 cm2 has been measured using the well-known kinetic method [49,50].
The absorption spectrum of HO2 in the near IR is very structured with sharp peaks, thus is it easy to verify the selectivity of the measurement towards HO2 by taking decays at the peak wavelength and just next to it, where the HO2 absorption is virtually zero. Figure 2 shows an example of both signals (online: black circles, offline: open black circles) measured following the 351 nm photolysis of Cl2 in presence of CH3CHO in 50 Torr helium. The offline HO2 signal perfectly matches the CH3C(O)O2 signal measured at the same conditions (blue circles, right y-axis): it is not unexpected that CH3C(O)O2 still absorbs in this wavelength range due to its broad background. From this observation, it can be considered that the HO2 concentrations can be obtained in a selective way by taking the difference between online and offline measurements (open squares). The small initial HO2 concentration (~7 × 1011 cm−3) results from (R9b) and corresponds to ~2% of the CH3C(O)O2 concentration (~3 × 1013 cm−3) (see Table 1).

2.4. Quantification of CH3O2

CH3O2 has been detected on the ν12 transition of the methyl torsion, with the maximum being located at 7488 cm−1. The spectrum in this range has been measured several times [50,51,52] and is, similar to the CH3C(O)O2 spectrum, made of a rather broad background with three distinct peaks. In order to check for the selectivity of the CH3O2 detection, decays were measured at different wavelengths: on top of the three peaks, as well as at different wavelengths on the broad background. Figure 3 summarizes the results.
There is a clear difference in shape between the decays on the peak wavelengths and those on the background wavelengths, an indication that the signal is due to the absorption of at least two different species. The second species should also be transient, i.e., not a stable product from the photolysis, because to make the signal in the background wavelength region look flat, the second absorber must decay roughly on the same time scale as the CH3O2 radical signal increases and should have roughly the same intensity as the absorption due to CH3O2. HO2 is not a possible candidate because (a) it is known that neither the OH vibration overtone [53] nor the Ã- X ˜ electronic transition [35,54] of HO2 are located in this wavelength range and (b) one would expect a structured spectrum in the case of HO2. However, it seems that the second absorbing species has a broadband type absorption: all decays in the background region have the same intensity and shape. The second (and major) species present in this system is the CH3C(O)O2 radical. While the spectrum of this radical has been measured in a large wavelength range in the near IR [41], it has never been measured around 7500 cm−1, and it is thought to be unlikely that its absorption feature reaches into this range [55]. An initial suspicion concerned the possible formation of the vinoxy peroxy radical, O2CH2CHO, formed from the O2 addition to the initially formed vinoxy radical, CH2CHO [56]. To our knowledge, the Ã- X ˜ electronic transition of this radical has never been measured but can be reasonably well expected in this wavelength range because its structure is closer to that of alkyl peroxy radicals than to the acetylperoxy radical. However, the upper limit of the branching fraction for the formation of the vinoxy radical in the reaction of Cl-atoms with CH3CHO is estimated to be only 7% [57], which would demand an unreasonably high absorption cross section, thus making it unlikely that this absorption is due to O2CH2CHO.
In order to remove doubts and to clarify the origin of this absorption, similar experiments have been carried out following the 248 nm photolysis in 100 Torr O2 of acetone. Figure 4 shows a typical example of [CH3C(O)CH3] = 8.5 × 1015 cm−3 (left graph) and 1.6 × 1016 cm−3 Cl2 in the presence of 5.9 × 1015 cm−3 CH3CHO (right graph). In the first system, only CH3O2 and CH3C(O)O2 (together with low concentrations of HO2 and OH) are expected: the main product (≈70%) is CH3O2 (black circles), CH3C(O)O2 (blue circles) is minor, and in the second system CH3C(O)O2 is expected to be the only product. However, in the offline CH3O2 measurements (scaled on the right y-axis to match the online CH3O2) of both experiments, a few data points in the first ms show a deviation from the online measurement, strengthening the hypothesis that CH3C(O)O2 is still absorbing around the CH3O2 band. The difference between online and offline measurements is less visible in Figure 4a compared to Figure 3 and Figure 4b for two reasons: (a) in Figure 4a, there is already a high initial CH3O2 concentration, making up the major fraction of the signal, while in Figure 3 and Figure 4b CH3O2 is only formed as a result of the CH3C(O)O2 self-reaction (see below) and (b) in Figure 4a. CH3C(O)O2 is decaying fast through the reaction with excess CH3O2 (see below), thus its impact on the CH3O2 offline signal is decreasing faster. For filled red and black circles in Figure 4b, see paragraph on Cl + CH3CHO as precursor.
Therefore, the signal measured at the online CH3O2 wavelength (7488.18 cm−1) is not selective for CH3O2 and must be treated as the sum of two species. Figure 5 shows four absorption signals from Figure 3: the three decays obtained at the peak wavelengths (c-d) as well as one at an offline wavelength (highlighted in magenta in Figure 3a). The CH3C(O)O2 signal is again shown as blue circles. The raw signals are given as open circles, again showing the very different shapes between online and offline signals. The full circles have been obtained by (i) subtracting 0.13 × αCH3C(O)O2 and (ii) by multiplying the obtained difference with a coefficient appropriate to bring all signals to the same absolute level: 1, 1.02, 1.6, and 4.1 for the red, blue, green, and black circles, in excellent agreement with the CH3O2 absorption cross sections at these wavelengths: 2.4, 2.35, 1.5, and 0.6 × 10−20 cm2, respectively.
The factor of 0.13 × αCH3C(O)O2 has been adjusted so as to give all signals from Figure 3 the same shape after multiplication with the corresponding relative absorption cross section. This test gives confidence that the signals at 7488.18 cm−1 can be used to get selective information on the CH3O2 concentration–-time profile, as long as the CH3C(O)O2 profile can be measured in a selective manner under the same conditions. From these experiments, it can be estimated that the absolute absorption cross section of CH3C(O)O2 around 7489 cm−1 is 13% of its value at 6497.94 cm−1, i.e., σCH3C(O)O2, 7488 cm−1 = 4.3 × 10−21 cm2.
As a conclusion, our experimental technique allows us to selectively follow the three key radicals playing a role during the study of the title reactions:
-
CH3C(O)O2 at 6497.94 cm−1 with σ = 3.3 × 10−20 cm2
-
HO2 at 6638.2 cm−1 with σ = 2.0 × 10−19 cm2 at 100 Torr O2 and 2.72 × 10−19 cm2 at 50 Torr He after subtracting the offline signal measured at 6637.15 cm−1
-
CH3O2 at 7489.16 cm−1 with σ = 2.4 × 10−20 cm2 after subtracting 0.13 × αCH3C(O)O2 such as measured at 6497.94 cm−1 (or, for convenience, by representing [CH3O2] as [CH3O2] + 0.179 × [CH3C(O)O2], with 0.179 = 4.3 × 10−21 cm2/2.4 × 10−20 cm2).
OH radicals, which are formed in the reaction of CH3CO + O2 as well as being produced by the cross reaction between CH3C(O)O2 + HO2, can in principle be quantified by cw-CRDS in the near IR, and absorption cross sections have been determined [58]. Some tests did allow the detecting of OH following the photolysis of CH3C(O)C(O)CH3 and CH3C(O)CH3 and resulting from (R9b), but the S/N ratio was poor: the OH lifetime is short in the presence of the precursors and peroxy radicals [2], and thus the concentrations are low. Moreover, CH3C(O)O2 is absorbing in this wavelength range as well as another species (a stable reaction product, possibly CH3OOH), so a rather small, short-lived OH-signal would be needed to be extracted from online-offline measurements. Therefore, no attempts were made to include OH signals in the modelling procedure. However, the initial OH concentration could be estimated and was roughly the same as the initial HO2 concentration under the same conditions. For this reason, a simplified reaction (R9b) leading to equal concentrations of OH and HO2 (see Table 3) has been used during modelling. The concentration was always small compared to CH3O2 or CH3C(O)O2, and hence the influence of (R9b) on the retrieved results for (R1) and (R2) is negligible. LIF measurements, also available in our set-up [37,59], were not possible due to strong quenching of the fluorescence, because experiments have been performed mostly in 100 Torr O2 in order to rapidly convert CH3O radicals into HO2.

3. Results and Discussion

3.1. Photolysis of CH3C(O)CH3 and CH3C(O)C(O)CH3

Typical concentration–time profiles obtained following the 248 nm photolysis of three different concentrations of acetone (left) and biacetyl (right) are presented in Figure 6a,b showing [CH3C(O)O2] and Figure 6c,d showing [CH3O2], i.e., α(CH3O2) converted with σ = 2.4 × 10−20 cm2, thus representing the sum of [CH3O2] + 0.179 × [CH3C(O)O2]. Figure 6e,f show [HO2]. The full lines represent the model given in Table 3, whereby the dashed line for the CH3O2 profiles represent the above sum and the full line represents the modelled [CH3O2] profile. The model in Table 3 contains only rate constants from the literature, except for the two title reactions: the self-reaction of CH3C(O)O2 (R1) and its cross reaction with CH3O2 (R2). It turned out that the profiles were not sensitive to the rate constant of the reaction with HO2 radicals (R3), and therefore the result from the most recent measurements [27], together with a branching ratio of 0.5 for the radical channel, has been used.
It can be seen that the radical profiles for all three species are very well reproduced for all conditions and precursors. However, some small deviations have been systematically observed, and cannot currently be explained:
The modelled CH3C(O)O2 profile is very well reproduced over the first few ms (up to 70–80% decay of its initial concentration), but decays become too fast thereafter, and are especially visible for the highest radical concentrations. This behaviour could not be corrected by adapting rate constants or branching ratios, because at longer reaction times the decay of CH3C(O)O2 is nearly exclusively governed by reaction with CH3O2, which itself is very well reproduced: slowing down the rate constant of (R2) does not remediate, because it would also have a similar impact at short reaction times, and would thus make the CH3C(O)O2 decay too slow in a short time. Trying to remediate by increasing k1 does not bring success neither, because (a) it increases the decay rate even more at short reaction times, when [CH3C(O)O2] is still high, and (b) it will increase the CH3O2 concentration well above the measurements. An explanation for this could be that, if a reaction product would absorb at the same wavelength than CH3C(O)O2, it is thought that the CH3C(O)O2 measurement is selective, because the profiles “online CH3C(O)O2 “ and “offline HO2” always have the same shape, despite a difference in the absorption cross section for CH3C(O)O2 of a factor of four between both wavelengths (see Figure 2). Another explanation could be an unidentified continuous formation of CH3C(O)O2. However, this is unlikely as it was observed with all precursors and a continuous formation would result in an increased formation of CH3O2 due to a sustained self-reaction. Currently, this deviation cannot be explained, but as it occurs only when [CH3C(O)O2] is already low, it is highly probable that the impact on the retrieved rate constants for (R1) and (R2) is very minor.
Another small deviation observed for all precursors and all conditions was a slight, systematic underestimation of HO2 at low radical concentrations: the experimental [HO2] profiles in a typical series such as shown in Figure 6 need to be decreased by around 10% for the lowest concentration. Alternatively, if HO2 was tentatively increased through either decreasing rate constants for its consumptions or increasing yields for its production, it was overestimated by around 10% at the highest radical concentrations. All HO2 in the mechanism of Table 3 originates from radical–radical reactions, and thus it will not be possible to bring into agreement these profiles under all conditions. It seems that a small fraction of HO2 radicals originates from a unimolecular (or pseudo-first order) process. It could also be the case that a sizeable fraction of HO2 is complexed with the precursor even at room temperature, as proposed by Hui et al. [27] However, no parameter could be found that led to satisfactory results over the entire concentration range. Moreover, the effect is very similar for acetone and biacetyle, which would suppose a similar equilibrium constant.
Interestingly, experiments at a total pressure of 200 Torr O2 can be very well simulated for all radicals with the rate constants from Table 3, except that the profile for HO2 radicals decays too fast at longer reaction times. Figure 7 shows a series of measurements following the 248 nm biacetyle photolysis at a total pressure of 200 Torr. CH3O2 and CH3C(O)O2 profiles are very well reproduced, but experimental HO2 profiles decay much faster than predicted by the model (full lines). An increase of the rate constant for the HO2 self-reaction from 1.7 × 10−12 cm3s−1 to 5 × 10−12 cm3s−1 leads to good reproduction of the HO2 profiles (dashed black line in HO2 profiles, Figure 7c). While it is known that this rate constant is pressure dependent, only a small increase up to around 2 × 10−12 cm3s−1 would be expected with an increase in O2 pressure from 100 to 200 Torr [61]. The effect was on the same order when acetone photolysis was the precursor (the rate constant for the HO2 self-reaction had to be increased to 4 × 10−12 cm3s−1 to well-reproduce the decay of the HO2 profiles). Such an observation points towards a strong chaperone effect of both precursors, as already proposed by Hui et al., and more experiments focussed on this subject are planned in the future. On the other hand, HO2 decays during 100 Torr experiments with comparable precursor concentration can be well reproduced using 1.7 × 10−12 cm3s−1 for the HO2 self-reaction. The increase of this rate constant has a negligible impact on the profiles of the other two species and on the retrieved results for (R1) and (R2): this is expected, as the cross reactions with HO2 are only minor paths for both species under our conditions, where the HO2 concentration is 4–5 times lower than the concentration of the two other species. Therefore, the influence of this observation is at the most very minor with respect to the retrieved rate constants and branching ratios of the title reactions. Experiments at higher temperature are planned in the future to exclude any influence of complexation on the HO2 profile.

3.2. Comparison with Literature Rate Constants

Figure 8 shows all three radical profiles (CH3O2 in blue, CH3C(O)O2 in red and HO2 in green) for the highest initial radical concentration of the acetone photolysis experiment at 100 Torr from Figure 6 (red symbols, left column). The four graphs show different models using the mechanism from Table 3 with rate constants for (R1) and (R2) from Table 1 (the model of Roehl et al. [16] is close to IUPAC and is not reproduced here): Figure 8a represents the best fit as deduced in this work and as given in Table 3. Figure 8b–d present the same model except for the rate constants for (R1) and (R2) that have been changed to different literature results. Figure 8b represents the model such as proposed by Maricq and Szente [17]: even though the rate constant for the self-reaction of CH3C(O)O2 is faster than in our model, the CH3C(O)O2 profile decays not fast enough compared to the observation. This is due to the fact that the authors propose only molecular products for the cross reaction with CH3O2—the HO2 profile is not reproduced at all because the radical path of (R2) is the major source of HO2—, and thus the removal of CH3C(O)O2 by both cross reactions is too slow. The two other models have higher radical yields for the cross reaction with CH3O2 (0.9 for IUPAC [30] and 0.65 for Villenave and Lesclaux [28]), but around a factor of two lower rate constant for k2. This leads to more or less acceptable HO2 profiles, however the CH3O2 profiles are not well reproduced: in both cases, the concentration initially increases before decaying roughly at the observed rate. This initial increase in CH3O2 concentrations has never been observed in our experiments. Moreover, the lower rate constant for (R2) leads to decays for CH3C(O)O2 that are much slower than the observed profiles. A comparison with the predictions of the semi-empirical study [29] is not shown, because no branching ratios are predicted, which is indispensable for the prediction of concentration–time profiles. However, the rate constant for (R2) predicted in the semi-empirical study, based on the stabilization energy of the tetroxide intermediate, is 7 × 10−12 cm3s−1 even below the lowest experimental value and it can therefore be supposed that the semi-empirical method is not reliable for this type of cross-reaction. To our knowledge, no theoretical calculations concerning mechanism and rate constants of (R1) and (R2), and more importantly the branching ratio for (R2), have been carried out, but that would certainly be interesting.

3.3. Reaction of Cl-Atoms with CH3CHO as Precursor

In all earlier studies summarized in Table 1, CH3C(O)O2 radicals have been prepared by H-atom abstraction from CH3CHO through reaction with Cl-atoms, whereby Cl-atoms have been generated from 351 nm photolysis of Cl2, a wavelength where CH3CHO does not absorb. The present study is the first one that used different precursors. Therefore, this precursor was also tested in this experiment. Another reason to try this precursor was that this reaction system should be a clean source of CH3C(O)O2 radicals next to low concentrations of O2CH2C(O)H, OH, and HO2 but no initial CH3O2. This reaction system should be especially suited for measuring the rate constant of (R1), as the initial decay of CH3C(O)O2 radicals is not perturbed by already present CH3O2 radicals. Figure 9 shows the profiles of the three radical species obtained following the 351 nm photolysis of [Cl2] = (0.34–1.6) × 1016 cm−3 in the presence of [CH3CHO] = 5.9 × 1015 cm−3, together with the simulation using the model from Table 3. To our great surprise, the measured CH3O2 profiles were not at all reproduced by the model, as the predicted CH3O2 concentration rises much too fast and too high. Moreover, the predicted HO2 rises too fast and too high, which is a direct consequence of the high CH3O2 concentration: HO2 is nearly exclusively formed as a product of (R2). CH3C(O)O2 also decays too fast, which is also a consequence of the too high CH3O2 concentration: the dashed magenta line in Figure 9 presents the fraction of CH3C(O)O2 radicals that has been removed through reaction with CH3O2 for the highest radical concentration (blue symbols). Decreasing the rate constant for (R1) to k1 = 1 × 10−11 cm3s−1 improves the agreement for CH3C(O)O2 profiles somewhat (although still too fast after around 70% of the decay, as for the other precursors), but even then the two other radicals are still much overestimated.
To test for unidentified secondary chemistry of Cl-atoms or acetaldehyde, experiments have been carried out using different ratios of Cl/CH3CHO: Figure 10 shows the three radical profiles of experiments using identical Cl2 concentrations and photolysis energies, but the concentration of CH3CHO has been changed by a factor of 3, from (3.1 to 9.2) × 1015 cm−3. No change in any of the three radical profiles is observed, from which it can be concluded that CH3CHO is not involved in the reaction system other than its reaction with Cl-atoms. Similar experiments have been carried out by changing the repetition rate of the photolysis laser between 1 and 0.1 Hz (experiments were typically carried out at 0.3 Hz) to test for possibly remaining reaction products. However, no change is observed, other than a slight increase of HO2 with increasing repetition rate (possibly due to reaction of Cl-atoms with remaining reaction products such as CH2O) (Figure 10d). CH3CO radicals are probably less energetic when using this precursor (H-abstraction from CH3CHO) compared to the photolysis of acetone or biacetyle. To test if the difference in internal energy of the initial radical can bias the results, Cl + CH3CHO experiments in 50 Torr helium have been carried out, but there was no difference in the profiles of the different radicals compared to the 100 Torr O2 experiments: there was always too much CH3O2.
From the above discussions, it can be concluded with reasonable confidence that the CH3O2 measurements are selective for CH3O2 in the same way that they are for the other precursors: Figure 4b shows CH3O2 online and offline measurements and the simultaneously obtained CH3C(O)O2 absorption profile, multiplied by 0.13. The absorption at t = 0 s starts at the same point, indicating that all absorption at t = 0 s is due to CH3C(O)O2 and no CH3O2 is formed initially, as expected. By treating the signal as shown in Figure 5, i.e., subtracting the absorbance due to CH3C(O)O2 from both online (black open circles) and offline (red open circles), identical signals (filled black and red circles) are obtained, indicating that with this precursor the CH3O2 signal can also be taken as selective if treated as the sum of α(CH3O2) + 0.13 × α(CH3C(O)O2).
Finally, the rate constants from the literature, which all used Cl + CH3CHO as precursor, have been tested against the profiles of the three radicals, and the result of the corresponding models is shown in Figure 11 for the highest radical concentration from Figure 9 (CH3O2 in blue, CH3C(O)O2 in red and HO2 in green): Figure 9a shows again the model from Table 3. Figure 9b represents k1 and k2 as given by Maricq and Szente [17]: the CH3C(O)O2 decay is reasonably well reproduced, but this is again the result of the branching ratio of (R2), which predicts no radical products, leading to much slower cross reactions for CH3C(O)O2. However, again, the HO2 profile is not at all reproduced, and even with this model the CH3O2 concentration is still strongly overpredicted. The situation is similar for the two other models: none of them can reasonably well reproduce all three radical profiles.
Therefore, no explanation can currently be given for the strong difference in radical profiles between the different precursors, so the mystery remains. Some unidentified secondary chemistry involving Cl, Cl2, or HCl might take place.

4. Conclusions

The rate constant of the self-reaction of CH3C(O)O2 radicals as well as the rate constant and branching ratio for the radical path for its cross reaction with CH3O2 radicals has been measured by following the concentration time profiles of the three key radicals CH3C(O)O2, CH3O2 and HO2 in a selective way. The rate constant of the self-reaction has been found as k1 = (1.35 ± 0.3) × 10−11 cm3s−1, in good agreement with current recommendations. However, the rate constant for the cross reaction has been found as k2 = (2.0 ± 0.4) × 10−11 cm3s−1, which around two times faster than currently recommended. The yield for the radical maintaining pathway (R2a) has been found as α = 0.67, which is slightly below the current IUPAC recommendation (0.9). Some systematic, unexplained deviations between model and measurement persist: the CH3C(O)O2 concentration seems to be maintained at long reaction times at a higher concentration than predicted by the model. This could be explained by the reaction product absorbing at the same wavelength as CH3C(O)O2, even though tests have been carried out which do not confirm this hypothesis. Another unexplained deviation persists in that at higher total pressures (200 Torr O2 instead of 100 Torr O2), the HO2 concentration decays faster than the model predicts: this could be due to a complexation of HO2 with the precursor and a resulting increased rate constant for the self-reaction. However, this explanation, even though already mentioned by Hui et al. [27], is not satisfying, as the profiles can be very well reproduced using the same precursor concentrations in 100 Torr O2 without accounting for complexation. The most mysterious, unexplained observation occurred when the reaction of Cl-atoms with CH3CHO was the precursor for CH3C(O)O2 radicals: the observed CH3O2 concentration was much higher than predicted by the model. Unidentified secondary chemistry involving Cl, Cl2, or HCl might be involved, but currently no explanation can be given for this observation. Thus, further experiments will be necessary to understand this phenomenon.

Author Contributions

Conceptualization, methodology, validation and formal analysis, M.A and C.F.; investigation and data curation, M.A.; writing—original draft preparation, C.F.; writing—review and editing, M.A and C.F.; supervision, project administration, and funding acquisition, C.F. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by French ANR agency under contract No. ANR-11-Labx-0005-01 CaPPA, the Région Hauts-de-France, the Ministère de l’Enseignement Supérieur et de la Recherche (CPER Climibio) and the European Fund for Regional Economic Development.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data can be obtained from the authors on request.

Acknowledgments

This project was supported by the French ANR agency under contract No. ANR-11-Labx-0005-01 CaPPA (Chemical and Physical Properties of the Atmosphere), the Région Hauts-de-France, the Ministère de l’Enseignement Supérieur et de la Recherche (CPER Climibio) and the European Fund for Regional Economic Development. The authors thank E. Assaf and M. Rolletter for help with initial measurements. This manuscript is dedicated to Robert Lesclaux.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Orlando, J.J.; Tyndall, G.S. Laboratory studies of organic peroxy radical chemistry: An overview with emphasis on recent issues of atmospheric significance. Chem. Soc. Rev. 2012, 41, 6294–6317. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  2. Fittschen, C. The reaction of peroxy radicals with OH radicals. Chem. Phys. Lett. 2019, 725, 102–108. [Google Scholar] [CrossRef]
  3. Assaf, E.; Song, B.; Tomas, A.; Schoemaecker, C.; Fittschen, C. Rate Constant of the Reaction between CH3O2 Radicals and OH Radicals revisited. J. Phys. Chem. A 2016, 120, 8923–8932. [Google Scholar] [CrossRef] [PubMed]
  4. Calvert, J.G.; Derwent, R.G.; Orlando, J.J.; Tyndall, G.S.; Wallington, T.J. Mechanisms of Atmospheric Oxidation of the Alkanes; Oxford University Press: New York, NY, USA, 2008. [Google Scholar]
  5. Guenther, A.B.; Jiang, X.; Heald, C.L.; Sakulyanontvittaya, T.; Duhl, T.; Emmons, L.K.; Wang, X. The Model of Emissions of Gases and Aerosols from Nature version 2.1 (MEGAN2. 1): An extended and updated framework for modeling biogenic emissions. Geosci. Model Dev. 2012, 5, 1471–1492. [Google Scholar] [CrossRef] [Green Version]
  6. Fischer, E.V.; Jacob, D.J.; Yantosca, R.M.; Sulprizio, M.P.; Millet, D.B.; Mao, J.; Paulot, F.; Singh, H.B.; Roiger, A.; Ries, L.; et al. Atmospheric peroxyacetyl nitrate (PAN): A global budget and source attribution. Atmos. Chem. Phys. 2014, 14, 2679–2698. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  7. Tan, D.; Faloona, I.; Simpas, J.B.; Brune, W.; Shepson, P.B.; Couch, T.L.; Sumner, A.L.; Carroll, M.A.; Thornberry, T.; Apel, E.; et al. HOx budgets in a deciduous forest: Results from the PROPHET summer 1998 campaign. J. Geophys. Res. Atmos. 2001, 106, 24407–24427. [Google Scholar] [CrossRef]
  8. Lelieveld, J.; Butler, T.M.; Crowley, J.N.; Dillon, T.J.; Fischer, H.; Ganzeveld, L.; Harder, H.; Lawrence, M.G.; Martinez, M.; Taraborrelli, D.; et al. Atmospheric oxidation capacity sustained by a tropical forest. Nature 2008, 452, 737–740. [Google Scholar] [CrossRef]
  9. Hofzumahaus, A.; Rohrer, F.; Lu, K.; Bohn, B.; Brauers, T.; Chang, C.C.; Fuchs, H.; Holland, F.; Kita, K.; Kondo, Y.; et al. Amplified trace gas removal in the troposphere. Science 2009, 324, 1702–1704. [Google Scholar] [CrossRef] [Green Version]
  10. Wolfe, G.M.; Thornton, J.A.; Bouvier-Brown, N.C.; Goldstein, A.H.; Park, J.H.; McKay, M.; Matross, D.M.; Mao, J.; Brune, W.H.; LaFranchi, B.W.; et al. The Chemistry of Atmosphere-Forest Exchange (CAFE) Model—Part 2: Application to BEARPEX-2007 observations. Atmos. Chem. Phys. 2011, 11, 1269–1294. [Google Scholar] [CrossRef] [Green Version]
  11. Mao, J.; Ren, X.; Brune, W.H.; Van Duin, D.M.; Cohen, R.C.; Park, J.-H.; Goldstein, A.H.; Paulot, F.; Beaver, M.R.; Crounse, J.D.; et al. Insights into hydroxyl measurements and atmospheric oxidation in a California forest. Atmos. Chem. Phys. 2012, 12, 8009–8020. [Google Scholar] [CrossRef] [Green Version]
  12. Fittschen, C.; Al Ajami, M.; Batut, S.; Ferracci, V.; Archer-Nicholls, S.; Archibald, A.T.; Schoemaecker, C. ROOOH: A missing piece of the puzzle for OH measurements in low-NO environments? Atmos. Chem. Phys. 2019, 19, 349–362. [Google Scholar] [CrossRef] [Green Version]
  13. Addison, M.C.; Burrows, J.P.; Cox, R.A.; Patrick, R. Absorption spectrum and kinetics of the acetylperoxy radical. Chem. Phys. Lett. 1980, 73, 283–287. [Google Scholar] [CrossRef]
  14. Moortgat, G.; Veyret, B.; Lesclaux, R. Absorption spectrum and kinetics of reactions of the acetylperoxy radicals. J. Phys. Chem. 1989, 93, 2362–2368. [Google Scholar] [CrossRef]
  15. Lightfoot, P.D.; Cox, R.A.; Crowley, J.N.; Destriau, M.; Hayman, G.D.; Jenkin, M.E.; Moortgat, G.K.; Zabel, F. Organic peroxy radicals—Kinetics, spectroscopy and tropospheric chemistry. Atmos. Environ. Part A-Gen. Top. 1992, 26, 1805–1961. [Google Scholar] [CrossRef]
  16. Roehl, C.M.; Bauer, D.; Moortgat, G.K. Absorption spectrum and kinetics of the acetylperoxy radical. J. Phys. Chem. 1996, 100, 4038–4047. [Google Scholar] [CrossRef]
  17. Maricq, M.M.; Szente, J.J. The CH3C(O)O2 Radical. Its UV Spectrum, Self-Reaction Kinetics, and Reaction with CH3O2. J. Phys. Chem 1996, 100, 4507–4513. [Google Scholar] [CrossRef]
  18. Niki, H.; Maker, P.D.; Savage, C.M.; Breitenbach, L.P. FTIR study of the kinetics and mechanism for chlorine-atom-initiated reactions of acetaldehyde. J. Phys. Chem. 1985, 89, 588–591. [Google Scholar] [CrossRef]
  19. Moortgat, G.K.; Veyret, B.; Lesclaux, R. Kinetics of the reaction of HO2 with CH3C(O)O2 in the temperature range 253–368 K. Chem. Phys. Lett. 1989, 160, 443–447. [Google Scholar] [CrossRef]
  20. Crawford, M.A.; Wallington, T.J.; Szente, J.J.; Maricq, M.M.; Francisco, J.S. Kinetics and Mechanism of the Acetylperoxy + HO2 Reaction. J. Phys. Chem. A 1999, 103, 365–378. [Google Scholar] [CrossRef]
  21. Tomas, A.; Villenave, E.; Lesclaux, R. Reactions of the HO2 Radical with CH3CHO and CH3C(O)O2 in the Gas Phase. J. Phys. Chem. A 2001, 105, 3505–3514. [Google Scholar] [CrossRef]
  22. LeCrane, J.-P.; Rayez, M.-T.; Rayez, J.-C.; Villenave, E. A reinvestigation of the kinetics and the mechanism of the CH3C(O)O2+ HO2 reaction using both experimental and theoretical approaches. Phys. Chem. Chem. Phys. 2006, 8, 2163–2171. [Google Scholar] [CrossRef] [PubMed]
  23. Horie, O.; Moortgat, G.K. Reactions of CH3C(O)O2 radicals with CH3O2 and HO2 between 263 and 333 K. A product study. J. Chem. Soc. Faraday Trans. 1992, 88, 3305–3312. [Google Scholar] [CrossRef]
  24. Jenkin, M.E.; Hurley, M.D.; Wallington, T.J. Investigation of the radical product channel of the CH3C(O)O2 + HO2 reaction in the gas phase. Phys. Chem. Chem. Phys. 2007, 9, 3149–3162. [Google Scholar] [CrossRef] [PubMed]
  25. Dillon, T.J.; Crowley, J.N. Direct Detection of OH Formation in the Reactions of HO2 with CH3C(O)O2 and Other Substituted Peroxy Radicals. Atmos. Chem. Phys. 2008, 8, 4877–4889. [Google Scholar] [CrossRef] [Green Version]
  26. Hasson, A.S.; Tyndall, G.S.; Orlando, J.J. A Product Yield Study of the Reaction of HO2 Radicals with Ethyl Peroxy (C2H5O2), Acetyl Peroxy (CH3C(O)O2), and Acetonyl Peroxy (CH3C(O)CH2O2) Radicals. J. Phys. Chem. A 2004, 108, 5979–5989. [Google Scholar] [CrossRef]
  27. Hui, A.O.; Fradet, M.; Okumura, M.; Sander, S.P. Temperature Dependence Study of the Kinetics and Product Yields of the HO2 + CH3C(O)O2 Reaction by Direct Detection of OH and HO2 Radicals Using 2f-IR Wavelength Modulation Spectroscopy. J. Phys. Chem. A 2019, 123, 3655–3671. [Google Scholar] [CrossRef] [Green Version]
  28. Villenave, E.; Lesclaux, R. Kinetics of the Cross Reactions of CH3O2 and C2H5O2 Radicals with Selected Peroxy Radicals. J. Phys. Chem. 1996, 100, 14372–14382. [Google Scholar] [CrossRef]
  29. Shallcross, D.E.; Raventos-Duran, M.T.; Bardwell, M.W.; Bacak, A.; Solman, Z.; Percival, C.J. A semi-empirical correlation for the rate coefficients for cross- and self-reactions of peroxy radicals in the gas-phase. Atmos. Environ. 2005, 39, 763–771. [Google Scholar] [CrossRef]
  30. Atkinson, R.; Baulch, D.L.; Cox, R.A.; Crowley, J.N.; Hampson, R.F.; Hynes, R.G.; Jenkin, M.E.; Rossi, M.J.; Troe, J. Evaluated Kinetic and Photochemical Data for Atmospheric Chemistry: Volume II—Gas Phase Reactions of Organic Species. Atmos. Chem. Phys. 2006, 6, 3625–4055. [Google Scholar] [CrossRef] [Green Version]
  31. Burkholder, J.B.; Sander, S.P.; Abbatt, J.P.; Barker, J.R.; Cappa, C.; Crounse, J.D.; Dibble, T.S.; Huie, R.E.; Kolb, C.E.; Kurylo, M.J.; et al. Chemical Kinetics and Photochemical Data for Use in Atmospheric Studies, Evaluation No. 19; JPL Publication: Pasadena, CA, USA, 2020. [Google Scholar]
  32. Shamas, M.; Assali, M.; Zhang, C.; Tang, X.; Zhang, W.; Pillier, L.; Schoemaecker, C.; Fittschen, C. Rate Constant and Branching Ratio for the Reactions of the Ethyl Peroxy Radical with Itself and with the Ethoxy Radical. ACS Earth Space Chem. 2022, 6, 181–188. [Google Scholar] [CrossRef]
  33. Thiebaud, J.; Aluculesei, A.; Fittschen, C. Formation of HO2 Radicals from the Photodissociation of H2O2 at 248 nm. J. Chem. Phys. 2007, 126, 186101. [Google Scholar] [CrossRef] [PubMed]
  34. Thiebaud, J.; Fittschen, C. Near Infrared cw-CRDS Coupled to Laser Photolysis: Spectroscopy and Kinetics of the HO2 Radical. Appl. Phys. B 2006, 85, 383–389. [Google Scholar] [CrossRef]
  35. Assaf, E.; Asvany, O.; Votava, O.; Batut, S.; Schoemaecker, C.; Fittschen, C. Measurement of line strengths in the à 2A’ ← X 2A” transition of HO2 and DO2. J. Quant. Spectrosc. Radiat. Transf. 2017, 201, 161–170. [Google Scholar] [CrossRef]
  36. Zhang, C.; Shamas, M.; Assali, M.; Tang, X.; Zhang, W.; Pillier, L.; Schoemaecker, C.; Fittschen, C. Absolute Absorption Cross-Section of the Ã←X~ Electronic Transition of the Ethyl Peroxy Radical and Rate Constant of Its Cross Reaction with HO2. Photonics 2021, 8, 296. [Google Scholar] [CrossRef]
  37. Parker, A.; Jain, C.; Schoemaecker, C.; Szriftgiser, P.; Votava, O.; Fittschen, C. Simultaneous, Time-Resolved Measurements of OH and HO2 Radicals by Coupling of High Repetition Rate LIF and cw-CRDS Techniques to a Laser Photolysis Reactor and its Application to the Photolysis of H2O2. Appl. Phys. B 2011, 103, 725–733. [Google Scholar] [CrossRef]
  38. Votava, O.; Masat, M.; Parker, A.E.; Jain, C.; Fittschen, C. Microcontroller Based Resonance Tracking unit for Time Resolved Continuous wave Cavity-Ringdown Spectroscopy Measurements. Rev. Sci. Instrum. 2012, 83, 043110. [Google Scholar] [CrossRef] [PubMed]
  39. Morajkar, P.; Bossolasco, A.; Schoemaecker, C.; Fittschen, C. Photolysis of CH3CHO at 248 nm: Evidence of Triple Fragmentation from Primary Quantum Yield of CH3 and HCO Radicals and H Atoms. J. Chem. Phys. 2014, 140, 214308. [Google Scholar] [CrossRef]
  40. Blitz, M.A.; Heard, D.E.; Pilling, M.J. OH formation from CH3CO+O2: A convenient experimental marker for the acetyl radical. Chem. Phys. Lett. 2002, 365, 374–379. [Google Scholar] [CrossRef]
  41. Zalyubovsky, S.J.; Glover, B.G.; Miller, T.A. Cavity Ringdown Spectroscopy of the à − X ˜ Electronic Transition of the CH3C(O)O2 Radical. J. Phys. Chem. A 2003, 107, 7704–7712. [Google Scholar] [CrossRef]
  42. Rolletter, M.; Assaf, E.; Assali, M.; Fuchs, H.; Fittschen, C. The absorption spectrum and absolute absorption cross sections of acetylperoxy radicals, CH3C(O)O2 in the near IR. J. Quant. Spectrosc. Radiat. Transf. 2020, 245, 106877. [Google Scholar] [CrossRef]
  43. Thiebaud, J.; Crunaire, S.; Fittschen, C. Measurement of Line Strengths in the 2n1 Band of the HO2 Radical using Laser Photolysis / Continous wave Cavity Ring Down Spectroscopy (cw-CRDS). J. Phys. Chem. A 2007, 111, 6959–6966. [Google Scholar] [CrossRef] [PubMed]
  44. Tang, Y.; Tyndall, G.S.; Orlando, J.J. Spectroscopic and Kinetic Properties of HO2 Radicals and the Enhancement of the HO2 Self Reaction by CH3OH and H2O. J. Phys. Chem. A 2010, 114, 369–378. [Google Scholar] [CrossRef] [PubMed]
  45. Ibrahim, N.; Thiebaud, J.; Orphal, J.; Fittschen, C. Air-Broadening Coefficients of the HO2 Radical in the 2v1 Band Measured Using cw-CRDS. J. Mol. Spectrosc. 2007, 242, 64–69. [Google Scholar] [CrossRef]
  46. Assaf, E.; Liu, L.; Schoemaecker, C.; Fittschen, C. Absorption spectrum and absorption cross sections of the 2v1 band of HO2 between 20 and 760 Torr air in the range 6636 and 6639 cm−1. J. Quant. Spectrosc. Radiat. Transf. 2018, 211, 107–114. [Google Scholar] [CrossRef]
  47. Onel, L.; Brennan, A.; Gianella, M.; Ronnie, G.; Lawry Aguila, A.; Hancock, G.; Whalley, L.; Seakins, P.W.; Ritchie, G.A.D.; Heard, D.E. An intercomparison of HO2 measurements by fluorescence assay by gas expansion and cavity ring-down spectroscopy within HIRAC (Highly Instrumented Reactor for Atmospheric Chemistry). Atmos. Meas. Tech. 2017, 10, 4877–4894. [Google Scholar] [CrossRef] [Green Version]
  48. Assali, M.; Rakovsky, J.; Votava, O.; Fittschen, C. Experimental determination of the rate constants of the reactions of HO2 + DO2 and DO2 + DO2. Int. J. Chem. Kinet. 2020, 52, 197–206. [Google Scholar] [CrossRef]
  49. Thiebaud, J.; Thevenet, F.; Fittschen, C. OH Radicals and H2O2 Molecules in the Gas Phase near to TiO2 Surfaces. J. Phys. Chem. C 2010, 114, 3082–3088. [Google Scholar] [CrossRef]
  50. Faragó, E.P.; Viskolcz, B.; Schoemaecker, C.; Fittschen, C. Absorption Spectrum and Absolute Absorption Cross Sections of CH3O2 Radicals and CH3I Molecules in the Wavelength Range 7473–7497 cm−1. J. Phys. Chem. A 2013, 117, 12802–12811. [Google Scholar] [CrossRef]
  51. Atkinson, D.B.; Spillman, J.L. Alkyl Peroxy Radical Kinetics Measured Using Near-infrared CW-Cavity Ring-down Spectroscopy. J. Phys. Chem. A 2002, 106, 8891–8902. [Google Scholar] [CrossRef]
  52. Onel, L.; Brennan, A.; Gianella, M.; Hooper, J.; Ng, N.; Hancock, G.; Whalley, L.; Seakins, P.W.; Ritchie, G.A.D.; Heard, D.E. An intercomparison of CH3O2 measurements by Fluorescence Assay by Gas Expansion and Cavity Ring–Down Spectroscopy within HIRAC (Highly Instrumented Reactor for Atmospheric Chemistry). Atmos. Meas. Tech. 2017, 10, 4877–4894. [Google Scholar] [CrossRef] [Green Version]
  53. Jacquinet-Husson, N.; Armante, R.; Scott, N.A.; Chédin, A.; Crépeau, L.; Boutammine, C.; Bouhdaoui, A.; Crevoisier, C.; Capelle, V.; Boonne, C.; et al. The 2015 edition of the GEISA spectroscopic database. J. Mol. Spectrosc. 2016, 327, 31–72. [Google Scholar] [CrossRef] [Green Version]
  54. Fink, E.H.; Ramsay, D.A. High-Resolution Study of the Ã2A’→X2A’’ Transition of HO2: Analysis of the 000–000 Band. J. Mol. Spectrosc. 1997, 185, 304–324. [Google Scholar] [CrossRef] [PubMed]
  55. Miller, T. Private communication by e-mail about absorption spectrum of CH3C(O)O2. 2021. [Google Scholar]
  56. Delbos, E.; Fittschen, C.; Hippler, H.; Krasteva, N.; Olzmann, M.; Viskolcz, B. Rate Coefficients and Equilibrium Constant for the CH2CHO + O2 Reaction System. J. Phys. Chem. A 2006, 110, 3238–3245. [Google Scholar] [CrossRef] [PubMed]
  57. Bartels, M.; Hoyermann, K.; Lange, U. An Experimental Study of the Reactions CH3CHO + Cl, C2H4O + Cl, and C2H4O + F in the Gas-Phase. Ber. Bunsenges. Phys. Chem. 1989, 93, 423–427. [Google Scholar] [CrossRef]
  58. Assaf, E.; Fittschen, C. Cross Section of OH Radical Overtone Transition near 7028 cm−1 and Measurement of the Rate Constant of the Reaction of OH with HO2 Radicals. J. Phys. Chem. A 2016, 120, 7051–7059. [Google Scholar] [CrossRef]
  59. Parker, A.; Jain, C.; Schoemaecker, C.; Fittschen, C. Kinetics of the Reaction of OH Radicals with CH3OH and CD3OD Studied by Laser Photolysis Coupled to High Repetition Rate Laser Induced Fluorescence. React. Kinet. Catal. Lett. 2009, 96, 291–297. [Google Scholar] [CrossRef]
  60. Fernandes, R.X.; Luther, K.; Troe, J. Falloff Curves for the Reaction CH3 + O2 (+ M) → CH3O2 (+ M) in the Pressure Range 2–1000 Bar and the Temperature Range 300–700 K. J. Phys. Chem. A 2006, 110, 4442–4449. [Google Scholar] [CrossRef]
  61. Atkinson, R.; Baulch, D.L.; Cox, R.A.; Crowley, J.N.; Hampson, R.F.; Hynes, R.G.; Jenkin, M.E.; Rossi, M.J.; Troe, J. Evaluated Kinetic and Photochemical Data for Atmospheric Chemistry: Volume 1—Gas Phase Reactions of Ox, HOx, NOx, and SOx, Species. Atmos. Chem. Phys. 2004, 4, 1461–1738. [Google Scholar] [CrossRef] [Green Version]
  62. Dagaut, P.; Wallington, T.J.; Liu, R.Z.; Kurylo, M.J. A kinetic investigation of the gas-phase reactions of hydroxyl radicals with cyclic ketones and diones: Mechanistic insights. J. Phys. Chem. 1988, 92, 4375–4377. [Google Scholar] [CrossRef]
  63. Assaf, E.; Tanaka, S.; Kajii, Y.; Schoemaecker, C.; Fittschen, C. Rate constants of the reaction of C2–C4 peroxy radicals with OH radicals. Chem. Phys. Lett. 2017, 684, 245–249. [Google Scholar] [CrossRef]
  64. Tyndall, G.S.; Orlando, J.J.; Kegley-Owen, C.S.; Wallington, T.J.; Hurley, M.D. Rate coefficients for the reactions of chlorine atoms with methanol and acetaldehyde. Int. J. Chem. Kinet. 1999, 31, 776–784. [Google Scholar] [CrossRef]
Figure 1. Kinetic decays at two different wavelengths, obtained following the 248 nm photolysis of [CH3C(O)CH3] = 8.5 × 1015 cm−3. Each data point results from one ring-down event, no averaging has been performed.
Figure 1. Kinetic decays at two different wavelengths, obtained following the 248 nm photolysis of [CH3C(O)CH3] = 8.5 × 1015 cm−3. Each data point results from one ring-down event, no averaging has been performed.
Atmosphere 13 00186 g001
Figure 2. Decays obtained following the 351 nm photolysis of [Cl2] = 4.5 × 1015 cm−3 in presence of [CH3CHO] = 8.4 × 1014 cm−3 at a total pressure of 50 Torr helium ([O2] = 3 × 1017 cm−3). Black dots: peak absorption of HO2 radicals (6638.2 cm−1), open black circles: offline HO2 (6637.15 cm−1), open squares: the difference between both (left y-axis applies). For comparison, the corresponding CH3C(O)O2 (blue dots, 6497.94 cm−1) has been scaled on the right y-axis to match the offline signal.
Figure 2. Decays obtained following the 351 nm photolysis of [Cl2] = 4.5 × 1015 cm−3 in presence of [CH3CHO] = 8.4 × 1014 cm−3 at a total pressure of 50 Torr helium ([O2] = 3 × 1017 cm−3). Black dots: peak absorption of HO2 radicals (6638.2 cm−1), open black circles: offline HO2 (6637.15 cm−1), open squares: the difference between both (left y-axis applies). For comparison, the corresponding CH3C(O)O2 (blue dots, 6497.94 cm−1) has been scaled on the right y-axis to match the offline signal.
Atmosphere 13 00186 g002
Figure 3. Absorption spectrum of CH3O2, adapted from Farago et al. [50] (b) and kinetic decays taken following the 351 nm photolysis of [Cl2] = 4.5 × 1015 cm−3 in presence of [CH3CHO] = 1.66 × 1015 at a total pressure of 50 Torr helium ([O2] = 3 × 1017 cm−3). (ce) show the decays taken at the three peaks of the spectrum, (a) shows all decays taken at background wavelengths, indicated by vertical dashed lines in the spectrum. The decay of CH3C(O)O2 is given for information as blue circles in graph a. (right y-axis applies).
Figure 3. Absorption spectrum of CH3O2, adapted from Farago et al. [50] (b) and kinetic decays taken following the 351 nm photolysis of [Cl2] = 4.5 × 1015 cm−3 in presence of [CH3CHO] = 1.66 × 1015 at a total pressure of 50 Torr helium ([O2] = 3 × 1017 cm−3). (ce) show the decays taken at the three peaks of the spectrum, (a) shows all decays taken at background wavelengths, indicated by vertical dashed lines in the spectrum. The decay of CH3C(O)O2 is given for information as blue circles in graph a. (right y-axis applies).
Atmosphere 13 00186 g003
Figure 4. (a) Kinetic decays following the 248 nm photolysis of [CH3C(O)CH3] = 9.8 × 1015 cm−3 at 200 Torr. (b) Kinetic decays obtained following the 351 nm photolysis of [Cl2] = 1.6 × 1016 cm−3, [CH3CHO] = 5.9 × 1015 cm−3. Black circles show online CH3O2 measurement (left y-axis), red circles are offline CH3O2 measurements (right y-axis). Blue circles show simultaneous CH3C(O)O2 measurements with open symbols after multiplication with 0.13 to match CH3O2 absorption (see text). Open and filled circles in (b) see text on Cl + CH3C(O)H precursor experiments.
Figure 4. (a) Kinetic decays following the 248 nm photolysis of [CH3C(O)CH3] = 9.8 × 1015 cm−3 at 200 Torr. (b) Kinetic decays obtained following the 351 nm photolysis of [Cl2] = 1.6 × 1016 cm−3, [CH3CHO] = 5.9 × 1015 cm−3. Black circles show online CH3O2 measurement (left y-axis), red circles are offline CH3O2 measurements (right y-axis). Blue circles show simultaneous CH3C(O)O2 measurements with open symbols after multiplication with 0.13 to match CH3O2 absorption (see text). Open and filled circles in (b) see text on Cl + CH3C(O)H precursor experiments.
Atmosphere 13 00186 g004
Figure 5. Absorption signals from Figure 3 for 4 different wavelengths: the signals at the three peak wavelengths are in colour, an example for the offline (magenta in Figure 3a) is shown in black. (a) Raw signals (open symbols), (b) signals obtained after subtracting 0.13 × αCH3C(O)O2 and subsequent multiplication with 1, 1.02, 1.6 and 4.1 for the red, green, orange and black circles, respectively. Blue circles are αCH3C(O)O2 (right y-axis applies).
Figure 5. Absorption signals from Figure 3 for 4 different wavelengths: the signals at the three peak wavelengths are in colour, an example for the offline (magenta in Figure 3a) is shown in black. (a) Raw signals (open symbols), (b) signals obtained after subtracting 0.13 × αCH3C(O)O2 and subsequent multiplication with 1, 1.02, 1.6 and 4.1 for the red, green, orange and black circles, respectively. Blue circles are αCH3C(O)O2 (right y-axis applies).
Atmosphere 13 00186 g005
Figure 6. Concentration-time profiles of CH3C(O)O2 (a,b), CH3O2 (c,d) et HO2 (e,f) measured simultaneously following the 248 nm photolysis of 3 different concentrations of CH3C(O)CH3 [CH3C(O)CH3] = 1.21 (red), 0.86 (blue) and 0.4×1016 cm−3 (green) (left raw) and CH3C(O)C(O)CH3 [CH3C(O)C(O)CH3] = 6 (red), 2.56 (blue) and 0.93×1016 cm−3 (green) (right raw) in 100 Torr O2. Full lines: simulation following the model and rate constants as given in Table 3. For the [CH3O2] profiles, the dashed lines show [CH3O2] + 0.179 × [CH3C(O)O2]. Experimental HO2 profiles have been decreased by around 10% for the lowest radical concentration, i.e., the model systematically underestimates HO2 at low overall radical concentrations.
Figure 6. Concentration-time profiles of CH3C(O)O2 (a,b), CH3O2 (c,d) et HO2 (e,f) measured simultaneously following the 248 nm photolysis of 3 different concentrations of CH3C(O)CH3 [CH3C(O)CH3] = 1.21 (red), 0.86 (blue) and 0.4×1016 cm−3 (green) (left raw) and CH3C(O)C(O)CH3 [CH3C(O)C(O)CH3] = 6 (red), 2.56 (blue) and 0.93×1016 cm−3 (green) (right raw) in 100 Torr O2. Full lines: simulation following the model and rate constants as given in Table 3. For the [CH3O2] profiles, the dashed lines show [CH3O2] + 0.179 × [CH3C(O)O2]. Experimental HO2 profiles have been decreased by around 10% for the lowest radical concentration, i.e., the model systematically underestimates HO2 at low overall radical concentrations.
Atmosphere 13 00186 g006
Figure 7. Concentration-time profiles of CH3O2 (a), CH3C(O)O2 (b) and HO2 (c) following the 248 nm photolysis of 3 different concentration of CH3C(O)C(O)CH3 (8.67 (red), 5.79 (blue) and 2.85 × 1016 cm−3 (green)) at a total pressure of 200 Torr O2. Full lines simulation with rate constants from Table 3, dashed black lines using a rate constant for HO2 self-reaction of 5 × 10−12 cm3 s−1. Changes in CH3O2 and CH3C(O)O2 profiles are not visible and have been omitted from the graph.
Figure 7. Concentration-time profiles of CH3O2 (a), CH3C(O)O2 (b) and HO2 (c) following the 248 nm photolysis of 3 different concentration of CH3C(O)C(O)CH3 (8.67 (red), 5.79 (blue) and 2.85 × 1016 cm−3 (green)) at a total pressure of 200 Torr O2. Full lines simulation with rate constants from Table 3, dashed black lines using a rate constant for HO2 self-reaction of 5 × 10−12 cm3 s−1. Changes in CH3O2 and CH3C(O)O2 profiles are not visible and have been omitted from the graph.
Atmosphere 13 00186 g007
Figure 8. Highest radical concentration from 248 nm photolysis of CH3C(O)CH3 shown in Figure 6 (red symbols from the left column): CH3O2 profile in blue, HO2 profile in green and CH3C(O)O2 profile in red. (a) model as given in Table 3, (b) same model, but rate constants for (R1) and (R2) such as propose by Maricq and Szente [17], (c) same model, but k1 and k2 such as recommended currently by IUPAC [30], (d) same, but k1 and k2 from Villenave and Lesclaux [28] (see Table 1).
Figure 8. Highest radical concentration from 248 nm photolysis of CH3C(O)CH3 shown in Figure 6 (red symbols from the left column): CH3O2 profile in blue, HO2 profile in green and CH3C(O)O2 profile in red. (a) model as given in Table 3, (b) same model, but rate constants for (R1) and (R2) such as propose by Maricq and Szente [17], (c) same model, but k1 and k2 such as recommended currently by IUPAC [30], (d) same, but k1 and k2 from Villenave and Lesclaux [28] (see Table 1).
Atmosphere 13 00186 g008
Figure 9. Concentration-time profiles for CH3O2 (a), CH3C(O)O2 (b) and HO2 (c), obtained following the photolysis of [Cl2] = = 1.6 (blue), 1.17 (green), 0.77 (red) and 0.34 × 1016 cm−3 (black) in presence of [CH3CHO] = 5.9 × 1015 cm−3 at 100 Torr O2. Full lines present the model from Table 3, dashed line in CH3O2 profiles represent [CH3O2] + 0.179 × [CH3C(O)O2].
Figure 9. Concentration-time profiles for CH3O2 (a), CH3C(O)O2 (b) and HO2 (c), obtained following the photolysis of [Cl2] = = 1.6 (blue), 1.17 (green), 0.77 (red) and 0.34 × 1016 cm−3 (black) in presence of [CH3CHO] = 5.9 × 1015 cm−3 at 100 Torr O2. Full lines present the model from Table 3, dashed line in CH3O2 profiles represent [CH3O2] + 0.179 × [CH3C(O)O2].
Atmosphere 13 00186 g009
Figure 10. Test for unidentified secondary chemistry involving CH3CHO or reaction products remaining within the photolysis volume: (a) CH3O2, (b) CH3C(O)O2, (c) HO2 profiles at different CH3CHO concentrations (Cl2 = 7.7 × 1015 cm−3, CH3CHO = 3.1 (blue), 6.2 (green) and 9.2× 1015cm−3 (red)). (d) HO2 profiles at different photolysis repetition rates.
Figure 10. Test for unidentified secondary chemistry involving CH3CHO or reaction products remaining within the photolysis volume: (a) CH3O2, (b) CH3C(O)O2, (c) HO2 profiles at different CH3CHO concentrations (Cl2 = 7.7 × 1015 cm−3, CH3CHO = 3.1 (blue), 6.2 (green) and 9.2× 1015cm−3 (red)). (d) HO2 profiles at different photolysis repetition rates.
Atmosphere 13 00186 g010
Figure 11. Highest radical concentration from Figure 9: [Cl2] = 1.6 × 1016 cm−3 (CH3O2 in blue, CH3C(O)O2 in red and HO2 in green) with different models, such as given in Table 1. Dashed blue lines represent [CH3O2] + 0.179 × [CH3C(O)O2], which should agree with measurements.
Figure 11. Highest radical concentration from Figure 9: [Cl2] = 1.6 × 1016 cm−3 (CH3O2 in blue, CH3C(O)O2 in red and HO2 in green) with different models, such as given in Table 1. Dashed blue lines represent [CH3O2] + 0.179 × [CH3C(O)O2], which should agree with measurements.
Atmosphere 13 00186 g011
Table 1. Summary of literature results for (R1) and (R2), all rate constants in cm3s−1.
Table 1. Summary of literature results for (R1) and (R2), all rate constants in cm3s−1.
ReferencesIUPAC [30]Roehl et al. [16]Maricq, Szente [17]Villenave, Lesclaux [28]This work
Reaction
CH3C(O)O2 + CH3O2 1.1 × 10−119.8 × 10−121.0 × 10−118.6 × 10−122.0 × 10−11
(R2a): CH3O + CH3C(O)O + O29.9 × 10−128.8 × 10−1205.3 × 10−121.3 × 10−11
(R2b): CH3C(O)OH + HCHO + O21.1 × 10−121.0 × 10−121 × 10−112.9 × 10−126.5 × 10−12
α (R2a)/(R2)0.90.900.650.67
ReferencesIUPAC [30]Roehl et al. [16]Maricq, Szente [17]Moortgat et al. [14]This work
Reaction
2 CH3C(O)O2 → 2 CH3C(O)O + O21.6 × 10−111.36 × 10−111.5 × 10−111.6 × 10−111.3 × 10−11
Table 2. Ratio of CH3C(O)O2 and CH3O2 radicals obtained from different precursors and at different pressures. Last column shows fraction of CH3CO radicals that lead in collision with O2 to HO2 radicals (R9).
Table 2. Ratio of CH3C(O)O2 and CH3O2 radicals obtained from different precursors and at different pressures. Last column shows fraction of CH3CO radicals that lead in collision with O2 to HO2 radicals (R9).
Reaction% CH3C(O)O2% CH3O2k9b/k9
CH3CHO + Cl10000.007 *
CH3C(O)C(O)CH3 + hν351 nm 100 Torr89110.014
CH3C(O)C(O)CH3 + hν248 nm 100 Torr47530.079
CH3C(O)C(O)CH3 + hν248 nm 200 Torr50500.079
CH3C(O)CH3 + hν248 nm 100 Torr38620.064
CH3C(O)CH3 + hν248 nm 200 Torr40600.064
* in 100 Torr O2. Ratio is around 0.02 in 50 Torr helium.
Table 3. Mechanism used for fitting the different profiles under all conditions.
Table 3. Mechanism used for fitting the different profiles under all conditions.
NoReactionk/10−11 cm3s−1References
12 CH3C(O)O2→ → → 2 CH3O21.3 ± 0.3 *This work
2aCH3C(O)O2 + CH3O2 → CH3O + CH3C(O)O + O21.35 ± 0.2 *This work
2b→ molecular products0.65 ± 0.2 *This work
3a/bCH3C(O)O2 + HO2 → molecular products0.86[27]
3c→ CH3C(O)O + OH + O20.86
5CH3 + O2 (+M) → CH3O2 (+M)0.035[60]
6CH3O + O2 → CH2O + HO21.9 × 10−4[30]
9aCH3CO + O2 (+ M) → CH3C(O)O2 (+ M)0.7[30]
9bCH3CO + O2CH2CO + HO2/CH2C(O)O + OHVariedsee Table 2
10CH3COCH3 + COVariedsee Table 2
112 HO2 → H2O2 + O20.17[61]
12a2 CH3O2 → 2 CH3O + O20.013[30]
12b→ CH3OH + CH2O + O20.022
13CH3O2+ HO2 → CH3OOH0.52[30]
14OH + CH3CHO → CH3CO + H2O1.6[30]
15OH + CH3C(O)CH3 → CH2C(O)CH3 + H2O0.022[30]
16OH + CH3C(O)C(O)CH3 → CH2C(O)C(O)CH3 + H2O0.025[62]
17OH + CH3O2 → CH3O + HO212[3]
18OH + CH3C(O)O2 → CH3C(O)O3H10[12,63]
19Cl + CH3CHO → CH3CO + HCl7.2[30]
20Cl2 + CH3CO → CH3COCl + Cl4.3[64]
21HO2, CH3O2, CH3C(O)O2 → diffusion1–2 s−1
* Uncertainties are only based on unacceptable deviations of the model from measurements using the absorption cross sections such as given in the text.
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Assali, M.; Fittschen, C. Rate Constants and Branching Ratios for the Self-Reaction of Acetyl Peroxy (CH3C(O)O2) and Its Reaction with CH3O2. Atmosphere 2022, 13, 186. https://doi.org/10.3390/atmos13020186

AMA Style

Assali M, Fittschen C. Rate Constants and Branching Ratios for the Self-Reaction of Acetyl Peroxy (CH3C(O)O2) and Its Reaction with CH3O2. Atmosphere. 2022; 13(2):186. https://doi.org/10.3390/atmos13020186

Chicago/Turabian Style

Assali, Mohamed, and Christa Fittschen. 2022. "Rate Constants and Branching Ratios for the Self-Reaction of Acetyl Peroxy (CH3C(O)O2) and Its Reaction with CH3O2" Atmosphere 13, no. 2: 186. https://doi.org/10.3390/atmos13020186

APA Style

Assali, M., & Fittschen, C. (2022). Rate Constants and Branching Ratios for the Self-Reaction of Acetyl Peroxy (CH3C(O)O2) and Its Reaction with CH3O2. Atmosphere, 13(2), 186. https://doi.org/10.3390/atmos13020186

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop