Fabian E.
Cano Ardila
a,
Sharath
Nagaraju
a,
Robert S.
Tranter
b,
Gustavo A.
Garcia
c,
Anthony
Desclaux
a,
Anthony
Roque Ccacya
a,
Nabiha
Chaumeix
a and
Andrea
Comandini
*a
aCNRS-INSIS, I.C.A.R.E., 1C Avenue de la recherche scientifique, 45071 Orléans cedex 2, France. E-mail: andrea.comandini@cnrs-orleans.fr
bChemical Sciences and Engineering Department, Argonne National Laboratory, 9700 S. Cass Avenue, Lemont, Illinois 60439, USA
cSynchrotron SOLEIL, L'Orme des Merisiers, St. Aubin BP 48, 91192 Gif sur Yvette, France
First published on 30th January 2024
The signal levels observed from mass spectrometers coupled by molecular beam sampling to shock tubes are impacted by dynamic pressures in the spectrometer due to rapid pressure changes in the shock tube. Accounting for the impact of the pressure changes is essential if absolute concentrations of species are to be measured. Obtaining such a correction for spectrometers operated with vacuum ultra violet photoionization has been challenging. We present here a new external calibration method which uses VUV-photoionization of CO2 to develop time-dependent corrections to species concentration/time profiles from which kinetic data can be extracted. The experiments were performed with the ICARE–HRRST (high repetition rate shock tube) at the DESIRS beamline of synchrotron SOLEIL. The calibration experiments were performed at temperatures and pressures behind reflected shock waves of 1376 ± 12 K and 6.6 ± 0.1 bar, respectively. Pyrolytic experiments with two aromatic species, toluene (T5 = 1362 ± 22 K, P5 = 6.6 ± 0.2 bar) and ethylbenzene (T5 = 1327 ± 18 K, P5 = 6.7 ± 0.2 bar), are analyzed to test the method. Time dependent concentrations for molecular and radical species were corrected with the new method. The resulting signals were compared with chemical kinetic simulations using a recent mechanism for pyrolytic formation of polycyclic aromatic hydrocarbons. Excellent agreement was obtained between the experimental data and simulations, without adjustment of the model, demonstrating the validity of the external calibration method.
Shock tubes (ST) coupled by differential pumped molecular beam sampling (MBS) to time-of flight mass spectrometers (TOF-MS) have been used to study complex reaction systems and simultaneously measure stable and radical species concentrations with high time resolution.4–6 Generally, in ST/TOF-MS cations are created by electron impact ionization (EI). While EI is efficient, typical energies are quite high, and most species fragment following ionization. Fragmentation can severely complicate analysis of the mass spectra particularly, for complex mixtures such as those in this study. In principle, fragmentation can be minimized by reducing the ionization energy (IE). However, this also severely reduces the sensitivity of the experiment and with most ST/TOF-MS apparatuses signal averaging methods cannot be used to compensate for the reduced sensitivity. The standard ST/TOF-MS method has been successfully applied to quite complex systems, but the lack of ability to discriminate between isomers and fragmentation limit the applicability to larger molecular weight components such as polycyclic aromatic hydrocarbons (PAH).
Many of the challenges posed by EI can be addressed with vacuum ultraviolet (VUV) photoionization (PI) which largely reduces fragmentation compared to EI. Furthermore, with highly tunable synchrotron sourced VUV, isomers and species of the same mass but different chemical composition can be distinguished.7–10 However, signal levels from PI-TOF-MS tend to be low and signal averaging is essential to obtain sufficient signal/noise (S/N). To take advantage of synchrotron-based VUV-PI methods miniature high repetition rate shock tubes (HRRST) were developed.11 Two of these are routinely used at synchrotron facilities. The original one developed at Argonne National Laboratory (ANL) is primarily used at the Advanced Light Source (ALS) with TOF-MS (ANL–HRRST/TOF-MS).12–15 A later HRRST was built at the Institut de Combustion Aérothermique Réactivité Environnement (ICARE)16 and is primarily used with double imaging photolelectron/photoion spectroscopy (i2PEPICO) at the DESIRS beamline of synchrotron SOLEIL.17–20 The ANL–HRRST and ICARE–HRRST are coupled by MBS systems to the charged particle analyzers. To a first order the apparatuses are identical and differ in the information content of the datasets produced. While both apparatuses have produced considerable insight into complex reaction mechanisms it has so far not been possible to extract kinetic data from them due to challenges with obtaining absolute concentrations of species. The main difficulty is a consequence of the fast changes in pressure that occur within a shock tube experiment that induce a slower increase in pressure in the ionization region of the spectrometer. This rise in pressure results in more ions being generated, even for an inert species, and the observed signal correspondingly increases. Thus, the signal for a reagent or product is a combination of the mole fraction of the species and the local pressure in the ionization region. These effects have to be decoupled to extract meaningful rate coefficients. The effect is well-understood4,5 and in EI systems is dealt with by adding a small amount of an inert gas (usually Ar, Kr or Xe) to the reagent mixture. The inert gas acts as an internal standard and allows the pressure effects to be accounted for.4,5 Implementing an internal calibration method for a shock tube experiment with PI sources is difficult, primarily due to the lack of inert species that have ionization energies in the range of most organic molecules. In the remainder of this paper, we present an alternative method for calibrating the pressure response which we refer to as an external calibration. Conceptually the method is similar to the external chemical thermometry method often employed with single pulse shock tubes.21,22 Following a discussion of the method, it is applied to two recent studies on toluene pyrolysis and ethylbenzene pyrolysis with the ICARE–HRRST/i2PEPICO experiment. The method is demonstrated for photoionization, but it should be equally applicable to other methods such as low energy electron impact and chemical ionization.
The driven section of the ICARE–HRRST is largely encased in the SAPHIRS chamber (primary vacuum chamber) at the DESIRS beamline.16 Gases continuously elute through the endwall nozzle into SAPHIRS forming a supersonic jet that quenches reaction. A portion from the jet centre passes through a skimmer (1 mm orifice) creating a molecular beam in an intermediate chamber. A portion from the core of the molecular beam passes through a second skimmer (2 mm orifice) into the ion source of the DELICIOUS III i2PEPICO spectrometer.19 The combination of nozzle and skimmers defines two stages of differential pumping between shock tube and ion source. The transient pressure changes in the spectrometer are around one order of magnitude (from ∼10−7 to ∼10−6 mbar) in each experimental cycle. The base pressure in the spectrometer was ∼5 × 10−8 mbar with the shock tube under vacuum.
The i2PEPICO method yields a multi-dimensional dataset from which mass spectra and the photoelectron spectrum associated with each peak in the mass spectra are extracted. Additionally, time-dependent data are obtained by providing a trigger signal that synchronizes firing of the HRRST and data acquisition with DELICIOUS III. For every experiment data were acquired from DELICIOUS III for 7.8 ms and the dataset comprised both pre-shock (non-reactive) and post-shock data. For every experimental cycle, i.e., each shock, sufficient data are recorded to allow post-processing of the dataset on a shock-by-shock basis. For example, different binning strategies can be tested, or shocks excluded to reduce standard deviations in reaction conditions. The experiments presented in this work were obtained at a repetition rate of the HRRST of 1 Hz. The photon energy was fixed at 10.0 eV for toluene (IE 8.82 eV)24 and ethylbenzene (IE 8.77 eV),24 and 14.5 eV for carbon dioxide (IE 13.78 eV).25 An argon gas filter removed high harmonic photons prior to the monochromator which was fitted with a 200 gr mm−1 low dispersion grating and delivered photon resolutions of around 25 meV at 10 eV. Details of DESIRS and DELICIOUS III in ref. 17–20.
In general, the mass spectrometer signal for species x, Sx, can be written as follows:
Sx = σx·[x]·nexp·Dx·ηset·f(P,t) | (1) |
SCO2 = σCO2·[CO2]·nCO2\_set·DCO2·ηCO2\_set·f(P,t) | (2) |
![]() | (3) |
Substituting eqn (3) into eqn (1), the concentration of any species x can be derived from
![]() | (4) |
The concentration of the external standard and the number of experiments are known, the ratio between signals can be obtained from the experimental measurements, while the mass discrimination factors can be estimated based on previous investigations.27 Thus, if the photoionization cross sections are measured or calculated, the only unknown in the equation is the ratio between the transmission factors. This ratio is the same for all the species measured in a specific dataset, including the fuel molecule. Thus, its value can be derived from the following equation
![]() | (5) |
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Fig. 1 Toluene pyrolysis, 0.1% in argon at T = 1362 ± 22 K and P = 6.6 ± 0.2 bar, photon energy 10.0 eV. Average mass spectrum from 107![]() |
As discussed above, the mass spectrometer signal is proportional to the gas density (or pressure) inside the mass spectrometer chamber, which varies during the miniature shock tube cycle due to the large rapid changes in thermodynamic conditions in the HRRST due to the primary shock wave. However, there is also a slower and smaller pressure variation in the post-shock conditions due to wave dynamics in the HRRST. This slow variation also has to be accounted for particularly in chemical kinetic simulations of species concentrations. An example pressure trace averaged over 1000 experiments is shown in Fig. 2. In this case, the single pressure profiles were shifted in the x-direction to align the arrival times at the sensor. The pressure profile in Fig. 2 represents the thermodynamic conditions inside the shock tube, to be used in kinetic simulations. The stochastic distribution of the incident shock wave arrival times at the endwall is within ±50 μs around the average. These times are estimated with respect to the initial signals which trigger the shock tube cycle starting with the opening of the high-pressure valve. The average pressure profile over 1000 experiments from the raw data without shifting is presented in Fig. S1.† The averaging process also affects the shape of the experimental curves. Fig. 2 also contains signal intensity/time (kinetic traces) plots for m/z = 92 (fuel molecule) and m/z = 78 (one of the main peak products, mainly benzene) from the dataset presented in Fig. 1 (0.1% toluene/Ar). The kinetic data shown in Fig. 2 have not been corrected for pressure changes in the spectrometer, and the fuel profile has been translated so that the time corresponding to around 50% of its maximum value matches the zero of the pressure profile. Following the initial rise in the m/z 92 signal it stays nearly constant for around 400 μs, before dropping almost to its baseline within 200 μs. For the example shown, the rise time for the fuel signal to go from the pre-shock value to its maximum is about 150 μs. This rise time is related to the time taken for the pressure increase in the spectrometer to reach a maximum and is similar to that seen in single shot ST/MS experiments.5 The width of initial rise in the averaged pressure profile from the raw data (Fig. S1†) is around 80 μs, the pressure build-up in the mass spectrometer chamber contributes for the remaining effect. The region of stable m/z 92 signal indicates that dissociation of toluene is slow in these experiments. As the fuel signal falls, first primary and then secondary products start to appear, for example m/z = 78 in Fig. 2. After the initial sharp rise at time = 0 the pressure profile rises slowly for 600 μs before decreasing. This behavior is due to wave dynamics within the HRRST and has to be accounted for when simulating the kinetic traces. Similar behavior is seen in more conventional shock tubes and the impact of reaction temperatures has been previously analyzed.28,29 In particular, the decrease in m/z 78 (benzene) cannot be due to sudden consumption after 600 μs. Rather the observed signal is a convolution of the actual concentration and variations in signal due to non-idealities in the HRRST and pressure build up in the spectrometer. As will be seen in the following sections the inert calibration species signal exhibits similar behavior. Thus, the external calibration provides not only a correction for the build-up of the pressure inside the mass spectrometer chamber but also for the non-ideal behaviors inside the HRRST, allowing extraction of kinetic information in units of mole fractions. For this to be accurate, it is important that the conditions for the external calibration experiments and the actual ones to be corrected are similar, not only in terms of T5 and P5, but also in terms of pressure time history.
![]() | ||
Fig. 2 Toluene pyrolysis, 0.1% in argon. Pressure profile from 1000 experiments; temporal species profiles from 107![]() |
A CO2 mole fraction of 0.1% in argon, at an average temperature of 1376 ± 12 K and pressure of 6.6 ± 0.1 bar, and photon energy equal to 14.5 eV was used for the external calibration experiments. A total of 6042 experiments were averaged to derive the CO2 time profile, presented in Fig. 3 together with the m/z = 92 from Fig. 2. Carbon dioxide does not react at the thermodynamic conditions of the experiments, thus its mole fraction behind the reflected shock wave is constant. On the other hand, its signal varies due to the pressure variations inside the shock tube and the shape is similar to the pressure profile in Fig. 2. The initial rise in the CO2 profile is slightly faster than the case of toluene. This is probably an artifact of the large difference in the number of experiments (∼6000 vs. 107000) and the signal levels. Note that the CO2 values have been multiplied by a factor of 3 in Fig. 3.
In the following sections, the results of applying the external standard calibration technique to toluene pyrolysis and ethylbenzene pyrolysis will be presented. One of the uncertainties in the development of the external calibration technique is related to the alignment between the fuel and the CO2 profiles, e.g., Fig. 3. In Fig. 4 three methods of correcting for the small temporal misalignment between the CO2 and toluene (m/z = 92) signals are compared. The m/z = 92 signal is anchored at t = 0 as in Fig. 2 and the CO2 signal is shifted on the X-axis as follows: (i) the times of the 50% signal rises are matched (Fig. 4 red dashed lines), (ii) the times of the two main peaks at the end of the sharp increase in signal are matched (Fig. 4 solid lines, CO2 profile shifted by +36 μs), (iii) the times at which the two profiles start rising are matched (Fig. 4 light-blue dashed lines, CO2 profile shifted by −24 μs). These times refer to the profiles in Fig. 3. During the first few tens of microseconds both the CO2 and m/z = 92 signals are small and what look like minor fluctuations can introduce quite large perturbations in the corrected signal. Overall, fewer fluctuations are seen with method ii although the three methods produce essentially the same shapes in the profiles indicating that the choice of alignment method is not significant. The corrected m/z = 78 product signal is little affected by the choice of correction method. This is primarily due to the CO2 signal being relatively large and stable when the m/z = 78 signal starts to rise. For all three methods, the noise in the treated signal before time zero, pre-shock, is quite large, thus the derived information is not useful. Our experience has shown that large fluctuations are also observed in the pre-shock signal when an internal calibrant is used with electron ionization.
Fig. 5a–c present the temporal species profiles for the fuel and some of the main products after correction. The species shown were chosen because they could be unambiguously identified by comparing the experimental photoelectron spectra with literature ones (excluding minor contributions from isomers) and the photoionization cross sections have been measured or estimated. The mass spectral peaks at m/z 78, 92, 102 and 104 are almost entirely due to benzene, toluene, phenylacetylene and styrene, respectively, for m/z 116 indene accounts for 90% of the signal, while at m/z 128 naphthalene is about 70% of the peak. The error associated due to the difference in photoionization cross sections for the remaining isomers not considered in the current analysis is not expected to be significant. The absolute photoionization cross sections at 10.0 eV for toluene, phenylacetylene, styrene, indene, and ethylbenzene were taken from Zhou et al.,30 benzene from Rennie et al.,31 while for naphthalene the estimated values from ref. 32 were used. An uncertainty of 20% in the photoionization cross sections of the single-ring species is estimated, which increases to 30% for indene and 50% for naphthalene. These uncertainties were used to calculate the error bars for the mole fractions, Fig. 5. The time uncertainties are represented by error bars based on the maximum shift in the fuel profile from Fig. 4. The photoionization cross section for carbon dioxide at 14.5 eV was obtained from Hitchcock et al.33 by interpolation of the values at 14.0 eV and at 15.0 eV. In Fig. 5a–c, the dashed lines represent simulations obtained with the ICARE chemical kinetic mechanism35 for PAH formation and growth. This mechanism was previously validated against species profiles vs. temperature conditions from single-pulse shock tube experiments for pyrolysis of many single fuels at a nominal pressure of 20 bar. Some of the datasets used to develop the model were toluene34,35 (100–200 ppm, T5 1050–1700 K), and ethylbenzene36 (100 ppm, T5 950–1700 K) and their mixtures with small aliphatics (including reactions toluene + C2Hx37 and toluene + C3Hx
35 at similar conditions). The simulations were performed with ANSYS CHEMKIN-Pro 2021 software using the batch reactor model with variable pressure. For these simulations the pressure profile in Fig. 2 was used. The error in the simulation results was obtained by considering the minimum and maximum temperatures in the T5 distribution (1362 ± 22 K). Overall there is excellent agreement between experiments and simulations for the decomposition of the fuel and the formation of the main single-ring aromatic products, including benzene (m/z = 78), styrene (m/z = 104), and phenylacetylene (m/z = 102), especially considering that the mechanism was not modified to match the experimental data. A peak at m/z = 91, corresponding to the benzyl radical, was also detected. The photoionization cross section was estimated by Li as 24.03 Mb at 9.98 eV.32 The shape of the m/z = 91 profile is correctly captured by the model. Species profiles for larger PAH products including indene (m/z = 116) and naphthalene (m/z = 128) are shown in Fig. 5c. Although the rise in the simulation profiles in Fig. 5c are delayed compared to the experiments and the absolute concentrations are not perfectly reproduced (especially in relative terms), the results are quite satisfactory considering the complexity of the chemistry involved in the PAH formation and the experimental errors related mainly to the availability and accuracy of ionization cross-sections. In particular, the simulations for the maximum naphthalene concentrations are within the experimental errors. Nevertheless, the data provide targets for future model development. The m/z 116 and m/z 128 profile would also need to be reduced by around 10% and 30% for comparison with indene and naphthalene, respectively, as additional isomers are not considered here. Thus, especially for naphthalene, the experimental profile would get closer to the simulation and substantially overpredict indene formation.
Fig. 5d contains mole fraction profiles of various main products (m/z = 78, 91, 102, and 202). In the analysis, the photoionization cross section of pyrene, estimated by Li,32 was used for m/z 202. From prior single-pulse shock tube measurements34 pyrene is one of the main isomers at m/z 202 and the small differences in photoionization cross sections of the different isomers will introduce little error. For clarity simulation results are not plotted. However, the figure shows that the corrected profiles have the shapes and relative heights that would be expected for species that are formed sequentially.
As briefly mentioned in the previous paragraphs, the external calibration method provides corrections not only for the initial pressure rise in the mass spectrometer, but also for the non-ideal behavior inside the shock tube at later times. To demonstrate the capability to compensate for long time effects, calculations were made using a constant value for the correction term, i.e. f(P,t) = f(t = 0) rather than the time dependent expression obtained from the CO2 profiles. The results are presented in Fig. 6 together with the kinetic simulations from Fig. 5 for toluene and benzene. Clearly, setting f(P,t) = f(t = 0) has a significant impact on the experimental profiles demonstrating the need to incorporate the full f(P,t) model. The use of the profiles in Fig. 6 for model validation would lead to incorrect mechanisms and kinetics.
The experimental results presented in Fig. 4 and 5 were obtained by averaging around 107000 signals from experiments at a 1 Hz repetition rate which took at least 36 hours to perform (∼30 hours of experiments and time to change gas bottles, refill bubblers with reagents etc.). This large number of experiments was performed to enhance the S/N of high mass (m/z > 326) and low concentration products. Ideally, the smallest number of experiments necessary would be performed to obtain S/N of the desired level. The number of experiments needed is largely dependent on the concentration and photoionization cross section of a target species. Thus, the number of experiments needed will vary greatly depending on the overall goal of a study. To test the effects of reducing the number of runs on the signal quality, a sub-set of 27
000 experiments was selected and used to derive temporal species profiles with the same data treatment procedure presented above. The number of experiments selected is the same as obtained in a subsequent study on ethylbenzene, discussed below. In this analysis, the first 27
000 experiments were kept. Tests were also performed randomly selecting different batches of 27
000 experiments and similar results were obtained. Selected results are presented in Fig. 7 for various m/z (dashed lines) together with the results from averaging 107
000 runs (solid lines). The overall profiles are very similar in the two cases, in terms of shape and mole fractions, although the noise is considerably reduced when all the runs are considered in the analysis. This is expected as the signal to noise ratio is proportional to the square root of the number of experiments. However, apart from the increase in noise the information gained from the full dataset, Fig. 5, and the reduced set, Fig. 7, are very similar. This suggests that, depending on the overall goals, a small experimental set can produce reliable results, albeit with more noise, and allow for efficient use of limited beamtime. For example, in Fig. S2b and e,†m/z 276 and 326 are reported from the average of 27
000 experiments, compared to the average from 107
000 experiments in Fig. S2a and d of the ESI.† The profile for m/z 276 is still well defined, despite the fact the related S/N is now 2 (compared to 4 in Fig. S2a†). The two profiles obtained with 107
000 and 27
000 experiments are compared in Fig. S2c.† The initial rise in the profiles as well as the concentrations at later times (around 1–1.2 ms) are not affected by the number of experiments averaged. There is a slight discrepancy around 800 μs which is mainly due to the noise levels. On the other hand, the S/N ratio is too low for m/z 326, and no kinetic profiles could be determined with reduced number of experiments. In order to further confirm that the S/N ratio of around 2 is sufficient to obtain the kinetic profiles, the number of experiments in Fig. 7 was further reduced to 7 000. The resulting signal has a S/N ∼2 and it still reproduces the signal from averaging 107
000 shocks, see Fig. 8.
![]() | ||
Fig. 8 Raw signals for m/z 102, toluene pyrolysis, at T = 1362 ± 22 K and P = 6.6 ± 0.2 bar, photon energy 10.0 eV. 107![]() |
The decomposition of toluene is relatively slow at 1360 K and 6 bar whereas ethylbenzene is far more reactive. The initial fuel concentration of ethylbenzene was the same as toluene (0.1% in argon) and the average temperature and pressure of the experiments was 1327 ± 18 K and 6.7 ± 0.2 bar, respectively. The small difference in temperature compared to the calibration experiments will have little impact on the mass flow through the nozzle. Consequently, the same CO2 calibration experiments were used with ethylbenzene. Approximately, 27000 experiments on ethylbenzene pyrolysis with an ionization photon energy of 10.0 eV were averaged. The corrected concentration/time profiles of ethylbenzene and toluene are compared in Fig. 9a. In the case of ethylbenzene, the profile starts decreasing right after the arrival of the shock wave at the end-wall. In addition, nearly all the ethylbenzene is consumed after 500 μs, while around 12% of toluene remains unreacted. The kinetic simulations with the ICARE pyrolysis model accurately capture the ethylbenzene consumption (Fig. 9b). Selected aromatic intermediates including benzene (m/z = 78), toluene (m/z = 92), styrene (m/z = 104), phenylacetylene (m/z = 102) and the benzyl radical (m/z = 91) are also reported in Fig. 9b and c. Overall, the experimental data are quite well reproduced by the model both in their shape and absolute values, although a small shift in the peak time is observed for toluene. Similar agreement is also observed for larger multi-ring products, such as naphthalene (m/z = 128) and indene (m/z = 116) as in Fig. 9d, where once again the relative concentrations are not perfectly simulated as for the toluene case, but the overall profiles are captured reasonably well.
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Fig. 9 Temporal species profiles from ethylbenzene pyrolysis (0.1% in argon), average over 27![]() |
Footnote |
† Electronic supplementary information (ESI) available. See DOI: https://doi.org/10.1039/d3an00819c |
This journal is © The Royal Society of Chemistry 2024 |