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Theoretical Researches of Kinetics and Anharmonic Effect for the Reactions Related to NO in the Ozone Denitration Process


Abstract

For studying the reaction mechanism of the reactions related to NO in the ozone denitration reactions, the harmonic and anharmonic rate constants were calculated by the transition state (TS) theory and Yao and Lin (YL) method. According to above calculations, the reactions of NO with O3 and NO3 play an essential role, and the kinetic parameters considering anharmonic effect were fitted. Furthermore, the rate constants were up as temperature increasing, and the tendencies of high temperature were more gradual than the low temperature. The research will provide theoretical basis for the ozone denitration reactions.


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INTRODUCTION

With regard to the exhaust gas from marine diesel engines, not only do nitric oxides (NOx) cause serious damage to the environment, but they are also harmful to human health, for example, acid rain and photochemical smog.1,2 It is widely accepted that more than 90% of cargoes in international trade are transported by ships throughout the world.3,4 In recent years, the environmental problems caused by the indiscriminate discharge of marine diesel engine exhaust gas have attracted people’s attention.5 Currently, available technologies of the flue gas denitration market are dominated by Selective Catalytic Reduction (SCR) and Exhaust Gas Recirculation (EGR) in ships.68 However, considering the characteristics of the unbalanced economical cost and low NOx removal efficiency, the application of those two technologies is not perfect. Ozone denitration technology, which is treated as an emerging low-temperature flue gas denitration technology, is attracting more and more attention. This technology has plenty of advantages, such as convenience, no pollutant, high NOx removal efficiency (more than 95%) and simultaneous removal with other types of pollutants.6,9 Basically, the principle of ozone denitration technology can be described as follows: NOx in the flue gas are oxidized by ozone to form high-valence NOx with high solubility in water,10 then the flue gases are sprayed and washed on the spray solution in the absorption tower arranged behind the flue, finally the NOx are removed from the flue gases and transferred to the liquid to achieve the purpose of denitration treatment of the flue gas.1,11 So far, ozone denitration technology attracts the more and more attentions of researches.6,10,1216

According to previous research results, N2O5 is the easiest to absorb among all the NOx.11 And, the solubility of N2O5 in water is 500 g/dm3.17 Therefore, the high-valence NOx mainly is N2O5. In another aspect, the most NOx (more than 90%) in marine exhaust gas existing is NO.18 And, the solubility of NO in water is 0.032 g/dm3.17 Therefore, the low-valence NOx mainly is NO. In other words, the conversion of low-valence NOx to high-velnce NOx can be simply regarded as the gradual oxidation process of NO to N2O5. However, the conversion process is not one step reaction. Species such as NO2 and NO3 may be involved in the conversion process.

Besides, the 76-steps kinetic reaction mechanism of O3-NOx is listed in reference 11.11 From that 76-steps kinetic reaction mechanism of O3-NOx, it is clear that ozone denitration technology not only include the reaction of NOx with O3. In the whole reaction process, more than 20 species (O, O2, H, OH, HO2, H2O and so on) will be generated in the flue gas. Because of most NOx in marine exhaust gas existing in the form of nitric oxide (NO), this paper primarily does research on the related reactions involving NO in ozone denitrification, including the reaction of NO with oxygen atom (O), oxygen gas(O2), ozone (O3), NO, nitrogen dioxide (NO2), nitrogen trioxide (NO3) and laughing gas (N2O), respectively. In the future work, more reactions relevant to the industrial application of NO ozonation process will be worked out. Since strongly oxidizing of the ozone, the oxidization reaction is able to occur even at room temperature (300 K), and the oxidation efficiency of the denitration reactions is up with the increasing temperature theoretically. Actually, since the reaction rate of ozone decomposition increases with increasing temperature, the oxidization effective of those reaction decreases when the temperature is above 473 K because of the concentration of O3 lowering, and the gaseous mixture barely have oxidizing ability for NOx above 673 K,12 which means the ozone denitration reaction is suitable for the temperature range from 300 K to 673 K. Additionally, the reactions related to NO are also critical in high-temperature combustion reactions. Therefore, this article chooses 300 K to 4000 K as the theoretical studying temperature range. On the one hand, the detailed mechanism of ozone oxidation denitration is quite complicated,6,911 which can’t be observed and analyzed directly in experimental conditions. On the other hand, the high temperature range chosen for studying is not accessible by conventional diagnostic method. Therefore, this paper carries out theoretical calculation and comprehends the processes of those above reactions recurring to TS theory. Based on the TS theory, using the steepest descent method, the Laplace transform and its inverse transform, YL method is inferred. The YL method has been proven as a very suitable method for solving rate constant and analyzing anharmonic effect (In 1962, Schlag and Sandsmark experimentally confirmed the existence and importance of anharmonic effect.19 Anharmonic effect has attracted the attention of more and more researchers, and it cannot be ignored especially in high-temperature range.2031). With respect to YL method, the rate constant is obtained and the anharmonic effect is discussed according to the frequencies, energies and other parameters calculated by Gauss View 5.0 and Gaussian 09 software. Furthermore, based on the rate constant, the three kinetic parameters (A, n, E) of the Arrhenius formula were fitted according to the least square method, and the detailed kinetic mechanisms of these reactions had been worked out. The research in this paper will provide a theoretical basis for subsequent research of the ozone denitration reactions.

EXPERIMENTAL CALCULATION METHODOLOGY AND COMPUTATIONAL THEORY

Ab initio Calculations

For the reactions of NO with NO, NO2, NO3 and N2O, the geometries of the reactants and TSs were optimized at the B3LYP/6-311++G(d,p) level. The B3LYP method is currently most cost-effective approach for anharmonic corrections.32 However, B3LYP method is not suit to calculate the reactions of NO with O, O2 and O3. M062X is the one of best functionals for a combination of main-group thermochemistry and kinetics. At the same time, the M062X functionals is recommended most highly for the study of main-group thermochemistry and kinetics.33 Therefore, for the reactions of NO with O, O2 and O3, the geometries of the reactants and TSs were optimized at the M062X/6-311++G(d,p) level. Here, Vibrational harmonic and anharmonic frequencies were used to identify all of the stationary points. In order to obtain the valid geometry of TS, intrinsic reaction coordinate (IRC) was traced at the same level. Then, the single-point energies (SPEs) were worked out by the coupled cluster QCISD(T) method with 6-311++G(d,p) basis set. At least, in order to obtain the more exact and trustworthy analog data, the calculated barriers were revised by zero-point energy (ZPE). All of the ab initio calculations of frequency and energy were carried out by Gaussian 09 program.29,34,35

Besides, the reactions calculated in this paper are mainly ground state reactions. States of relative species are considered by spin multiplicity (spin multiplicity=2S+1, S=u/2, S is spin angular momentum, u is single electron number) in the Table 1.36 It is worth noting that spin multiplicity of ground states for O and O2 are 3 (3O and 3O2), and spin multiplicity of excited states for O and O2 are 1 (1O and 1O2). Therefore, for calculating relative energies and kinetics data, these two reactions (NO with O and O2) are worked out considering ground state (2NO+3O→2NO2, 2NO+3O22NO2+3O) and excited state (2NO+1O→4NO2, 2NO+1O22NO2+1O). Other reactions of this paper calculated are ground state reactions, furthermore, atoms/molecules without providing the information about the spin multiplicity are all ground state species.

Table1.

Spin multiplicity of ground state and excited state for relative reactants and products in this paper

Species Spin multiplicity of ground state Spin multiplicity of excited state
NO 2 4
NO2 2 4
NO3 2 4
N2O 1 3
O 3 1
O2 3 1
O3 1 3
N2 1 3

Transition State Theory

According to the TS theory, it is well known that the rate constant k(T) expression for unimolecular reaction is expressed as:3742

(1)
k ( T ) = k b T h Q ( T ) Q ( T ) e E k b T

where kb is Boltzmann’s constant, T is the temperature of the system, h is the Planck’s constant, and E is the activation energy. Q(T) and Q(T) are partition functions of reactant and TS, respectively.

Similarly, the rate constant k(T) expression for bimolecular reaction can be expressed as below:

(2)
k ( T ) = k b T h Q ( T ) Q A ( T ) Q B ( T ) e E k b T

where QA(T) and QB(T) represents the partition function for the two reactants of A and B, respectively. The expression of the partition function is:

(3)
Q = i N q i = i N n i n i ( m ) e β E n i

where qi is the ith partition function of vibration mode, N is the number of the vibrational modes of reactant, b=1/kbT, Eni is ith vibrational mode energy. And the logarithmic function of Q can be expressed as follows:

(4)
ln Q = i N ln q i = i N ln n i n i ( m ) e β E n i

Here, applies YL method to calculate the partition function, which takes advantage of Laplace transformation, inverse Laplace transformation and Morse oscillators (MO).29,34,43 MO potential is applied to calculate the partition function. For MO,

(5)
q i = n i n i ( m ) e β E n i

(6)
E n i = n i + 1 2 ω i x i n i + 1 2 2 ω i

where ωi is the frequency of the ith vibrational mode, ni is the vibrational quantum number of ith vibrational mode, and ni(m)=1/2xi-1/2. xi is the anharmonic constant for various molecules, and ℏ=h/2π. Hence, the rate constant can be worked out by the corresponding expressions, and the anharmonic effect in the canonical case can be discussed in this paper.

Numerical Fitting of the Kinetics Parameters of Reaction Mechanism

According to the Arrhenius equation, the rate constant expression in the canonical ensemble is expressed as below:44,45

(7)
k = A T n e E R T

where A represents pre-exponential factor, n represents the temperature exponent. E represents the activation energy of reaction, and R=8.314 J·mol-1·K-1. Then, the equation can be expressed as follows:

(8)
y = f ( x ) = a 0 + a 1 x + a 2 e x

where, lnk=y, lnT=x, T=ex, a0=lnA, a1=n, a2=-E/R. Based on the least square method:

(9)
m = 1 i = z y i f ( x i ) 2

(10)
m = 1 i = z y i b 0 b 1 x i b 2 e x i 2

where m is the least numerical value of the right side of the equation, z is the total number of the rate constants corresponding to different temperatures. Subsequently, it is obvious that the differentiating values of b0, b1 and b2 are zero, respectively.

(11)
m b 0 = 2 1 i = z y i b 0 b 1 x i b 2 e x i = 0

(12)
m b 1 = 2 x i 1 i = z y i b 0 b 1 x i b 2 e x i = 0

(13)
m b 2 = 2 e x i 1 i = z y i b 0 b 1 x i b 2 e x i = 0

So far, the kinetics parameters of Arrhenius formula can be worked out.

RESULTS AND DISCUSSION

For this work, the reactions related to NO in the ozone denitrification reaction were studied, which will provide some theoretical support for the research of the whole reaction mechanism. The specific reaction processes are shown as follows:

NO+O TS1 NO 2   NO+O 2 TS2 NO 2 +O NO+O 3 TS3 a IM1 TS3 b NO 2 +O 2 NO+NO TS4 a IM2 TS4 b N 2 +O 2 TS4 c O+N 2 O NO+NO 2 TS5 a IM3 TS5 b N 2 O+O 2 NO+NO 3 TS6 2 NO 2 NO+N 2 O TS7 NO 2 +N 2

For each of the above reactions, the geometry optimizations of the reactant and TS were optimized, meanwhile, the frequency and energy were obtained. The Gibbs free energies (ΔG), reaction enthalpies (ΔH) and potential barriers (ΔE) were listed in the Tables 2-8, and the potential energy surfaces (PES) were shown in the Figs. 1-6. According to these parameters, the harmonic rate constants and anharmonic rate constants were calculated at the temperature range from 300 K to 4000 K in the Figs. 7-13. The detailed calculation results were described as follows.

Table2.

The Gibbs free energies, reaction enthalpies and potential barriers for the reaction of NO+O

Reaction path ΔG M062X kcal·mol-1 ΔH M062X kcal·mol-1 ΔE M062X kcal·mol-1 ΔE QCISD(T) kcal·mol-1
NO+O 0 0 0 0
TS1 29.48 15.55 16.73 22.98
NO2 -49.32 -65.32 -64.15 -60.25
Table3.

The Gibbs free energies, reaction enthalpies and potential barriers for the reaction of NO+O2

Reaction path ΔG M062X kcal·mol-1 ΔH M062X kcal·mol-1 ΔE M062X kcal·mol-1 ΔE QCISD(T) kcal·mol-1
NO+O2 0 0 0 0
TS2 99.22 81.07 82.27 83.49
NO2+O 50.16 48.43 48.44 42.86
Table4.

The Gibbs free energies, reaction enthalpies and potential barriers for the reaction of NO+O3

Reaction path ΔG M062X kcal·mol-1 ΔH M062X kcal·mol-1 ΔE M062X kcal·mol-1 ΔE QCISD(T) kcal·mol-1
NO+O3 0 0 0 0
TS3a 7.05 -10.75 -9.56 6.12
IM1 -4.86 -24.48 -23.30 -12.16
TS3b -5.18 -24.30 -23.12 -16.27
NO2+O2 -64.83 -64.54 -64.55 -50.01
Table5.

The Gibbs free energies, reaction enthalpies and potential barriers for the reaction of NO+NO

Reaction path ΔG B3LYP kcal·mol-1 ΔH B3LYP kcal·mol-1 ΔE B3LYP kcal·mol-1 ΔE QCISD(T) kcal·mol-1
NO+NO 0 0 0 0
TS4a 90.48 68.69 69.88 74.58
IM2 71.94 50.04 51.23 52.95
TS4b 105.68 85.47 86.66 96.10
TS4c 105.71 85.46 86.66 95.41
N2+O2 -39.60 -41.58 -41.58 -41.31
O+N2O 41.78 36.39 36.36 36.32
Table6.

The Gibbs free energies, reaction enthalpies and potential barriers for the reaction of NO+NO2

Reaction path ΔG B3LYP kcal·mol-1 ΔH B3LYP kcal·mol-1 ΔE B3LYP kcal·mol-1 ΔE QCISD(T) kcal·mol-1
NO+NO2 0 0 0 0
TS5a 83.27 78.98 80.17 78.64
IM3 76.02 71.38 72.58 72.96
TS5b 72.18 65.64 66.83 155.93
N2O+O2 -22.94 -8.71 -8.71 -6.78
Table7.

The Gibbs free energies, reaction enthalpies and potential barriers for the reaction of NO+NO3

Reaction path ΔG B3LYP kcal·mol-1 ΔH B3LYP kcal·mol-1 ΔE B3LYP kcal·mol-1 ΔE QCISD(T) kcal·mol-1
NO+NO3 0 0 0 0
TS6 6.99 -17.45 -16.26 1.94
2NO2 11.57 -22.90 -22.90 -35.73
Table8.

The Gibbs free energies, reaction enthalpies and potential barriers for the reaction of NO+N2O

Reaction path ΔG B3LYP kcal·mol-1 ΔH B3LYP kcal·mol-1 ΔE B3LYP kcal·mol-1 ΔE QCISD(T) kcal·mol-1
NO+N2O 0 0 0 0
TS7 54.76 38.44 39.63 50.73
NO2+N2 -16.66 -32.87 -32.87 -34.53
Figure1.

The potential energy surfaces for the reaction of NO+O at QCISD(T)/6-311++G(d,p) level.

jkcs-65-185-f001.tif
Figure2.

The potential energy surfaces for the reaction of NO+O2 at QCISD(T)/6-311++G(d,p) level.

jkcs-65-185-f002.tif
Figure3.

The potential energy surfaces for the reaction of NO+O3 at QCISD(T)/6-311++G(d,p) level.

jkcs-65-185-f003.tif
Figure4.

The potential energy surfaces for the reaction of NO+NO at QCISD(T)/6-311++G(d,p) level.

jkcs-65-185-f004.tif
Figure5.

The potential energy surfaces for the reaction of NO+NO2 at QCISD(T)/6-311++G(d,p) level.

jkcs-65-185-f005.tif
Figure6.

The potential energy surfaces for the reactions of NO+NO3 and NO+N2O at QCISD(T)/6-311++G(d,p) level.

jkcs-65-185-f006.tif
Figure7.

The harmonic and anharmonic rate constants for the reaction of NO+O from 300 K to 4000 K.

jkcs-65-185-f007.tif
Figure8.

The harmonic and anharmonic rate constants for the reaction of NO+O2 from 300 K to 4000 K.

jkcs-65-185-f008.tif
Figure9.

The harmonic and anharmonic rate constants for the reaction of NO+O3 from 300 K to 4000 K.

jkcs-65-185-f009.tif
Figure10.

The harmonic and anharmonic rate constants for the reaction of NO+NO from 300 K to 4000 K. ((a) TS4a, (b) TS4b and TS4c).

jkcs-65-185-f010.tif
Figure11.

The harmonic and anharmonic rate constants for the reaction of NO+NO2 from 300 K to 4000 K. ((a) TS5a, (b) TS5b).

jkcs-65-185-f011.tif
Figure12.

The harmonic and anharmonic rate constants for the reaction of NO+NO3 from 300 K to 4000 K.

jkcs-65-185-f012.tif
Figure13.

The harmonic and anharmonic rate constants for the reaction of NO+N2O from 300 K to 4000 K.

jkcs-65-185-f013.tif

NO+O

Concerning this reaction, the reaction equation was NO+O→NO2, and the graph of the potential energy surface was shown in the Fig. 1. It can be seen that the barrier was 22.98 kcal·mol-1 when the reaction was in ground state. Besides, this reaction was predicted to be exothermic and exergonic with ΔH=−65.32 kcal·mol-1 and ΔG=−49.32 kcal·mol-1 calculated at M062X method as shown in the Table 2. According to the obtained data, the harmonic and anharmonic rate constants at the temperature range from 300 K to 4000 K in the canonical ensemble were worked and listed in the Fig. 7. It can be seen that harmonic and anharmonic rate constants had the same order of magnitudes at the same temperature, and these two curves of rate constants were very close, which means the anharmonic effect was not obvious. Besides, in order to verify this calculation, the calculated rate constants by this work were compared with the researches by others. The obtained rate constants by Tsang were 1.81×1013 cm3·mol-1·s-1 at 300 K and 3.69×1012 cm3·mol-1·s-1 at 2500 K,46 and the result by Cobos was 13 order of magnitudes from 300 K to 1900 K.47 Although the rate constants were up with the temperature rising, the rate constant of this reaction was only 10 order of magnitudes when the temperature reached 2800 K. Therefore, the excited state reaction of NO+1O→4NO2 were worked out. It was clear that the calculated values of excited state reaction were closer to references than that ground state. And, the rate constants were 13 order of magnitudes when the temperature reached 1900 K. Therefore, the calculated results by this work were reliable.

NO+O2

For the reaction channel of NO+O2→NO2+O, from the Table 3, this reaction was not easy to occur because of ΔH=48.43 kcal·mol-1 and ΔG=50.16 kcal·mol-1 calculated at M062X method, and the barrier was 83.49 kcal·mol-1 at QCISD(T) method. The potential energy surface was shown in the Fig. 2, and the harmonic and anharmonic rate constants at the temperature range from 300 K to 4000 K were given in the Fig. 8. When the temperature was above 1300 K, the reaction can occur slowly. When the temperature was 1600 K, the anharmonic rate constant was 9.80×103 cm3·mol-1·s-1. Besides, the rate constants calculated by this work were compared with Dumas’s for this reaction channel at 300 K.48 Similarly, it can be seen that the calculated values of excited state reaction were closer to references than that ground state. Therefore, it was reliable that the ground state reaction of NO+O2→NO2+O was not easy to occur.

NO+O3

This reaction was not a one-step reaction. With regard to the detailed reaction progress, O3 combined with NO to generate intermediate 1 (IM1) via the channel of TS3a firstly, and then IM1 cleaved into NO2 and O2 by the channel of TS3b. For the whole reaction process, the potential energy surface was shown in the Fig. 3. The related geometries of stationary point of this reaction channel were similar to that of trans PES channels by Julio.49 Among them, the barrier for reaction process of channel TS3a was 6.12 kcal·mol-1, and the barrier of channel TS3b was −4.11 kcal·mol-1. Owing to the barrier-less reaction of the second step, the whole rate constant can be expressed by the first step. Besides, from the Table 4, this reaction was predicted to be exothermic and exergonic with ΔH=−64.54 kcal·mol-1 and ΔG=−64.83 kcal·mol-1 calculated at M062X method and ΔE=−50.01 kcal·mol-1 at QCISD(T) method. Therefore, this reaction was crucial for the conversion process of NO.

The harmonic and anharmonic rate constants at the temperature range from 300 K to 4000 K in the canonical ensemble were given in the Fig. 9. Moreover, the rate constants obtained by this study were compared with DeMore’s and Borders’s for this reaction channel.50,51 The rate constants of DeMore’s paper were 1.10×109 cm3·mol-1·s-1 at 200 K and 1.13×1010 cm3·mol-1·s-1 at 300 K. The rate constants of Borders’s paper were 1.35×109 cm3·mol-1·s-1 at 200 K, 1.18×1010 cm3·mol-1·s-1 at 300 K and 2.83×1010 cm3·mol-1·s-1 at 350 K. In this paper, the anharmonic and harmonic rate constant were 6 order of magnitudes at 200 K, and 9 order of magnitudes at 300 K, respectively. When the temperature was 350 K, the harmonic and anharmonic rate constant was 3.32×1010 cm3·mol-1·s-1 and 1.10×1010 cm3·mol-1·s-1. The rate constant calculated by this work were very close to that by Borders at 350 K. Therefore, this calculation was reliable. Moreover, when the temperature was 4000 K, the harmonic rate constant (1.10×1019 cm3·mol-1·s-1) differed from anahrmonic rate constant (1.31×1016 cm3·mol-1·s-1) 829.69 times. It can be seen that effect of anharmonic factor on rate constant were up with the increasing temperature, and the anharmonic effect at the high temperature range was more obvious than the low temperature range. Therefore, the anharmonic effect was very obvious and cannot be ignored especially in high temperature environment.

NO+NO

The researches on the reaction between NO and NO have not been studied deeply,37,52,53 this work conducted research on this reaction generating the final products. As shown in the Table 5 and Fig. 4, firstly, NO combined with NO to form IM2 via the reaction channel of TS4a, then IM2 broke into two products via TS4b and TS4c, respectively. The barrier for reaction processes of channel TS4a, 4b, 4c were 74.58 kcal·mol-1, 43.15 kcal·mol-1, 42.46 kcal·mol-1 at QCISD(T) method, respectively. Moreover, the reaction of NO+NO→N2+O2 was predicted to be exothermic and exergonic with ΔH=−41.58 kcal·mol-1 and ΔG=−39.61 kcal·mol-1, and the reaction of NO+NO→N2O+O was predicted to be endothermic and endergonic with ΔH=36.39 kcal·mol-1 and ΔG=41.78 kcal·mol-1 calculated at M062X method. However, owing to the high barrier, the reaction NO+NO→N2+O2 was not easy to occur, even though this reaction was endothermic and endergonic.

According to the obtained data, the anharmonic and harmonic rate constants at the temperature range from 300 K to 4000 K in the canonical ensemble were calculated. For TS4a, the rate constants were given in the Fig. 10(a). When the temperature was above 1300 K, the reaction can slowly occur. The rate constants were 4 order of magnitudes at 1600 K. And, when the temperature was 4000 K, the anharmonic rate constant was 1.32×1012 cm3·mol-1·s-1. The harmonic rate constant was 8.79×1011 cm3·mol-1·s-1. It can be seen that the curves of harmonic and anharmonic rate constants at the same temperature were relatively close, which indicates the anharmonic effect was not obvious. However, the rate constant changed rapidly at the low temperature range (300 K - 1000 K), and the rate constant changed gradually at the high temperature range (1000 K - 4000 K). In general, the rate constant at the high temperature range was still higher than the low temperature range. Besides, in order to verify this calculation, the rate constants obtained by Yuan, Freedman and Trung were compared with this calculation.5456 It can be seen that the ate constant calculated by this work were similar to these references. Therefore, this work was reliable.

For TS4b and TS4c, the rate constants were given in the Fig. 10(b). It was clear that the rate constants were similar at the same temperature for these two reaction channels. As shown in the Fig. 10(b), the rate constant changed rapidly at the low temperature range (300 K - 1000 K), and the rate constant changed gradually at the high temperature range (1000 K - 4000 K). In general, the anharmonic effect was not obvious. However, the anharmonic effect at the high temperature range was still more obvious than the low temperature range. On the whole, the rate constant at the high temperature range was still higher than the low temperature range.

NO+NO2

This reaction was a two-step reaction. Firstly, NO2 combined with NO to form IM3 via the passage of TS5a. Then, IM3 was cleaved into N2O and O2 by TS5b. For the whole reaction process, the potential energy surface was shown in the Fig. 5. Among them, the barrier for reaction process of channel TS5a was 78.64 kcal·mol-1, and the barrier for reaction process of channel TS5b was 82.93 kcal·mol-1. It was clear that the reaction was difficult to occur because of the high barrier, even though this whole reaction process was exothermic and exergonic as shown in the Table 6 and Fig. 5.

For TS5a, the harmonic and anharmonic rate constants at the temperature range from 300 K to 4000 K in the canonical ensemble were given in the Fig. 11(a). the harmonic rate constant was 12 order of magnitudes at above 3100 K. the anharmonic rate constant was 10 order of magnitudes at above 3100 K. Therefore, the anharmonic effect of this reaction was obvious and cannot be ignored especially at high temperature range. And, the anharmonic effect at the high temperature range was still more obvious than the low temperature range. On the whole, the rate constant at the high temperature range was still higher than the low temperature range.

For TS5b, the harmonic and anharmonic rate constants at the temperature range from 300 K to 4000 K in the canonical ensemble were given in the Fig. 11(b). As shown in the figure, the rate constant changed rapidly at the low temperature range (300 K - 1000 K), and the rate constant changed gradually at the high temperature range (1000 K - 4000 K). In general, the anharmonic effect was not obvious. However, the anharmonic effect at the high temperature range was still more obvious than the low temperature range. On the whole, the rate constant at the high temperature range was still higher than the low temperature range.

NO+NO3

For this reaction, the reaction equation was NO+NO3→2NO2, and the barrier of reaction channel was 1.94 kcal·mol-1 from the Table 7. Therefore, this reaction was very easy to occur. The potential energy surface was shown in the Fig. 6, and the harmonic and anharmonic rate constants at the temperature range from 300 K to 4000 K in the canonical ensemble were given in the Fig. 12. Furthermore, rate constants calculated by this work were compared with the Atkinsons’ and Ashmores’ for this reaction channel.57,58 When the temperature range was from 300 K to 4000 K, the reference value of rate constants obtained by Atkinson reached 13 orders of magnitude. And the data obtained by Ashmore was 11-12 orders of magnitude at 500-700 K. In this paper, the rate constant was 13 orders of magnitude at about 600 K. Therefore, this result was similar to that reference at low temperature range. Moreover, the rate constant was 17 orders of magnitude at about 4000 K. The anharmonic and harmonic rate constant was close at the same temperature. Therefore, the anharmonic effect was not obvious. In addition, the rate constants were up with the temperature rising, and the curve of rate constants changing with temperature was steep from 300 K to 1000 K (low temperature range), whereas the curve was gentle at 1000 K - 4000 K (high temperature range). In general, the rate constant at the high temperature range was still higher than the low temperature range.

NO+N2O

For the reaction channel of NO+N2O→NO2+N2, as shown in the Table 8, the reaction of was predicted to be exothermic and exergonic with ΔH=-32.87 kcal·mol-1 and ΔG=-16.66 kcal·mol-1 calculated at M062X method, and the barrier and ΔE of this reaction was 50.73 kcal·mol-1 and -34.53 kcal·mol-1 at QCISD(T) method. According to the obtained data, the potential energy surface was shown in the Fig. 6, and the harmonic and anharmonic rate constants at the temperature range from 300 K to 4000 K in the canonical ensemble were given in the Fig. 13. The harmonic and anharmonic rate constants were -24 orders of magnitude at about 300 K. When the temperature was 1600 K, the harmonic rate constant (7.63×109 cm3·mol-1·s-1) was great 713.08 times than that anharmonic (1.07×107 cm3·mol-1·s-1). When the temperature was 4000 K, the harmonic rate constant (1.14×1016 cm3·mol-1·s-1) was great 57000 times than that anharmonic (2.00×1011 cm3·mol-1·s-1). Therefore, the anharmonic effect was obvious and cannot be ignored especially in high temperature range. And, the anharmonic effect at the high temperature range was still more obvious than the low temperature range. Besides, in order to verify this calculation, the rate constants were compared with other data.5962 As shown in the Fig. 13, the reference of others mainly was corresponding with the harmonic rate constant of this work. Therefore, this calculation was credible and anharmonic effect of this reaction cannot be ignored.

The Fitted Kinetic Parameters

In addition, according to above calculation, A, n, E of Arrhenius equation related to NO in the ozone denitration reactions respectively were fitted and listed in the Table 9 through obtained anharmonic and harmonic rate constants at the temperature range from 300 K to 4000 K. Therefore, kinetic parameters of these reactions were worked out. Next, the numerical simulation by CHEMKIN can be accomplished through the fitted kinetic results. Besides, it was worth noting that the fitted anharmonic and harmonic parameters were different. Therefore, the research of anharmonic effect cannot be ignored.

Table9.

The fitted kinetics parameters of all the reactions in this paper

Reaction path Anharmonic Harmonic
A n E A n E
NO+O→TS1a→NO2 1.53×105 1.95 9.54×104 4.85×105 2.07 9.41×104
NO+1O→TS1b→4NO2 4.73×106 1.48 -8.84×104 7.24×104 2.00 -9.41×104
NO+O2→TS2a→NO2+O 3.44×106 2.76 3.51×105 3.96×101 4.20 3.43×106
NO+1O2→TS2b→NO2+1O 5.25×107 2.12 1.15×105 1.25×102 4.08 1.10×105
NO+O3→TS3→NO2+O2 2.04×1011 1.47 3.35×104 1.50 5.31 2.13×104
NO+NO→TS4a→IM2 4.75×102 3.76 3.07×105 3.48×101 3.99 3.04×105
IM2→TS4b→N2+O2 1.39×1016 -0.77 1.87×105 1.78×1013 0.23 1.85×105
IM2→TS4c→O+N2O 1.64×1016 -0.79 1.84×105 1.72×1013 0.23 1.82×105
NO+NO2→TS5a→IM3 3.58×1010 1.52 3.36×105 2.39×10-1 5.22 3.23×105
IM3→TS5b→N2O+O2 3.24×1011 0.52 3.47×105 4.27×1012 0.02 3.48×105
NO+NO3→TS6→2NO2 1.06×10-1 5.07 2.50×102 4.64 4.75 1.32×103
NO+N2O→TS7→NO2+N2 1.17×1014 0.03 2.19×105 3.75×10-1 5.33 2.07×105

The unit of unimolecule decomposition reaction for A was s-1, the unit of biomolecule reaction for A was cm3·mol-1·s-1, unit of E was J·mol-1.

CONCLUSION

The detailed mechanism of ozone oxidation denitration is complicated. In this paper, the related reactions involving NO in the ozone denitrification process were researched, including the reactions of NO with O, O2, O3, NO, NO2, NO3 and N2O. The geometry optimizations of reactants and TSs were optimized. Moreover, the frequencies and energies of reactants and TSs were calculated by Gauss View 5.0 and Gaussian 09 software. The harmonic and anharmonic rate constants of these reactions were calculated by YL method combined with TS theory. At the same time, according to the Arrhenius formula and the least square method, three kinetic parameters of Arrhenius equation were worked out considering anharmonic and harmonic factor, respectively. Furthermore, the anharmonic effect of the related reactions involving NO in the process of ozone denitrification can be researched in this paper.

In conclusion, it was easy for the reactions of NO with NO3 and O3 to occur because of its extremely low barrier, and the rate constant was relatively large. Therefore, these two reactions were curial for the conversion process of NO. Such as the reaction of NO with NO3, the anharmonic rate constant can reach 11 orders of magnitude at room temperature and up to 17 orders of magnitude at 4000 K.

In addition, for NO+O, O2, NO and NO3, it can be seen that the harmonic and anharmonic rate constants at the same temperature were relatively close, and the anharmonic effect was not obvious. But for NO+O3, NO2 and N2O, the harmonic and anharmonic rate constants at 300 K were relatively approximate, however, there was an apparent difference between the harmonic and anharmonic rate constants at 4000 K, which means that the anharmonic effect was obvious for those three reactions at high temperature. Therefore, the anharmonic effect cannot be neglected for the NO-related reactions, especially at high temperature range.

Furthermore, the detailed mechanism and kinetic parameters of the NO-related reactions in ozone oxidation denitration process were researched by these calculations and analysis. For the subsequent researches of ozone denitrification reactions and other reactions involving NO, these data can provide some theoretical support.

Acknowledgements

This work was supported by the Major Research plan of the National Natural Science Foundation of China (Grant No.91441132). And the Publication cost of this paper was supported by the Korean Chemical Society.

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