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Modelling ozonolysis in a
multi-inlet flow reactor
Mixtli Campos-Pineda
Group Meeting 2
Fall 2016
1 2 3 4 5 76 8 109P
To pump
39.75”
22.75”
Purge N2 Purge N2
Orange: Ozone
inlet
Green: Alkene inlet
(+ Oxygen during
oxygen
experiments)
Blue: plugged port (ultratorr+cap)
Multi-inlet flow cell/CRDS cavity
Ozone flow manifold
FMFM
N2
in
Ozone
adsorbed
in silica gel
To flow cell
Alkene + N2 + Scavenger flow manifold
FM
FM N2 in
FM
O2 in
(oxygen experiments only)
Alkene in
To flow cell
Simulation of the reaction in a flow reactor.
The system of ODEs is solved using
an approximation method by the
kinetic simulator KINTECUS.
Multi-Inlet Flow Cell (reaction perpendicular to beam)
1 2 3 4 5 76 8 109P
Ozone
in
Alkene/Nitrogen
/Scavenger in
1 2 3 4 5 76 8 109P
To
pump
Pros:
• Every segment is independent
• No carryover reaction
• Simple modelling
Cons:
• Turbulence
Multi-Inlet Flow Cell (reaction parallel to beam)
1 2 3 4 5 76 8 109P
To pump
Ozone +
Alkene
Ozone
Pros:
• Greatly reduced turbulence
Cons:
• Measurement is the average of segment concentrations
• Initial conditions change for each segments
1 2 3 4 5 76 8 109P
To pump
39.75”
22.75”
Purge N2 Purge N2
Orange: Ozone
inlet
Green: Alkene inlet
(+ Oxygen during
oxygen
experiments)
Blue: plugged port (ultratorr+cap)
Multi-inlet flow cell/CRDS cavity
Total flow changes due to ozone addition:
• Ozone “spike” concentration changes
• Species concentrations change
We measure averages:
Nozone,average = [O3
0+(O3
1+(F1/F2)O3
0)+...+(O3
9+(F9/F10)O3
0)]/10
Nozone,segment = O3
s-1+(Fs-1/Fs)O3
0
Nspecies,segment = (Fs-1/Fs) Nspecies,s-1
Nspecies,average = [∑1
10 Nspecies,s]/10
0 1E16 2E16 3E16 4E16 5E16 6E16 7E16 8E16 9E16
0.20
0.40
0.60
0.80
1.00
1.20
[CH2
CHO]/[CH2
CHO]0
Oxygen (molecules/cc)
11/4/16
5/5/16
Vinoxy data (with new experiments from Friday)
+
O3
CH2CO CH3OH
SOZ
++H2O
P
P
P
P
P
+
+
P
+ 2O2 P
SOZ
P
OH
OH + CO
OH
O2
H2OO3
OH
wall
decomp
wall
CH2OH
CH3O
H2O
OH
O2
+ HO2
OHOH
HO2 + O2
P
0.5 OH + P
trans-2-butene ozonolysis
mechanism used in
KINTECUS (11/06/2016)
2 +H2O+H2C2
1.00 0.1 0.5 0.05 0.07
0.950.05
0.85
0.15
1.1E-12
2.6E-14
3.6E-15
1.7E-16
7.5E-13
1.9E-16
6.4E-11
1.6E-12
4E-18
370 s-1
1E-15
1E-12
6.12E-15
1.84E-14
3.67E-14
1E-11
9.1E-12
1E-11
10 s-1
10 s-1
1E-11 HCHO + OH HCO + H2O
7.5E-13
Modelling ozonolysis in a multi-inlet flow reactor
Modelling ozonolysis in a multi-inlet flow reactor
0 2 4 6 8 10
0.00E+000
2.00E+013
4.00E+013
6.00E+013
8.00E+013
F
A
CH2CHO
No oxygen
No oxygen
0 2 4 6 8 10
0.00E+000
2.00E+010
4.00E+010
6.00E+010
8.00E+010
1.00E+011
1.20E+011E
A
CH3CHOO
8.45E15 molecule/cc oxygen
0 2 4 6 8 10
0.00E+000
1.00E+012
2.00E+012
F
A
CH2CHO
8.45E15 molecule/cc oxygen
0 2 4 6 8 10
-2.00E+010
0.00E+000
2.00E+010
4.00E+010
6.00E+010
8.00E+010
1.00E+011
1.20E+011
1.40E+011
1.60E+011
1.80E+011
E
A
CH3CHOO
8.45E15 molecule/cc oxygen
0 2 4 6 8 10
6.80E+015
7.00E+015
7.20E+015
7.40E+015
7.60E+015
7.80E+015
8.00E+015
8.20E+015
8.40E+015
8.60E+015
G
A
O2
0.00E+000 2.00E+015 4.00E+015 6.00E+015 8.00E+015 1.00E+016
0.0
0.2
0.4
0.6
0.8
1.0
Simulation
Exp 11/04/2016
Oxygen (molecule/cc)
[Vinoxy]/[Vinoxy]0
0.5
0.6
0.7
0.8
0.9
1.0
1.1
1.2
[Vinoxy]/[Vinoxy]0
Comparison experiment vs simulation
• Vinoxy concentration from modelling much higher:
 Yield of vinoxy in model is overestimated
 Not enough vinoxy depletion channels, or rates underestimated
• Vinoxy depletion by oxygen much higher:
 Vinoxy + Oxygen rates overestimated
 High vinoxy concentration in modelling driving reaction
 Not enough oxygen depletion channels, or rates underestimated
+
O3
CH2CO CH3OH
SOZ
++H2O
P
P
P
P
P
+
+
P
+ 2O2 P
SOZ
P
OH
OH + CO
OH
O2
H2OO3
OH
wall
decomp
wall
CH2OH
CH3O
H2O
OH
O2
+ HO2
OHOH
HO2 + O2
P
0.5 OH + P
trans-2-butene ozonolysis
mechanism used in
KINTECUS (11/06/2016)
2 +H2O+H2C2
1.00 0.1 0.5 0.05 0.07
0.950.05
0.85
0.15
1.1E-12
2.6E-14
3.6E-15
1.7E-16
7.5E-13
1.9E-16
6.4E-11
1.6E-12
4E-18
370 s-1
1E-15
1E-12
6.12E-15
1.84E-14
3.67E-14
1E-11
9.1E-12
1E-11
10 s-1
10 s-1
1E-11 HCHO + OH HCO + H2O
7.5E-13
0 2 4 6 8 10
0.00E+000
2.00E+010
4.00E+010
6.00E+010
8.00E+010
1.00E+011
1.20E+011
E
A
CH3CHOO
Revisiting Criegee Intermediates
Modelling ozonolysis in a multi-inlet flow reactor
Modelling ozonolysis in a multi-inlet flow reactor
What about acetone oxide?
+ O3
+
0 2 4 6 8 10
-1.00E+011
0.00E+000
1.00E+011
2.00E+011
3.00E+011
4.00E+011
5.00E+011
6.00E+011
7.00E+011
G
A
CH3CO2CH3
Parallel
0 5 10
8.60E+011
8.80E+011
9.00E+011
9.20E+011
9.40E+011
9.60E+011
9.80E+011
1.00E+012
1.02E+012
1.04E+012
F
A
CH3CO2CH3
Perpendicular
Summary
Mechanism for t2b need more work!
Time to revisit measurement of CIs

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Modelling ozonolysis in a multi-inlet flow reactor

  • 1. Modelling ozonolysis in a multi-inlet flow reactor Mixtli Campos-Pineda Group Meeting 2 Fall 2016
  • 2. 1 2 3 4 5 76 8 109P To pump 39.75” 22.75” Purge N2 Purge N2 Orange: Ozone inlet Green: Alkene inlet (+ Oxygen during oxygen experiments) Blue: plugged port (ultratorr+cap) Multi-inlet flow cell/CRDS cavity
  • 3. Ozone flow manifold FMFM N2 in Ozone adsorbed in silica gel To flow cell Alkene + N2 + Scavenger flow manifold FM FM N2 in FM O2 in (oxygen experiments only) Alkene in To flow cell
  • 4. Simulation of the reaction in a flow reactor. The system of ODEs is solved using an approximation method by the kinetic simulator KINTECUS.
  • 5. Multi-Inlet Flow Cell (reaction perpendicular to beam) 1 2 3 4 5 76 8 109P Ozone in Alkene/Nitrogen /Scavenger in 1 2 3 4 5 76 8 109P To pump Pros: • Every segment is independent • No carryover reaction • Simple modelling Cons: • Turbulence
  • 6. Multi-Inlet Flow Cell (reaction parallel to beam) 1 2 3 4 5 76 8 109P To pump Ozone + Alkene Ozone Pros: • Greatly reduced turbulence Cons: • Measurement is the average of segment concentrations • Initial conditions change for each segments
  • 7. 1 2 3 4 5 76 8 109P To pump 39.75” 22.75” Purge N2 Purge N2 Orange: Ozone inlet Green: Alkene inlet (+ Oxygen during oxygen experiments) Blue: plugged port (ultratorr+cap) Multi-inlet flow cell/CRDS cavity Total flow changes due to ozone addition: • Ozone “spike” concentration changes • Species concentrations change
  • 8. We measure averages: Nozone,average = [O3 0+(O3 1+(F1/F2)O3 0)+...+(O3 9+(F9/F10)O3 0)]/10 Nozone,segment = O3 s-1+(Fs-1/Fs)O3 0 Nspecies,segment = (Fs-1/Fs) Nspecies,s-1 Nspecies,average = [∑1 10 Nspecies,s]/10
  • 9. 0 1E16 2E16 3E16 4E16 5E16 6E16 7E16 8E16 9E16 0.20 0.40 0.60 0.80 1.00 1.20 [CH2 CHO]/[CH2 CHO]0 Oxygen (molecules/cc) 11/4/16 5/5/16 Vinoxy data (with new experiments from Friday)
  • 10. + O3 CH2CO CH3OH SOZ ++H2O P P P P P + + P + 2O2 P SOZ P OH OH + CO OH O2 H2OO3 OH wall decomp wall CH2OH CH3O H2O OH O2 + HO2 OHOH HO2 + O2 P 0.5 OH + P trans-2-butene ozonolysis mechanism used in KINTECUS (11/06/2016) 2 +H2O+H2C2 1.00 0.1 0.5 0.05 0.07 0.950.05 0.85 0.15 1.1E-12 2.6E-14 3.6E-15 1.7E-16 7.5E-13 1.9E-16 6.4E-11 1.6E-12 4E-18 370 s-1 1E-15 1E-12 6.12E-15 1.84E-14 3.67E-14 1E-11 9.1E-12 1E-11 10 s-1 10 s-1 1E-11 HCHO + OH HCO + H2O 7.5E-13
  • 13. 0 2 4 6 8 10 0.00E+000 2.00E+013 4.00E+013 6.00E+013 8.00E+013 F A CH2CHO No oxygen
  • 14. No oxygen 0 2 4 6 8 10 0.00E+000 2.00E+010 4.00E+010 6.00E+010 8.00E+010 1.00E+011 1.20E+011E A CH3CHOO
  • 15. 8.45E15 molecule/cc oxygen 0 2 4 6 8 10 0.00E+000 1.00E+012 2.00E+012 F A CH2CHO
  • 16. 8.45E15 molecule/cc oxygen 0 2 4 6 8 10 -2.00E+010 0.00E+000 2.00E+010 4.00E+010 6.00E+010 8.00E+010 1.00E+011 1.20E+011 1.40E+011 1.60E+011 1.80E+011 E A CH3CHOO
  • 17. 8.45E15 molecule/cc oxygen 0 2 4 6 8 10 6.80E+015 7.00E+015 7.20E+015 7.40E+015 7.60E+015 7.80E+015 8.00E+015 8.20E+015 8.40E+015 8.60E+015 G A O2
  • 18. 0.00E+000 2.00E+015 4.00E+015 6.00E+015 8.00E+015 1.00E+016 0.0 0.2 0.4 0.6 0.8 1.0 Simulation Exp 11/04/2016 Oxygen (molecule/cc) [Vinoxy]/[Vinoxy]0 0.5 0.6 0.7 0.8 0.9 1.0 1.1 1.2 [Vinoxy]/[Vinoxy]0 Comparison experiment vs simulation
  • 19. • Vinoxy concentration from modelling much higher:  Yield of vinoxy in model is overestimated  Not enough vinoxy depletion channels, or rates underestimated • Vinoxy depletion by oxygen much higher:  Vinoxy + Oxygen rates overestimated  High vinoxy concentration in modelling driving reaction  Not enough oxygen depletion channels, or rates underestimated
  • 20. + O3 CH2CO CH3OH SOZ ++H2O P P P P P + + P + 2O2 P SOZ P OH OH + CO OH O2 H2OO3 OH wall decomp wall CH2OH CH3O H2O OH O2 + HO2 OHOH HO2 + O2 P 0.5 OH + P trans-2-butene ozonolysis mechanism used in KINTECUS (11/06/2016) 2 +H2O+H2C2 1.00 0.1 0.5 0.05 0.07 0.950.05 0.85 0.15 1.1E-12 2.6E-14 3.6E-15 1.7E-16 7.5E-13 1.9E-16 6.4E-11 1.6E-12 4E-18 370 s-1 1E-15 1E-12 6.12E-15 1.84E-14 3.67E-14 1E-11 9.1E-12 1E-11 10 s-1 10 s-1 1E-11 HCHO + OH HCO + H2O 7.5E-13
  • 21. 0 2 4 6 8 10 0.00E+000 2.00E+010 4.00E+010 6.00E+010 8.00E+010 1.00E+011 1.20E+011 E A CH3CHOO Revisiting Criegee Intermediates
  • 26. 0 2 4 6 8 10 -1.00E+011 0.00E+000 1.00E+011 2.00E+011 3.00E+011 4.00E+011 5.00E+011 6.00E+011 7.00E+011 G A CH3CO2CH3 Parallel
  • 28. Summary Mechanism for t2b need more work! Time to revisit measurement of CIs