22CYL23 & Chemistry Laboratory for Chemical Engineering (Chemical-B-Alkalinit...
Defense Presentation 2014 October 14 New
1. A m a n d a J a m e e r
S u p e r v i s o r : D r . D o n a l d R . H a s t i e
O c t o b e r 3 1 , 2 0 1 4
Evaluating the Utility of an Atmospheric
Pressure Chemical Ionization Mass
Spectrometer (APCI-MS/MS) at Detecting
Organic Peroxides
1
2. Presentation Outline
2
Project goals
What are organic peroxides?
Formation in the atmosphere
Importance of organic peroxides
Previous and current detection methods
Experimental set-up
Results
Future work
3. Project Goals
To evaluate the ability of a positive-ion atmospheric pressure chemical
ionization mass spectrometer ((+) APCI-MS) to detect organic peroxide
formation during β-pinene ozonolysis experiments
How do organic peroxides behave in the APCI-MS/MS?
What APCI-MS/MS analysis mode will be useful for organic peroxide
detection?
Based on common features from mass spectra, can a “fingerprint” analysis
be developed for future applications?
3
4. What are Organic Peroxides?
Compounds containing at least two oxygen atoms linked together
Where:
R1 = H atom or organic substituent
R = organic substituent
4
Hydroperoxide Peroxy acid
Peroxy ester Peroxy hemiacetal
Dialkyl peroxide
R
O
OH O
OH
R
1
O
R
1
OH
O
O
R
O
O
R
1
O
R
R
O
O
R
5. Formation in the Atmosphere – HO Radicals
Generally formed through hydroxyl (HO) -initiated reactions
RH + HO· → R· + H2O
R· + O2 + M → ROO· + M
ROO· + HOO· → ROOH + O2
5
ROO· + NO· → RO· + NO2
ROO· + NO· → RONO2
ROO· + NO2
· → ROONO2
6. Formation in the Atmosphere – Ozone (O3)
O3-initiated reactions with unsaturated hydrocarbons
6
R1R2
R3R4
O
O
+
O
-
R 2
R4
O
O
O
R1
R3
O
R3
R4
+ C
O
O
R1
R 2
O
R1
R2
+ C
O
O
R3
R4
a
b
c
Primary
Ozonide
Criegee
Intermediate
Criegee
Intermediate
R
2
C
O
O
R
1
R
4
C
O
O
R
3Primary
Ozonide
Criegee Biradical
Criegee Biradical
8. Importance of Organic Peroxides
8
Play an important role in the chemistry of the troposphere
Organic peroxides are potential products from volatile organic compound
oxidation with hydroxyl (HO) radicals or ozone (O3)
Organic peroxides are reservoirs for radicals
These radicals help determine the lifetime of both natural and anthropogenic
hydrocarbons in the atmosphere
May contribute to secondary organic aerosol (SOA) formation
9. Contribution to SOA
Compounds with sufficiently low vapour pressure to be present in the particle
phase
Organic peroxides are major components of SOA formed from alkene
ozonolysis
Docherty et al., (2005) estimated that organic peroxides contributed ~ 47% and
~85% of SOA mass formed during α- and β-pinene oxidation experiments
respectively
9
10. Previous Detection Methods
Colorimetric method for detecting hydrogen peroxide (H2O2)
Chemiluminescent method for detecting and quantifying H2O2
High performance liquid chromatography – Fluorescence method for detecting
and quantifying H2O2 and organic peroxides
Tunable diode laser adsorption spectroscopy for detecting and quantifying
H2O2
10
11. Mass Spectrometry
Can provide information about the molecular weight of a species
Depending on the instrument set-up, can provide structural information of a
species
On-line analysis
Does not requires sample pre-treatment
Require samples to be ionized before analysis
11
12. Detecting Organic Peroxides by Mass
Spectrometry
Chemical ionization mass spectrometry (CIMS) analysis
Target neutral molecule is ionized through a series of collisions with a reagent
ion present in the ion source
“Softer” ionization technique where ions are produced with little excess energy
For example, Crounse et al., (2006) used CF3O- reagent ions to detect H2O2 and
peroxyacetic acid (PAA)
CF3O- + H2O2 CF3O-H2O2
CF3O- + PAA CF3O-PAA
12
13. Detecting Organic Peroxides by Mass
Spectrometry
Baker et al., (2001) and Reining et al., (2009) used (H2O)H+ reagent ions to
detect organic peroxide formation from linear alkene and monoterpene
ozonolysis
M + (H2O)nH+ [M + H]+ + (H2O)n
Organic peroxides containing a –OOH functional group were identified based
on a mass loss of 34 u (H2O2) from the [M + H] ion while performing tandem
mass spectrometry (MS/MS)
13
14. APCI-MS/MS
Chemical ionization at atmospheric pressure conditions
q0 Q1 Q3q2
Triple quadrupole mass
spectrometer
Ion source
Purified air flow
Ionization reagent
(H2O)nH+
(CH3OH)nH+
Detector
14
Mass spectrum
33 43 55
m/z
15. Ion-Molecule Reactions in the Ion Source
Most common ion-molecule reaction is proton transfer
Occurs if the proton affinity of M is greater than the proton affinity of R
If the proton affinity between M and RH+ are similar…
Adduct formation
M + RH+ [M + H]+ + R
M + RH+ [M + RH]+
15
17. A N A L Y S I S O F C O M M E R C I A L L Y A V A I L A B L E
O R G A N I C P E R O X I D E S T A N D A R D S
H o w d o o r g a n i c p e r o x i d e s b e h a v e i n t h e A P C I -
M S / M S ?
W h a t A P C I - M S / M S a n a l y s i s m o d e w i l l b e u s e f u l f o r
o r g a n i c p e r o x i d e d e t e c t i o n ?
Phase 1 of Project
17
18. Experimental Design for Standard Analysis
Commercially available organic peroxides were analyzed neat or by preparing a
10% v/v solution in either water or methanol
M + (H2O)nH+ [M + H]+ + (H2O)n
[M + H2O + H]+
M + (CH3OH)nH+ [M + H]+ + (CH3OH)n
[M + CH3OH + H]+
Purified air flow
To dilu on flask
Syringe pump
To ion source M + 1
M + 19
M + 1
M + 33
18
19. Organic Peroxide Standard Selection
CH3
CH3
CH3
O
OH
CH3
CH3
CH3
O
O
CH3
CH3
CH3
CH3CH3
O
OH
CH3
O
O
OH
CH3
CH3
CH3
O
O
O
CH3
tert-butyl
hydroperoxide
di-tert-butyl
hydroperoxide
tert-butyl
peroxyacetate
peracetic acid
cumene
hydroperoxide
19
20. Results for Full Scan Analysis Mode
Ionization with Protonated Water (H2O)H+
Mass spectra were dominated by fragment ion signals
[M + H]+ or [M + H2O + H]+ ion signals not found in appreciable amounts
100
80
60
40
20
0
RelativeAbundance(%)
30025020015010050
m/z
73
181
tert-butyl hydroperoxide tert-butyl peroxyacetate
100
80
60
40
20
0
RelativeAbundance(%)
30025020015010050
m/z
265
73
20
m/z 91 or 108
m/z 133 or 151
21. Results for Full Scan Analysis Mode
Ionization with Protonated Methanol (CH3OH)H+
Fragment ions were apparent in mass spectra
Four out of five standards displayed a [M + CH3OH + H]+ ion signal
120
80
40
0
RelativeAbundance(%)
25020015010050
m/z
73
65
123
181
100
80
60
40
20
0
RelativeAbundance(%)
25020015010050
m/z
73
265
165
tert-butyl hydroperoxide tert-butyl peroxyacetate
21
22. Results for Neutral-Loss Scan Analysis
Only three standards contained an –OOH functional group
tert-butyl hydroperoxide, peroxyacetic acid and cumene hydroperoxide
CH3
CH3
CH3
O
OH
CH3
CH3
CH3
O
O
CH3
CH3
CH3
CH3CH3
O
OH
CH3
O
O
OH
CH3
CH3
CH3
O
O
O
CH3
tert-butyl
hydroperoxide
di-tert-butyl
hydroperoxide
tert-butyl
peroxyacetate
peracetic acid
cumene
hydroperoxide
22
25. Water versus Methanol Results
Enthalpy of the Overall Gas-phase Protonation Reaction ( ΔH°reaction )
Compound PA (kJ/mol)
Water as Ionization
Reagent
Methanol as Ionization
Reagent
tert-butyl hydroperoxide 803 -107 -37
di-tert-butyl peroxide 790 -94 -24
cumene hydroperoxide >696
peracetic acid 783 -87 -17
peroxyacetate 791 -95 -25
25
M + (H2O)H+ [M + H]+ + H2O
M + (CH3OH)H+ [M + H]+ + CH3OH
ΔPA = PAionization reagent – PAstandard = - ΔH°reaction
26. Summary of Standard Analysis
How do organic peroxides behave in the APCI-MS/MS?
Organic peroxides fragment or decompose after the ionization process
Excess energy owing to the large ΔPA values, inducing fragmentation
Intact adduct ion only found when using methanol as an ionization reagent (i.e.
[M + CH3OH + H]+)
Less energy available to facilitate fragmentation since ΔPA values are small
26
27. Summary of Standard Analysis
What APCI-MS/MS analysis mode was useful for organic
peroxide detection?
Full scan analysis mode provided a qualitative overview of the ions produced in
the ion source
Nothing “selective” about this analysis mode
Neutral-loss scan analysis mode was useful at detecting ion signals that
represented a hydroperoxide or peroxy acid
A mass loss of 34 u was characteristic for organic peroxides containing a –OOH
functional group
27
28. S M O G C H A M B E R E X P E R I M E N T S
A p p l y k n o w l e d g e g a i n e d f r o m s t a n d a r d a n a l y s i s
A r e t h e r e a d d i t i o n a l c o m m o n m a s s l o s s c r i t e r i a t h a t
c a n b e u s e d t o s e l e c t i v e l y d e t e c t o r g a n i c p e r o x i d e s ?
Phase 2 of Project
28
29. Smog Chamber Experiments
Ozonolysis experiments using β-pinene as the precursor hydrocarbon
Naturally emitted hydrocarbon
Monoterpene with the formula C10H16
Is a significant source of SOA
29
32. Results for Ozonolysis Experiments
Ionization using Protonated Water
Full Scan Mass Spectrum
Odd number m/z values
Nothing selective about this analysis mode
m/z
32
33. Results for Ozonolysis Experiments
Ionization with Protonated Water
Neutral-loss Scan Mass Spectrum
m/z values that lost 34 u during collision events
Reduced complexity to a handful of m/z values
m/z
33
m/z values
171
173
187
201
203
34. Ionization with Protonated Methanol
34
Chemical ionization using protonated water caused excessive fragmentation
during standard analysis
Intact ions were observed during full scan analysis while using protonated
methanol as an ionization reagent
M + (CH3OH)H+ [M + CH3OH + H]+
M + 33
Can additional m/z values be observed in full scan mass
spectrum if protonated methanol is used as an ionization
reagent?
35. Results for Ozonolysis Experiments
35
Ionization with Protonated Methanol
Full scan mass spectrum
Odd number m/z values
Appears similar to previous full scan mass spectrum using protonated water
100
80
60
40
20
0
RelativeAbundance(%)
40035030025020015010050
m/z ratio, amu
139
155
185
293
201
187
203
171
m/z m/z
Ionization with protonated waterIonization with protonated methanol
36. Results for Ozonolysis Experiments
36
Ionization with Protonated Methanol
Neutral-loss mass spectrum
m/z value capable of losing 34 u
No additional m/z values observed
100
80
60
40
20
0
RelativeAbundance(%)
350300250200150100
m/z ratio, amu
187
171
173
203
m/z
Ionization with protonated methanol
m/z
Ionization with protonated water
37. Results for Ozonolysis Experiments
37
No new information was obtained by using protonated methanol as an
ionization reagent
Ozonolysis experiments continued using protonated water as an ionization
reagent
Can additional m/z values be observed in full scan mass
spectrum if protonated methanol is used as an ionization
reagent?
38. Product-Ion Scan Analysis
38
m/z values 171, 173, 187, 201, and 203 were investigated further using product-
ion scan analysis mode
Validate mass losses of 34 u and determine additional common mass losses
Propose plausible structures based on observed losses and ozonolysis
mechanism
39. Product-Ion Mass Spectrum for m/z 187
39
100
80
60
40
20
0
RelativeAbundance(%)
1801601401201008060
m/z ratio, amu
187
169153
125
155
109
m/z
Losses observed
18 u (H2O)
32 u (O2)
34 u (H2O2)
62 u (H2O2 and CO)
41. Investigating Losses of 62 u
41
Combined mass losses totaling 62 u
Loss of H2O2 and CO
Peroxy acids can explain these losses
O
OH
O
Cl
3-chloroperbenzoic acid
Hydroperoxide Peroxy acid
Peroxy ester Peroxy hemiacetal
Dialkyl peroxide
R
O
OH O
OH
R
1
O
R
1
OH
O
O
R
O
O
R
1
O
R
R
O
O
R
42. 3-chloroperbenzoic acid
42
[M + H]+ and [M + CH3OH + H]+ were apparent in full scan mass spectrum
Product-ion mass spectrum for m/z 173 showed major losses of 62 u
Possible for peroxy acids to exhibit this mass loss during collision events
m/z m/z
Full Scan Mass Spectrum
Product-ion Mass Spectrum for
m/z 173
44. Summary for Smog Chamber Experiments
44
Are there additional common mass loss criteria that can be
used to selectively detect organic peroxides?
Yes, product-ion mass spectra for organic peroxide candidates showed common
mass losses
Aside from mass losses of 34 u, mass losses of 32 and 62 u can be used to
selectively enhance the detection organic peroxides containing a –OOH functional
group
45. Project Summary
45
(+) APCI-MS/MS can be used to selectively detect organic peroxides
Required little to no sample treatment before analysis
Tandem mass spectrometry analysis was useful to for selectively detecting
organic peroxides
Neutral-loss analysis for 32, 34, and 62 u can be used as a criteria to observe
m/z values that were organic peroxide candidates
46. W h a t a r e t h e f u t u r e d i r e c t i o n s f o r t h i s p r o j e c t
k n o w i n g t h a t o r g a n i c p e r o x i d e s c a n b e s e l e c t i v e l y
d e t e c t e d b y t h e A P C I - M S / M S ?
46
Future Work
47. Future Work
47
Factors that influence organic peroxide formation
Additional experiments under high and low NOx (NO + NO2) conditions
Relative humidity experiments
Quantitative studies
Need standards that are representative of products formed in the smog chamber
48. Acknowledgements
48
Supervisor: Dr. Donald Hastie
Group members: Mehrnaz Sarrafzadeh and Zoya Dobrusin
Supervisory and exam committee members: Dr. R. McLaren, Dr. J. Rudolph, and
Dr. M. Gordon
CAC graduate students and postdocs
Carol Weldon from CAC
Greg Koyanagi from CRMS
IACPES
Charles Hantho and Harold Schiff Foundations
Editor's Notes
The overall aim of this project was determine if an APCI-MS/MS can used to detect organic peroxide formation during beta pinene ozonolysis experiments. Organic peroxides are important compounds in the atmosphere and it is of great interest to develop a method for their detection.
However, to address this project goal, it required us propose a few research questions. For example, how do organic peroxides behave in the APCI-MS/MS? Since there are a suite of analysis modes available for this instrument, are there analysis modes that would prove to be useful for organic peroxide detection? And lastly, can we develop a method to only selectively detect organic peroxides based on some kind of common “feature”?
Before we get into project details, its best to understand what these compounds are, how they are formed and why they are important to study. At the very least, these compounds contain two oxygen atoms linked together. However, there are different classes of organic peroxides depending on the rest of the structure. This figure shows examples of different types of organic peroxides. In this diagram, “R” represents and organic substituent for example a methyl or ethyl group while R1 can be either a hydrogen atom or organic substituent.
In the atmosphere, these compounds are primarily formed by the oxidation of hydrocarbons by hydroxyl radicals. Through a series of steps, the oxidation process produces a peroxy radical (RO2) which then reacts with a another peroxy radical to form an organic peroxide. However, organic peroxide formation by this mechanism is limited by the presence nitrogen oxides. Nitrogen oxides can result in the formation of an alkoxy radical, organic nitrate or a peroxy nitrate.
An alternative mechanism involves the oxidation of unsaturated hydrocarbon with ozone. The ozonolysis mechanisms starts off by ozone adding across the double bond to form a primary ozonide. This structure is highly unstable and decomposes to form a Criegee intermediate and a carbonyl. The name “Criegee” originated from the German organic chemist Rudolph Criegee who first postulated the mechanism. Two pathways are shown here because one of the two peroxy bonds are cleaved along with the C – C bond.
Criegee intermediate then reacts with water vapour to form the organic peroxide.
SOA is formed through the oxidation of VOC to form lower volatility products that essentially partitions into the condensed phase
It is speculated that organic peroxides might be a major component of SOA formed through ozonolysis. In fact Docherty and coworkers performed several laboratory measurements and found that the SOA produced during alpha and beta – pinene was composed of ~ 47% and ~ 85 % organic peroxides. Their laboratory results looked at total organic peroxide content and didn’t distinguish between different classes of organic peroxides. However, this group speculated that bulk organic peroxides were mostly organic hydroperoxides and peroxy hemiacetals
Given their role in SOA composition and formation…
Early methods were considered “offline” techniques where the sample is extracted and treated before analysi. Colorimetry and chemi was able to detect H2O2 while HPLC methods was able to do H2O2 and selected organic peroxides
TDLAS – on-line measurement, did not require any sample pre-treatment but was used to detect and quantify H2O2
Does not require sample pre-treatment like extraction and/or derivitization like the HPLC-Fluo methods
An array of methods for ionizing samples before analysis
Crounse work was looking at full scan mass spectra
Mention NL scans here
Ions produced in the ion source are mass selected inside the triple quadrupole mass spectrometer and counted by a detector. This produces a mass spectrum which we use to determine distribution of ions by mass.
There are numerous ion-molecule reactions that occur inside the ion source. Proton transfer is one of the most common reactions. Here, a target neutral molecule represented by “M” undergoes proton transfer upon colliding with a proton rich reagent ion represented here by RH. As long as the proton affinity of M is greater than R, than proton transfer will occur. In the advent that the PA are similar, you can have adduct formation.
The instrument I have is capable of analyzing ions in different modes. In full scan mode, ions are mass selected in Q1, allowed to be transmitted into q2 and Q3, and counted by a detector. If I am interested in a specific ion, I can set Q1 to mass select for the target ion, allow the ion to fragment inside q2 which serves as a collision cell, and all resulting fragment ions will be analyzed by Q3 and subsequently counted by the detector. Lastly, If I am only interested in ions that exhibit a specific neutral mass loss, for example 34, I can set Q1 and Q3 to scan with the exception that Q3 is off set by the neutral mass of interest. The instrument in this mode produces a mass spectrum containing the ions that lost 34 u inside the collision cell.
Start addressing the objectives outlined earlier
Say what “M” is…
These are the 5 organic peroxide standards used in this phase of the experiment. I tried to get standards that represented different classes of organic peroxides. For instance, TBHP and CHP both represented organic hydroperoxides, while peracetic acid represented peroxy acids, TBPA was a peroxy ester while dTBP was a dialkyl peroxide
Here are two examples of mass spectra acquired using protonated water as an ionization reagent. We noticed that mass spectra were dominated by fragment ions, in fact m/z value 73 was a common organic fragment ion seen for both TBHP, TBPA and dTBP. The dimer signal was apparent in these two mass spectra. However, we noticed that there were no M + H or adduct signals. For instance m/z 91 and 108 where not apparent in the mass spectrum for TBHP. The same thing for TBPA, no m/z 133 or 151. Although I’ve only shown two mass spectra, this was consistent for the remaining standards
However, when we used protonated methanol as an IR, we noticed that four out of five standards produced an adduct, that is a M+ CH3OH + H ion signal. No results for Cumene hydroperoxide were possible because the standard was not soluble in methanol.
In the NLS analysis mode, the APCI was set to only detect ion signals that lost 34 mass units during collision events. In all three mass spectrum, we observed the [M + H] ion signal for all three standards that contained a hydroperoxy functional group. The M+H ion signal is shown inside the red circle.
Performing the same experiment using protonated methanol as an ionization reagent also showed the [M + H] ion signal. This was interesting because only adduct ion signals were apparent in the full scan mass spectrum. It was clear that methanol as an ionization reagent was capable of forming intact ion signals during full scan analysis mode and [M + H] ions were apparent in NLS analysis mode.
We decided to look into why we were getting different results depending on the type of ionization reagent we used. We calculated the enthaply of the reaction by taking the PA difference between the ionization reagent and the standards. What we noticed was that the there was excess energy available to further fragment ions formed in the ion source when protonated water was used as an ionization reagent. However, the small delta PA obtained with methanol indicated that this ionization was more “soft” compared to water and did not not have excess energy to further fragment .
Based on putting something “known” into the system…you can not determine which ions are organic peroxides if you put an unknown air sample in the instrument.
Ozonolysis experiments were conducted using beta-pinene as the precursor hydrocarbon. This compound was selected was selected since it is known to be a significant source of SOA
In our 8 m3 smog chamber, Beta-pinene is injected into a stream of purified air and allowed to mix inside the chamber. After, Ozone is in injected into the chamber. The air inside the chamber is then sampled to analyze ozone concentrations using the ozone analyzer and oxidation products in the gas-phase are analyzed by the APCI-MS/MS
Oxidation products in the gas-phase were analyzed using the 3 different analysis modes discussed earlier on this presentation.
This is an example of a full scan mass spectrum of the oxidation products found in the gas-phase. Odd numbered m/z values were expected since all the oxidation products only contained carbon, hydrogen and oxygen. However, there is nothing selective about this analysis mode. We can not just look at this spectrum and single out m/z values that represent organic peroxides
However, when we set the instrument to look for m/z values that lose 34 mass units during collision events, we reduced the complexity found in the full scan mass spectrum to a handful of m/z values of particular interest. The neutral loss mass spectrum shown here indicates that there are 5 m/z values of interest that are potential organic peroxide candidates.
We decided to repeat the experiments again using protonated methanol as an ionization reagent. Surprisingly, the mass spectrum acquired does not look different when compared the full scan mass spectrum acquired using protonated water. We expected them to be different based on the observations during standard analysis, however this was not the case.
When we decided to look for m/z values that displayed losses of 34 mass units, the resultant neutral loss mass spectrum did not display additional m/z value as potential organic peroxide candidates. Although the sensitivity for certain m/z values were enhanced, the whole point of using methanol was to see if it could provide additional m/z values.
Since no new information was obtained using protonated methanol as an ionization reagent, We decided to continue ozonolysis experiment using protonated water as an ionization reagent.
After coming to this conclusion, we decided to look at the 5 m/z values that were apparent in NL mass spectrum for 34 mass unit losses. To confirm this mass loss we decided to do product-ion analysis on these 5 ions. That is, we fragment these ions in the collision cell and observe what fragmented ions are produced. The purpose of this was to determine additional common mass losses along with proposing plausible structures for these ions.
Here is an example of a product-ion mass spectrum for m/z value 187. To acquire this mass spectrum, m/z value 187 was mass selected and allowed to fragment inside the collision cell. The spectrum we see here shows all the fragment ions produced after collision. The m/z values that are labelled show neutral losses. For example m/z value 169 and 153 are apparent in this scan because the m/z 187 ion lost 18 or 34 mass units. What was interesting doing the same analysis for the other 4 m/z values was that they produced a mass spectrum showing the same types of losses seen here.
This is a summary of the mass losses observed during product-ion scan analysis. Losses of 18 mass units were not considered unique since its possible to observe these losses for any compound containing an alcohol or carboxylic acid functional group. Mass losses of 32 u was interesting and was first experienced while analyzing cumene hydroperoxide during standard analysis. This was believed be a loss of O2. But the most interesting and unexpected loss was a mass loss of 62 u. This has never been seen by our group member and has not been found in mass spec literature. This was was investigated further.
Upon studying the product-ion scans for all 5 m/z values, we realized that losses of 62 u can be explained by a loss of H2O2 and CO. When we review the different classes of organic peroxides, we realized that peroxy acids can theoretically exhibit this type of loss. However, confirming this loss requires analyzing peroxy acid standards. There are not a lot of standards available but we did find one standard, 3-chloroperbenzoic acid. This standards was prepared in a similar manner to the organic peroxides standards during phase 1, except a standard was only made in methanol.
The M+H ion signal was apparent in the full scan mass spectrum as shown by m/z value 173 and the adduct ion signal at m/z 205. The PI mass spectrum for m/z 173 showed that losses of 62 u is possible shown by the presence of m/z 111, for peroxy acids. Keep in mind that no other standards were available to continue to test this notion.
Based on the PI scans, work by previous and current group members, 6 structures were proposed. Structures with MW 186 has been seen by our group members Mehrnaz and Janeen. An organic peroxide structure with MW 200 has only been described by one paper (Reinning). Two structures for MW 172 were proposed since the PI scan could not be explained by a single structure. The remaining structures have been reported by Docherty, Heaton and Reinnig.
Now that we have a method for selectively detection organic peroxides, now we can do additional experiments such as look at the factors that influence organic peroxide formation. This can include looking at Organic peroxide formation under high or low Nox environments or at different levels of RH
Quantiative experiments would be great to determine the amount of organic peroxides produced in the chamber. However, this continues to be problematic due to the availability of standards.