Topics Covered
Introduction
Experimental Design
Results
Conclusion
References
An automated head space auto sampler is
typically applied to analyse a raw sample or segment of finished material for
the presence of volatile compounds. With little or no sample preparation
involved using the auto sampler, high-quality control testing is possible for
material in the manufacturing industry.
The Bruker SCION SQ single quadrupole
mass spectrometer is a synchronomous SIM/Scan mode, which allows
for quantitative data reflecting the content of non-target compounds from a
given sample.
Introduction
Industrial handling of chemicals and gases
means that the application of sampling methods for the detection of volatile
organic chemicals is fundamental for the health and safety of consumers, and
particularly important where materials such as plastic are being applied in
manufacturing techniques that expose this type of material to extreme
temperatures in limited or no ventilated areas (for example, the application of
certain types of plastic in automobiles that are prone to high temperatures due
to sun exposure from the environment).
Volatile organic chemicals are typically
used for the manufacturing of interior furnishings, such as as carpets, and
polyvinyl chloride (PVC) in piping material, both of which are commonly used in
houses that, if not well ventialted, may force volatile organic chemicals to
build up to toxic levels in a confined living space posing a heath risk.
Chlorinated solvents, such as dichloromethan,
trichloroethane, trichloroethane, and tetrachloroethene have an integral
role in industrial and commercial industries. With chlorinated compounds having
a relatively low boiling point, they are economical and have properties
that make them useful for degreasing fats, oils, waxes, and resins. They are
used widely and have been manufactured in large quantities.
Chlorinated solvents
are considered to be carcinogenic and are released as a bi-product of industrial
practices and are highly hazardrous to the envirmonment. Other compounds
detected may be uncharacterized with little known about their toxicity. Certain
chlorinated compounds have been associated with human toxicity such as phthalate
esters, which have been linked to endocrine disruption in certain animal
species; however, regulations are emerging to enforce better control of using
such toxic substances for the manufacturing of plastic
bottles.1
Experimental Design
This study involved samples of
polypropylene from a car manufacturer and PVC pipe that were then cut into small
pieces and placed directly into 20mL head space vials. About 500mg-1g was added.
The Bruker SHS-40 Auto sampler conditions used are cited in Table 1.
Table 1.
SHS-40 Sampling Conditions.
| Parameter
|
SetPoint |
| Oven Temp
|
70°C |
| Valve/Loop Temp |
160°C |
| Transfer
lineTemp |
125°C |
| Pressure |
500psi |
| Loop Volume
|
1mL |
| PC (incubation) Time |
30 min. |
| GC/MS Run
Time |
20 min.
|
| Shake option |
ON |
.jpg)
Figure 1.
Bruker SHS-40 Headspace Autosampler (left) with SCION
GC/MS.
The SCION GC/MS
column, oven program, and injector conditions:
| Column
|
BR-624ms, 20M x 0.18mm x 1.0um |
| Injector
|
BR-1079, PTV injector with 3.4mm single
goose-neck open split liner set at 200°C |
| Injector
split ratio |
1:20 |
| Column flow
|
1 mL/min |
| Oven
program |
Initial 35°C hold 2min; program to170°C at
10°C/min; hold 0; program to 250°C at 50°C/min, hold 1 min,
(totalruntime17.9min.) |
Results
A full scan of the polypropylene dash board sample
was analysed in this experimental study. Figure 2 illustrates all compounds
that were tentatively identified using an automated library search against the
NIST 08 library.
.jpg)
Figure 2.
Full Scan Identification of Compounds in Polypropylene
Sample.
Table 2. List of compounds detected in polypropylene dashboard sample.
| RT(min)
|
Peak
Name |
Result
Type |
Amt
|
Match
|
Result
|
Library
|
| 2.581 |
Pentane,
2-Methyl- |
TIC |
450552256
|
1 |
933 |
NIST |
| 3.066 |
Hexane |
TIC |
43213484 |
1 |
903 |
NIST |
| 6.216 |
1-Butanol,
2-Ethyl- |
TIC |
10450404
|
1 |
877 |
NIST |
| 6.766 |
Toluene |
TIC |
10159705 |
1 |
901 |
NIST |
| 7.333 |
Hexane,
2,3,5-Trimethyl- |
TIC |
139044608
|
1 |
925 |
NIST |
| 7.455 |
Hexane, 2,3,4-Trimethyl- |
TIC |
1922249344 |
1 |
922 |
NIST |
| 7.919 |
2,
4-Dimethyl-1-Heptene |
TIC |
16034614
|
1 |
858 |
NIST |
| 8.16 |
Nonane, 4-Ethyl-5-Methyl- |
TIC |
48203884 |
1 |
909 |
NIST |
| 8.279 |
Hexane,
3-Ethyl- |
TIC |
418871424
|
1 |
921 |
NIST
|
| 11.732 |
1-Nonene, 4,6,8-Trimethyl- |
TIC |
85041800 |
1 |
876 |
NIST |
| 11.821 |
1-Undecene,
4-Methyl- |
TIC |
1740321664
|
1 |
884 |
NIST |
| 11.921 |
Undecane, 4,7-Dimethyl- |
TIC |
208282336 |
1 |
883 |
NIST |
| 12.482 |
Octane,
2,3,6,7-Tetramethyl- |
TIC |
48176440
|
1 |
878 |
NIST |
| 12.565 |
Hexane, 2,3,4-Trimethyl- |
TIC |
417671808 |
1 |
877 |
NIST |
| 12.657 |
Hexane,
2,3,4-Trimethyl- |
TIC |
92484168
|
1 |
889 |
NIST |
| 12.775 |
Undecane, 4-Methyl- |
TIC |
21904856 |
1 |
870 |
NIST |
| 13.634 |
6-Methyl-2-Pyrazinylmethanol
|
TIC |
15546811
|
1 |
766 |
NIST |
| 14.128 |
OxalicAcid, Isobutyl Nony lEster |
TIC |
11080139 |
1 |
885 |
NIST |
| 15.271 |
1-Lodo-2-Methylundecane
|
TIC |
40731856
|
1 |
882 |
NIST |
| 15.321 |
Heptadecane, 2,6,10,14-Tetramethyl- |
TIC |
638716608 |
1 |
911 |
NIST |
Table 3.
Synchronous SIM/SCAN parameters.
| Compound
Name |
RetentionTime
(RT) |
RT Window
|
Scan Mode,
Ionsmonitored |
Dwell Time
(ms) |
| Vinyl
Chloride |
3.10 |
1.0 |
SIM, 62, 64
|
49 |
| 1,2-Dichloroethane |
4.67 |
1.0 |
SIM, 62, 64 |
49 |
| Full Scan
|
NA |
2.0-17.9
|
Full (m/z
35-300) |
300
|
Table 4. Tentatively Identified compounds in PVC
sample.
| RT (min)
|
Peak Name
|
Result
Type |
Area |
Amt |
Match
|
Result
|
Library |
| 1.184 |
1-Methyldodecylamine
|
TIC |
6.79E+07
|
67918424
|
1 |
735 |
NIST |
| 1.283 |
Hydrazinecarboxamide |
TIC |
6.61E+06 |
6613686 |
1 |
762 |
NIST |
| 1.389 |
Ethyne,
Fluoro- |
TIC |
546473 |
546473 |
1 |
665 |
NIST |
| 2.159 |
Acetone |
TIC |
4.23E+06 |
4234303 |
1 |
867 |
NIST |
| 3.116 |
Thiirane
|
TIC |
4.68E+08
|
4.68E+08
|
1 |
907 |
NIST |
| 3.583 |
Butane, 2-Nitro- |
TIC |
1.32E+07 |
13169822 |
1 |
760 |
NIST |
| 5.659 |
Pentanal
|
TIC |
5.34E+06
|
5341163 |
1 |
796 |
NIST |
| 5.705 |
2-Propenoic, Acid, 2-Methyl-, Methyl Este
|
TIC |
5.40E+06 |
5398963 |
1 |
806 |
NIST |
| 5.807 |
Acetaldehyde
|
TIC |
5.83E+06
|
5825911 |
1 |
830 |
NIST |
| 7.752 |
Hexanal |
TIC |
2.89E+07 |
28887902 |
1 |
886 |
NIST |
| 9.732 |
Heptanal
|
TIC |
6.03E+06
|
6025094 |
1 |
867 |
NIST |
| 9.848 |
Benzene, (1-Methylethyl)- |
TIC |
6.89E+06 |
6891179 |
1 |
853 |
NIST |
| 10.159 |
2,2,7,7-Tetramethyloctane
|
TIC |
2.41E+07
|
24139264
|
1 |
872 |
NIST |
| 10.348 |
1-Butanol, 3,3-Dimethyl- |
TIC |
5.30E+06 |
5302461 |
1 |
747 |
NIST |
| 10.421 |
2,2,7,7-Tetramethyloctane
|
TIC |
1.39E+07
|
13884072
|
1 |
846 |
NIST |
| 10.516 |
Heneicosane, 11-(2,2-Dimethylpropyl)- |
TIC |
8.77E+06 |
8773806 |
1 |
824 |
NIST |
| 10.657 |
Hexanal,
2-Ethyl- |
TIC |
5.78E+06
|
5782036 |
1 |
776 |
NIST |
| 10.763 |
Tetradecane, 1-Iodo- |
TIC |
1.00E+07 |
9995009 |
1 |
793 |
NIST |
| 10.787 |
Pentane,
2,3,4-Trimethyl- |
TIC |
5.01E+06
|
5005334 |
1 |
764 |
NIST |
| 10.885 |
Pentanoic Acid, 1,1-DimethylpropylEster |
TIC |
3.35E+06 |
3354330 |
1 |
733 |
NIST |
| 11.25 |
Heneicosane,
11-(2,2-Dimethylpropyl)- |
TIC |
2.04E+07
|
20381632
|
1 |
890 |
NIST |
| 11.409 |
Pentane, 3-Ethyl-2,2-Dimethyl- |
TIC |
8.05E+06 |
8048495 |
1 |
896 |
NIST |
| 11.543 |
Octane,
2,4,6-Rrimethyl- |
TIC |
4.56E+07
|
45579500
|
1 |
867 |
NIST |
| 11.802 |
Oxalic Acid, Isobutyl Nonyl Ester |
TIC |
6.71E+06 |
6708442 |
1 |
850 |
NIST |
| 11.88 |
Pentane,
3-Ethyl-2,2-Dimethyl- |
TIC |
2.68E+07
|
26790618
|
1 |
886 |
NIST |
| 11.919 |
Heneicosane, 11-(2,2-Dimethylpropyl)- |
TIC |
2.79E+06 |
2789403 |
1 |
795 |
NIST |
| 11.983 |
Oxalic Acid,
Isobutyl Octyl Ester |
TIC |
2.44E+07
|
24356798
|
1 |
886 |
NIST |
| 12.224 |
Hexane, 2,4-Dimethyl- |
TIC |
2.94E+07 |
29438408 |
1 |
817 |
NIST |
| 12.554 |
Hexane,
1,1-Dichloro-3-Methyl- |
TIC |
8.90E+06
|
8901146 |
1 |
656 |
NIST |
| 13.033 |
Ethanone, 2,2-Dihydroxy-1-Phenyl- |
TIC |
1.32E+07 |
13228981 |
1 |
879 |
NIST |
| 13.282 |
Nonanal |
TIC |
2.19E+07
|
21900612
|
1 |
865 |
NIST |
| 13.367 |
Benzenemethanol, .Alpha., .Alpha.-Dimethy |
TIC |
8.96E+06 |
8960782 |
1 |
727 |
NIST |
| 13.63 |
6-Methyl-2-Pyrazinylmethanol
|
TIC |
9.97E+06
|
9966499 |
1 |
741 |
NIST |
| 14.874 |
2-Decen-1-Ol |
TIC |
1.31E+07 |
13070243 |
1 |
888 |
NIST |
The PVC
sample was run in SIM/Scan mode. Figure 3 shows detection of 1,2-dichloroethane,
a target compound with qualifier ion.
.jpg)
Figure 3.
SIM/Scan analysis of PVC sample.
.jpg)
Figure 4. RIC of PVC sample.
The compounds were tentatively identified
and are listed in Table 3. Lower display is magnification of peaks eluting
between 10 and 14 min.
Conclusion
The findings demonstrate that the Bruker SHS-40 headspace coupled
with the SCION GC/MS is
an excellent tool for qualitiative and quantitative identification of volatile
compounds in raw materials. Using SIM, compounds can be selectively quantitated
at very low concentrations. Full scan data can be interrogated for TICs and used
for quality control “fingerprints”.
This information has been sourced and adapated from Information
provided by Bruker CAM.
For more information please contact Bruker CAM
References
1. Developmental Effects of Endocrine-disrupting Chemicals in
Wildlife and Humans; T. Colborn, F. S. vom Saal, and A. M. Soto, W. Alton Jones
Foundation, Washington, DC 20037.