Use of Heated Headspace and GC/MS to Analyze Finished Plastic Products

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

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.

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.

Figure 3. SIM/Scan analysis of PVC sample.

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.

Date Added: Jun 15, 2012 | Updated: Jun 16, 2012
Ask A Question

Do you have a question you'd like to ask regarding this article?

Leave your feedback
Submit