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Determination of BTEX Compounds in Ambient Air Using Solid Phase Microextraction Gas ChromatographyM

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Title: Determination of BTEX Compounds in Ambient Air Using Solid Phase Microextraction Gas ChromatographyM


1
Determination of BTEX Compounds in Ambient Air
Using Solid Phase Microextraction Gas
Chromatography-Mass Spectrometry
Christopher L. Marcum1 Bert C. Lynn2
  • Department of Chemistry, Eastern Kentucky
    University, Richmond, KY
  • Department of Chemistry, University of Kentucky,
    Lexington KY

Conclusions
Introduction
Results and Discussion
  • Air quality is of paramount importance. Exposure
    to air which contains contaminants can lead to
    major health problems including nervous system
    damage.
  • Recently, solid phase microextraction (SPME) has
    been offered as an alternative to traditional air
    sampling techniques for determination of air
    contaminants.
  • The purpose of our study is to develop a
    technique for the determination of BTEX compounds
    (benzene, toluene, ethylbenzene, xylenes) in
    ambient indoor air using SPME, coupled with gas
    chromatography/mass spectrometry (GC/MS).
  • Evidence also shows a possible link between these
    BTEX contaminants and electronic equipment, such
    as laser printers and copiers.
  • SPME proved to be a very simple technique for air
    sampling and, when coupled with GC/MS, was very
    sensitive and selective for volatile organic
    compounds, including BTEX compounds.
  • Although concentrations were not determined, the
    chemistry copy room, chemistry office, and
    intellectual property office had the highest
    levels of contamination from BTEX compounds.
  • We found no observable link between either the
    presence or the use of a laser printer and an
    increase in BTEX compounds in the air.
  • We also were unable to link the presence of a
    copy machine to an increase in BTEX contamination.

Future Work
Experimental Methods
  • Air sampling was accomplished through the use of
    a carboxen/PDMS SPME fiber placed in a manual
    holder. Before sampling, each fiber was
    conditioned for 2 hours in a hot GC injection
    port.

The chromatogram (top) is from a SPME fiber
exposed for 6 hours in the chemistry department
copy room. The peaks labeled A-D were identified
as the BTEX compounds shown above. Chromatograms
were obtained from each location and the peak
areas were examined in order to compare the
locations.
  • Analysis of other locations, including other
    campus buildings and perhaps some off-campus
    locations
  • Use of other traditional air sampling techniques
    to verify SPME results
  • Determine the concentration of BTEX compounds in
    each sample location
  • Testing of other possible sources of BTEX
    contamination using glove bag techniques

1 Chemistry Copy Room 2 Chemistry Office 3
Intellectual Property Office 4 ASTeCC Copy
Room 5 ASTeCC Conference Room 6 Outside
ASTeCC
  • Several locations were sampled across the campus
    of the University of Kentucky, Lexington, KY
  • Chemistry Department Copy Room, Chemistry Physics
  • Building
  • Chemistry Department Office, Chemistry-Physics
  • Building
  • Intellectual Property Office, Advanced Science
    and
  • Technology Commercialization Center (ASTeCC)
  • Building
  • Copy/Fax Room, ASTeCC Building
  • Conference Room, ASTeCC Building
  • Outside the ASTeCC Building

Acknowledgements
  • The peak areas for BTEX compounds were much
    greater in the chemistry copy room, chemistry
    office and intellectual property office.
  • We are grateful to the Department of Chemistry,
    University of Kentucky REU program, funded by NSF
    and the Air Force ASSURE program for support of
    this work.
  • Fibers were transported to and from sample
    locations in clean glass tubes. Each sample
    fiber had an associated trip blank, which was not
    exposed to the air.
  • Immediately following sampling, analysis of the
    fibers was carried out via a Varian 3400 4D GC/MS
    equipped with electron ionization and an ion trap
    mass analyzer.
  • The effects of a laser printer on air quality
    were determined by enclosing a laser printer in a
    nitrogen filled glove bag and sampling the air in
    the bag while the printer was in several
    configurations off, on without toner, and while
    printing.

1 Nitrogen Only 2 Printer Off 3 Printer
On 4 Printer Printing
  • We would also like to thank the University of
    Kentucky Mass Spectrometry Facility and Michael
    Timmons for their assistance with this project. 
  • Peak areas for BTEX compounds did not increase
    within an enclosed glove bag when a laser printer
    was introduced, turned on, or printing.
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