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April 24 - 27, 2007

The Effect of Temperature on the Uptake Rates of a New PDMS-Based Permeation Passive Sampler for VOCs in Air. Suresh Seethapathy, Tadeusz Górecki. Department of Chemistry, University of Waterloo, Waterloo, ON, Canada. Monika Partyka, Bożena Zabiegała, Jacek Namieśnik.

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April 24 - 27, 2007

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  1. The Effect of Temperature on the Uptake Rates of a New PDMS-Based Permeation Passive Sampler for VOCs in Air Suresh Seethapathy, Tadeusz Górecki Department of Chemistry, University of Waterloo, Waterloo, ON, Canada. Monika Partyka, Bożena Zabiegała, Jacek Namieśnik Department of Analytical Chemistry, Gdańsk University of Technology, Gdańsk, Poland 7th Passive Sampling Workshop and Symposium Virginia, United States April 24 - 27, 2007

  2. Sample environment Diffusion barrier Sorbent Concentration Distance Concentration Profiles for the Two Types of Passive Samplers Diffusion samplers Permeation samplers Membrane thickness Sample environment Sorbent Concentration Distance

  3. Comparison of Diffusion and Permeation Passive Samplers Permeation passive sampling – permeation through a membrane Diffusive passive sampling – diffusion through air • Diffusion samplers • sampling rate can be estimated based on the properties of the analyte • sensitive to moisture, air currents, temperature variations • Permeation samplers • effective moisture elimination, much less sensitive to air currents and temperature changes • must be calibrated for each analyte

  4. Cma Cms Co PDMS membrane sorbent Calibration Constant / Uptake rate M = Amount of analyte collected by sorbent D = Diffusion coefficient A = Area of membrane Cma = Concentration of the analyte on the membrane surface in contact with air Cms = Concentration of the analyte on the membrane surface in contact with the sorbent t = Time of sampling Lm = Membrane thickness Concentration

  5. Theory M = Amount of analyte collected by sorbent D = Diffusion coefficient A = Area of membrane Cma = Concentration of the analyte on the membrane surface in contact with air. Cms = Concentration of the analyte on the membrane surface in contact with the sorbent t = Time of sampling Lm = Membrane thickness K = Partition coefficient of the analyte between air and the membrane P = Permeability constant of the polymer towards the analyte Co= Concentration of the analyte in air k = Calibration Constant (time/volume) k-1 = Uptake rate (volume/time)

  6. Properties of PDMS • Individual segmental motions even at –127 OC !!! • Nearly constant diffusion coefficient for most VOCs • Relative permeabilities are primarily decided by partition coefficients • Temperature effects on permeability • increase in temperature results in • - decreased partition coefficient • - increased diffusivity P = Đ K

  7. Energy of Activation of permeation Heat of solution Energy of activation of diffusion For PDMS, towards most volatile organic compounds ΔHs < 0 Ed > 0

  8. Effect of Temperature on the Calibration Constant slope

  9. Passive Sampler Design Area of PDMS membrane exposed: 38 mm2 Al cap PDMS membrane 1.8 mL crimp top vial Turned upside down before use Disposable 1.8 mL crimp-top vial based permeation passive sampler

  10. Sampler Preparation Cutting tool PDMS membrane Aluminum crimp cap vial Teflon lined septum cut membrane sorbent 1. Remove septum from crimp cap 2. Cut PDMS membrane 3. Add sorbent to the vial 6. Attach support/turn upside down for sampling 4. Assemble membrane and cap 5. Crimp to seal

  11. Analyte extraction/analysis 9. Introduce into GC auto sampler – either directly or after transferring the extract into a different vial 8. Crimp with aluminum crimp cap/teflon lined septum and shake 7. De-crimp cap, add desorption solvent

  12. Design of a Reusable Passive Sampler Area of PDMS membrane exposed: 38 mm2 Reusable, 1.8 mL crimp-top vial-based permeation passive sampler Aluminum crimp cap Mouth portion of a crimp top vial PDMS membrane Mouth portion of a screw top vial Plastic screw cap

  13. Experimental Setup Flow controller High pressure N2 source Air Purifier Standard gas mixture generator Vent Flow controller and monitor Activated carbon sampling tube Thermostated exposure chamber Suction Pump stirrer Laboratory made permeation tubea Brass ferrule PTFE tube Neat liquid PTFE Plug aProf. Jacek Namieśnik, Technical University of Gdańsk, Private communication.

  14. Effect of Temperature on the Calibration Constant • Experiments were conducted over a temperature range of 285 to 312.5 K • Model compounds included n-nonane, n-decane, ethyl acetate, propyl acetate, methyl butyrate, sec-butyl acetate, ethyl butyrate, butyl acetate, propyl butyrate, butyl butyrate. • n-nonane and n-decane used as references. • Experiments started with esters as they have polarity between that of highly polar alcohols and highly non-polar alkanes and aromatic hydrocarbons.

  15. Temperature – Calibration constant relationship for esters

  16. Temperature – Calibration constant relationship for esters - average variation for moderately polar esters - 1.4% per oK

  17. Temperature – Calibration constant relationship for n-alkanes - non-polar n-nonane and n-decane - 0.9% per oK

  18. Energy of Activation of Permeation

  19. Conclusions • A simple, cost effective passive sampler and sampling procedure have been devised to quantify VOCs in air. • Temperature effects on calibration constant have been studied for esters, n-nonane and n-decane. • Fundamental transport properties like energy of activation of permeation can be determined using the data. • Temperature effects are usually negligible in indoor air environments.

  20. Acknowledgments • Natural Sciences and Engineering Research Council (NSERC Canada). • University Consortium for Field-focused Groundwater Contamination Research. • Workplace Safety and Insurance Board of Ontario (WSIB)

  21. Questions?

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