National Institute for Occupational Safety and Health

Summary

National Institute for Occupational Safety and Health NIOSH Manual of Analytical Methods… (1994)

Convert gas volumes to masses, correcting for compressibility and water vapor (see APPENDIX B) , and prepare DE calibration graph of peak area or height vs. μg/mL 1,3-butadiene. d. Read the concentrations, μg/mL, in media standards and blanks from DE calibration graph and multiply by the desorption volume to calculate the masses recovered. e. Prepare a graph of DE vs. μg taken. DE = (mass found – blank mass) / (mass taken) . 12.
Analyze three quality control blind spikes to insure that calibration graph (step 10) is in control.
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National Institute for Occupational Safety and Health NIOSH Manual of Analytical Methods… (1994)

When exposed to 0.7 and 2.5 mL of pure 1,3-butadiene gas followed by 80% RH air, breakthrough occurred after 35 L and 28.5 L, respectively. The corresponding respective timeweighted average concentrations were 20 and 88 ppm. For the analysis of media standards at levels of 1.1, 4.4, 18, 125, and 480 μg per sample, the pooled was 0.025, and the desorption efficiencies were 67%, 68%, 75%, 102%, and 97%, respectively. Adding water to media standards just after spiking or during desorption had no significant effect on desorption efficiencies.
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National Institute for Occupational Safety and Health NIOSH Manual of Analytical Methods… (1994)

Subsequently, simulated samples were exposed to known amounts of approximately 10% 1,3-butadiene in helium, followed by 25 L of air at 80% RH. The 1,3-butadiene concentration was independently determined by packed column gas chromatography with thermal conductivity detection. Media standards were prepared via calibrated sampling valves. The recovery from six simulated samples at 463 μg per sample was 101.6% versus media standards and 91.3% versus standard solutions
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