This work is licensed under a Creative Commons Attribution-NonCommercial-ShareAlike License. Your use of this material constitutes acceptance of that license and the conditions of use of materials on this site. Copyright 2006, The Johns Hopkins University, Patrick Breysse, and Peter S. J. Lees. All rights reserved. Use of these materials permitted only in accordance with license rights granted. Materials provided “AS IS”; no representations or warranties provided. User assumes all responsibility for use, and all liability related thereto, and must independently review all materials for accuracy and efficacy. May contain materials owned by others. User is responsible for obtaining permissions for use from third parties as needed. Air Sampling for Gases and Vapors Patrick N. Breysse, PhD, CIH Peter S.J. Lees, PhD, CIH Johns Hopkins University Section A Introduction Exposure Assessment Methods General air-sampling methodology Air Pump Flow Adjust Collection Media Air + Contaminant 4 Concentration Mass conta min ant Concentrat ion = Volume air Contaminant mass from laboratory analysis Air volume from product of calibrated air flow rate and sampling time 5 Source: U. S. Government 6 Charcoal Tube Calibration Calibrator Tubing Source: Patrick Breysse Charcoal tube Holder Sampling Pump 7 Personal Sampling Pumps Source: Patrick Breysse 8 Section B Sample Collection Methods Sampling for Gases and Vapors Absorptive methods – Absorption is a molecular process by which molecules are homogeneously dispersed in another substance – Forming a solution (i.e., requires a liquid sampling medium) Methods now mostly obsolete Continued 10 Sampling for Gases and Vapors Adsorptive methods – Adsorption is a molecular process by which molecules are reversibly bound to a surface – Bound by intermolecular or van der Waals forces – Uses solids as sampling medium Most current gas and vapor methods are adsorptive 11 Absorptive Methods: Impingers Contaminant bubbled through absorbent solution Solution changes according to analyte Analyzed by wet chemical methods Messy and unstable; not suited to personal sampling Used for gases (NO2) 12 Impingers Source: U. S. Government Continued 13 Adsorptive Methods Gas and vapor molecules “stick” to solid surface Highly efficient reversible process Contaminant stable for transport Many different adsorbents available Can be affected by high humidity Subject to overload Continued 14 Adsorptive Methods Some common adsorbent media – Activated charcoal: Polar solvents (many hydrocarbons) – Silica gel: Non-polar solvents (alcohols and aldehydes) – Treated diatomaceous earth – Gas chromatographic supports 15 Adsorbent Tubes Source: Patrick Breysse 16 Adsorptive Methods: Charcoal Sampling – 20–200 ml/min drawn through tube Analysis – Analyte(s) desorbed (CS2, or thermally) – Typically analyzed using gas chromatography Continued 17 Adsorptive Methods: Charcoal Overload – >25% on “B” section indicates breakthrough (loss) – Discard sample or report as underestimate 18 Standard Sampling Tube Direction of flow Source: U.S. Government 19 Section C Passive Sampling Methods Passive (Diffusive) Sampling Passive sampling relies on the natural diffusive energy of molecules to move them to sampling media Contaminant flux (mass/sampler area/unit time) is governed by Fick’s Law Effective flow rates generally 5–30 ml/min A variety of designs 21 Example: Passive Sampler Source: Peter Lees 22 Section D Sample Analysis Gas and Vapor Analysis Numerous methods – Spectrophotometric – Chromatographic • Gas chromatography (GC) • High-performance liquid chromatography (HPLC) • GC-Mass spectrometry (GC-MS) – Wet chemical 24 Analytical Laboratory Choose analytical laboratory before sampling Choose standard method Know limits of detection – Calculate minimum sample volume to be minimally detectable – Evaluate breakthrough potential Know interferences 25 Quality Control Blanks – At least 10% of samples should be blanks Spiked samples – Whenever possible, submit a “known” or spiked sample Continued 26 Quality Control Split samples – If possible, submit split samples to either the same laboratory or two different laboratories 27 Section E Direct-Reading Instruments Direct-Reading Instruments “Real time” measurement of contaminant Information saved to data logger Subsequent data analysis (mean, min., max., etc.) Principle of operation varies – Infrared absorption – Ultraviolet absorption – Electro-chemical method Continued 29 Direct-Reading Instruments Numerous designs and manufacturers Possible uses – Walk-through survey (preliminary hypothesis testing) – Leak detection – Over-exposure alarm – Personal monitoring – Emergency response Continued 30 Direct-Reading Instruments Limitations – Specific versus non-specific response – Must know principal of operation – Must know positive and negative interference – Must be calibrated often – Subject to damage 31