Lecture 10: Air Sampling for Gases and Vapors

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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
Š General air-sampling methodology
Air
Pump
Flow
Adjust
Collection
Media
Air + Contaminant
4
Concentration
Mass conta min ant
Concentrat ion =
Volume air
Š Contaminant mass from laboratory
analysis
Š 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
Š 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)
Š Methods now mostly obsolete
Continued
10
Sampling for Gases and Vapors
Š 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
Š Most current gas and vapor methods
are adsorptive
11
Absorptive Methods: Impingers
Š Contaminant bubbled through
absorbent solution
Š Solution changes according to analyte
Š Analyzed by wet chemical methods
Š Messy and unstable; not suited to
personal sampling
Š Used for gases (NO2)
12
Impingers
Source: U. S. Government
Continued
13
Adsorptive Methods
Š Gas and vapor molecules “stick” to
solid surface
Š Highly efficient reversible process
Š Contaminant stable for transport
Š Many different adsorbents available
Š Can be affected by high humidity
Š Subject to overload
Continued
14
Adsorptive Methods
Š 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
Š Sampling
– 20–200 ml/min drawn through tube
Š Analysis
– Analyte(s) desorbed (CS2, or
thermally)
– Typically analyzed using gas
chromatography
Continued
17
Adsorptive Methods: Charcoal
Š 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
Š Passive sampling relies on the natural
diffusive energy of molecules to move
them to sampling media
Š Contaminant flux (mass/sampler
area/unit time) is governed by Fick’s Law
Š Effective flow rates generally 5–30 ml/min
Š A variety of designs
21
Example: Passive Sampler
Source: Peter Lees
22
Section D
Sample Analysis
Gas and Vapor Analysis
Š Numerous methods
– Spectrophotometric
– Chromatographic
• Gas chromatography (GC)
• High-performance liquid
chromatography (HPLC)
• GC-Mass spectrometry (GC-MS)
– Wet chemical
24
Analytical Laboratory
Š Choose analytical laboratory before
sampling
Š Choose standard method
Š Know limits of detection
– Calculate minimum sample volume
to be minimally detectable
– Evaluate breakthrough potential
Š Know interferences
25
Quality Control
Š Blanks
– At least 10% of samples should be
blanks
Š Spiked samples
– Whenever possible, submit a
“known” or spiked sample
Continued
26
Quality Control
Š 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
Š “Real time” measurement of contaminant
Š Information saved to data logger
Š Subsequent data analysis (mean, min.,
max., etc.)
Š Principle of operation varies
– Infrared absorption
– Ultraviolet absorption
– Electro-chemical method
Continued
29
Direct-Reading Instruments
Š Numerous designs and manufacturers
Š Possible uses
– Walk-through survey (preliminary
hypothesis testing)
– Leak detection
– Over-exposure alarm
– Personal monitoring
– Emergency response
Continued
30
Direct-Reading Instruments
Š 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