study guide
EHST 3700 1
Basic air sampling approaches
Integrated sampling
Direct-reading method
Types of sampling
Personal sampling
Area sampling
Particulate sampling
Filters
Size-selective sampling
Gas/vapor sampling
Sorbent tube
Passive sampling
Impingers
Grab sampling
Validated sampling methods
OSHA Reference Methods
NIOSH Manual of Analytical Methods
Pump calibration
Liters/minute
Inverted buret, electronic calibrators
EHST 3700/3701:
Industrial Hygiene
To discuss the reasons for air sampling in the
workplace
To explain the different types of sampling
strategies
To describe some sampling methods for air
contaminants
To describe analytical instruments and methods
in laboratories to evaluate air samples
To interpret and evaluate air sampling results
To discuss documentation of sampling events
To discuss about sources of errors in sampling
To discuss problems or limitations associated
with air samples
Uses of Air Sampling
Sampling Particulates
Sampling Gases and Vapors
Standard Sampling and Analysis Methods
Laboratory Analytical Techniques
Direct-Reading Methods
Air Sampling Strategies
Sampling train
Sampling media
Laboratory analysis
EHST 3700 2
Dusts and fibers
Gravimetric analysis
Graticule or reticule
Metal dust and
fumes
Similar to gas and
vapor analysis
Gas and vapor analysis
Spectrophotometer
Gas chromatography
Mass spectrometry
Absorption spectroscopy
Inductively coupled plasma
Fluorescence spectrometry
Gravimetric analysis Graticule or Reticule
Walton-Beckett Graticule
Porton Counting Reticule
Desiccator Pre-sampling weight
Post-sampling weight
Dust sampling
Desiccator
24 hr
24 hr
Dust weight = post-sampling weight – pre-sampling weight
Spectrophotometer
Gas chromatography (GC)
Mass spectrometry (MS)
Absorption spectroscopy
Inductively coupled plasma (ICP)
Fluorescence spectrometry
For gases and vapors collected by dissolution
or absorption in a solution
Measures the intensity of the solution color
(proportional to the analyte concentration)
Measures the degree of light scattering that
is proportional to the amount of precipitate
in the solution
Used for detection of dusts and other
airborne particulates
Technique used in direct-reading instruments
EHST 3700 3
Lab Analysis
Sorbent Tube
Desorbed
Analyte Desorbing
Solution
Used for organic compounds
Identity of compound is determined by the
amount of time needed for it to pass through
the column (retention time)
Sample output from a
GC analysis used to
identify an unknown
Sample bombarded with a beam of electrons to become ionized
Each ion produced has specific mass
Relationship between mass of an ion and its charge (m/e) is unique
Unique to a compound (fingerprint)
n-octane
2,2,4-trimethylpentane
Involves the measurement of the amount of
energy that is absorbed by a compound
The particular wavelength where energy is
absorbed indicates the identity of the
compound
Techniques
Ultraviolet spectrometry
Infrared spectrometry
Atomic absorption
EHST 3700 4
Benzene
Toluene
Also relies on specific spectrum of energy
absorption to identify the analyte compound
Used most commonly to detect metals
An example of emission spectroscopy
Utilizes the ability of electrons to absorb
energy but measures the energy loss of
excited electrons as they return to the
ground state
Spectrum emission is specific to the analyte
Intensity of emissions is proportional to the
amount that is present
Useful in metal scans (a number of elements
analyzed from the same sample)
Determines intensity and wavelength of
energy emitted by excited electrons
Used in the analysis of organic compounds,
particularly those with aromatic rings (i.e.
benzene)
Lamp used as a source of energy to excite
the sample
Lamp selection depends on the analytes of
interest (i.e. xenon-arc, tungsten, mercury
lamps)
EHST 3700 5
Gas meters
Photoionization and flame ionization
detectors
Detector or length-of-stain tubes
Portable units containing a
small pump that draws air
into the instrument
Passes into sampling
chamber (sensor unit)
Connected to a readout
device
Can be specific to a gas or
multi-gas
Oxygen
Combustibles
Toxics: total hydrocarbons
(non-specific)
1. Wheatstone bridge circuit
Catalytic combustion sensors
Heat of combustion Change in electrical
resistance imbalance in the circuit
2. Metal-oxide semiconductor (MOS)
Adsorption onto an MOS
Change in electrical conductivity
3. Thermal conductor
Thermal conductivity
Change in temperature
Sensors can become
less sensitive over
time.
Sensors can become
contaminated by
interfering compounds.
Instrument most often used to
detect organic vapors (i.e.
alcohols, ketones, ethers)
UV lamp light energy
absorbed by contaminants
become charged collected by an
electrode current proportional
to the concentration of
contaminant ions
Limitation: non-specific
Use: Screening of atmosphere for
set of contaminants
EHST 3700 6
Ionizes contaminant molecules using energy
from hydrogen flame
Commonly used to detect hydrocarbons and
organic compounds
Limitation: non-specific
Use: Screening of atmosphere for set of
contaminants
Length-of-stain tubes
Contain a solid sorbent coated
with a reagent that reacts with
a contaminant and causes a
color change
1. Determine agents to be sampled.
2. Select the sampling method.
3. Obtain and review a copy of the sampling
method.
4. Obtain adequate sampling media and
equipment.
5. Calibrate sampling pumps or instruments.
6. Perform sampling.
7. Ship samples to laboratory for analysis.
8. Interpret analytical results.
9. Prepare a report to employee and
management.
Laboratory techniques for particulates
include gravimetric analysis, counting
tecniques and microscopy.
Laboratory techniques for gases and vapors
include GC, MS, AA, ICP, FS, etc.
Direct-reading methods involve the use of
portable instruments that provide results at
the site, including gas meters, PID, FID and
detector tubes.