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NARSTO Measurement Methods Compendium
NO2 Methods |
- NO2
-
Chemiluminescence after NO2
conversion to NO - (FRM)
- Basis: Chemiluminescence is the technique used to measure an analyte
by mixing it with a species with which it reacts to form light. The
intensity of the light is proportional to the concentration of the analyte
and can be measured. Ambient air is flooded with excess ozone, which
reacts with NO to produce excited NO2. The NO2
emits a photon as it returns to ground state. The NO2 in
a second ambient air sample is then reduced to NO by a converter. The
new NO concentration can again be measured by chemiluminescence. The
difference of the concentrations is the concentration of NO2.
- Range: 0.25 - 25 ppmv
- Minimum Detection Level: 0 .005 ppmv
- Operating Temperature: N/A
- Known Interference: Water vapor above 20 ppm concentration.
NO2 to NO converter specific interference:
- Catalytic reduction using heated molybdenum - PAN (375°C,
450°C); ethyl nitrate; ethyl nitrite; HONO; HNO3
(350°C, 375°C, 450°C); methyl nitrate, n-propyl nitrate,
n-butyl nitrate, nitrocresol (450°C)
- Catalytic reduction using heated stainless steal -
NH3, CH3NH2, HCN, N2O
(650°C)
- Reaction with CO over a gold catalyst surface - n-propyl
nitrate; HNO3, N2O5,
PAN (3,000 ppm CO over 300°C gold surface); HCN, NH3
(except in the presence of water vapor under 700°C)
- Reaction with iron sulfate (FeSO4) at room
temperature - PAN, HONO, and other nitrogen-containing species
(dry conditions)
- Reaction with carbon at 200°C - PAN (285°C),
HNO3 (285°C), n-propyl nitrate, phosgene, trichloroacetyl
chloride, chloroform, chlorine, hydrogen chloride, photochemical reaction
products of perchloroethylene-NOx mixtures, photochemical
reaction products of molecular chloride (Cl2)-NOx
mixtures, photochemical reaction products of molecular chloride
(Cl2)-methanethiol mixtures, methanethiol, ethanethiol,
ethyl sulfide, ethyl disulfide, methyl disulfide, 3-methylthiophene,
H2S, 2,5-dimethylthiophene, methyl sulfide, methyl ethyl
sulfide
- Photolysis at 320-400 nm - HONO; NO3;
HO2NO2; N2O5
- Notes of Interest: N/A
- Instrument - Manufacturer:
- Advanced Pollution Instrumentation, Inc. Model 200 NO2
Analyzer - Advanced Pollution Instrumentation, Inc.
- Advanced Pollution Instrumentation, Inc. Model 200A NO2
Analyzer - Advanced Pollution Instrumentation, Inc.
- Beckman Model 952-A NO/NO2/NOx Analyzer -
Beckman Coulter
- Bendix Model 8101-B Oxides of Nitrogen Analyzer - Bendix Corporation
(refer to ABB
Process Analytics)
- Bendix/Combustion Engineering Model 8101-C Oxides
of Nitrogen Analyzer - Bendix Corporation (refer to ABB Process
Analytics)
- Columbia Scientific Industries Models 1600 and 5600 Analyzers -
Columbia Scientific Industries
- Dasibi Model 2108 Oxides of Nitrogen Analyzer - Dasibi Environmental
Corp.
- Environnement S.A. Model AC31M NO Analyzer - Environnement S.A.
- Horiba Instruments Model APNA-360 NO-NO2-NOx
Monitor - Horiba Instruments
Inc.
- Monitor Labs Model 8440E Nitrogen Oxides Analyzer - Monitor Labs
Inc.
- Monitor Labs Model ML9841B - Monitor Labs
- Monitor Labs/Lear Siegler Model 8840
and Model 8841 Nitrogen Oxides Analyzer - Monitor Labs
Inc.
- Monitor Labs/Lear Siegler Models ML9841 and ML9841 - Monitor Labs
Inc.
- Wedding and Associates Model 1030 NO2
Analyzer - Wedding and Associates Inc. (a subsidiary of Thermo Environmental Instruments Inc.)
- Phillips Model PW9762/02 NO/NO2/NOx Analyzer -
Phillips Electronic Instruments, Inc.
- Thermo Electron/Thermo Environmental Instruments Model 14 B/E and
Model 14 D/E - Thermo Environmental
Instruments Inc.
- Thermo Environmental Instrument Model 42
and 42C NO/NO2/NOx Analyzer - Thermo Environmental Instruments Inc.
- References: 1, 4, 5, 23 (Go to
References)
- Differential Optical Absorption Spectrometry
(DOAS) - (FEM)
- Basis: The wavelength of light where a distinct absorption peak
occurs is determined for an analyte. A wavelength (
) on either
side of the absorption peak is next determined. The intensity of a
light source at wavelength (
) is measured and then the intensity is
measured again after the light passes through the analyte. The difference
of the intensities is proportional to the concentration to the analyte.
- Range: 0-500 ppbv
- Minimum Detection Level: 4 ppbv
- Operating Temperature: 20°C-30°C and an air temperature
of -50°C-50°C
- Known Interference: Anything that interrupts the path of the laser
will cause some interference (i.e., animals, cars, planes, etc.).
- Notes of Interest: DOAS is a long path measuring
technique. Measurements can be made in an optical pathway from 1 to
10 kilometers.
- Instrument - Manufacturer:
- OPSIS Model AR 500 and System 300 Open Path Ambient
Air Monitoring System for NO2 - manufactured by OPSIS AB of Sweden (available from ABB Power Plant
Controls, Inc.)
- References: 1, 4, 8, 14, 15 (Go to
References)
- Sodium Arsenite Method - (FEM)
- Basis: Ambient air is bubbled with an orifice bubbler through
a solution of sodium hydroxide (NaOH). The NO2 is
reduced to nitrite. The nitrite is reacted with sulfanilamide and
N-1-napthylethylenediamine (NEDA) in acid media to form an azo dye. The
dye can be analyzed with a spectrophotometer at 540 nm.
- Range: 30-150 ppbv
- Minimum Detection Level: 5 ppbv
- Operating Temperature: N/A
- Known Interference: NO and CO2 are known interferences
but at concentrations far exceeding those found in ambient air. The role
of SO2 as an interference has not been determined.
- Notes of Interest: The original manual FRM was the Jacobs-Hochheiser
Method. The method was withdrawn in 1973 by the EPA and is now considered
unacceptable for air sampling and analysis.
- Instrument - Manufacturer: This is a manual method.
- References: 1, 11 (Go to References)
- Sodium Arsenite Method Technicon II Automated
Analysis System - (FEM)
- Basis: Ambient air is bubbled with an orifice bubbler through
a solution of sodium hydroxide (NaOH). The NO2 is
reduced to nitrite. The nitrite is reacted with sulfanilamide and
N-1-napthylethylenediamine (NEDA) in acid media to form an azo dye.
The dye can be analyzed with a spectrophotometer at 540 nm. This method
is considered a continuous method because hardware is used to make
continuous measurements of the concentration of NO2.
- Range: 30-150 ppbv
- Minimum Detection Level: 5 ppbv
- Operating Temperature: N/A
- Known Interference: NO and CO2 are known interferences
but at concentrations far exceeding those found in ambient air. The role
of SO2 as an interference has not been determined.
- Notes of Interest: The original manual FRM was the Jacobs-Hochheiser
Method. The method was withdrawn in 1973 by the EPA and is now considered
unacceptable for air sampling and analysis.
- Instrument - Manufacturer: No current information on Technicon
could be located.
- References: 1, 11 (Go to References)
- TGS-ANSA - (FEM)
- Basis: Ambient air is bubbled with an orifice bubbler through a
solution of triethanolamine, guaiacol, and sodium metabisulfite (TGS). The
NO2 is reduced to nitrite and then reacted with sulfanilamide
and 8-amino-1-naphthalene-sulfonic acid ammonium salt (ANSA) to form an
azo dye. The dye is analyzed with a spectrophotometer at 550 nm.
- Range: 30-150 ppbv
- Minimum Detection Level: 8 ppbv
- Operating Temperature: N/A
- Known Interference: No interference from NH3, CO,
formaldehyde, NO, phenol, O3, or SO2.
- Notes of Interest: The original manual FRM was the Jacobs-Hochheiser
Method. The method was withdrawn in 1973 by the EPA and is now considered
unacceptable for air sampling and analysis.
- Instrument - Manufacturer: This is a manual method.
- References: 1, 10 (Go to References)
For definitions of method description terms see the Annotated Method Description Outline and
Definitions.
For more information on FRM/FEM instrumentation, visit the AMTIC Designated Methods --
NO2.
NARSTO Measurement Methods Compendium
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