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Method no.: ID-190 (This method supersedes ID-109)
Matrix: Air
OSHA Permissible Exposure Limits
  Final Rule and
  Transitional Limits:

25 ppm (Time Weighted Average)
Collection Device: The sampling device consists of:
1) Two glass tubes which contain triethanolamine-impregnated molecular sieve
2) a middle tube which contains an oxidizer
3) a personal sampling pump is used to draw a measured volume of air through the tubes.
Recommended Sampling Rate: 0.025 L/min
Recommended Maximum Air Volume: 6.0 L
Analytical Procedure: The sample is desorbed using a 1.5% triethanolamine solution and analyzed as nitrite by ion chromatography.
Detection Limit

0.11 ppm (6-L air sample)
0.32 ppm (6-L air sample)
Precision and Accuracy
  Evaluation Range:
  Overall Error:

13.0 to 50.5 ppm
Method Classification: Validated Method
Chemist: James Ku
Date (Date Revised): April, 1989 (May, 1991)

Commercial manufacturers and products mentioned in this method are for
descriptive use only and do not constitute endorsements by USDOL-OSHA.
Similar products from other sources can be substituted.
Branch of Inorganic Methods Development
OSHA Technical Center
Sandy, Utah
1. Introduction

This method describes the collection and analysis of airborne nitric oxide (NO). Samples are taken in the breathing zone of workplace personnel and analyses are performed by ion chromatography (IC).

1.1. History

Previous methods involved oxidation of NO to nitrogen dioxide (NO2) using a chromate compound and subsequent conversion of NO2 to nitrite using triethanolamine-impregnated molecular sieve (TEA-IMS) sampling tubes. Common methods used a combination sampling tube and NO was determined colorimetrically (as NO2-) using a modified Griess-Saltzman reaction (8.1.-8.2.). This method, like most colorimetric procedures, can have significant interferences.

A differential pulse polarographic (DPP) method (8.3.) was later developed to improve analytical sensitivity and decrease the potential for interferences. The sensitivity of the DPP method was more than adequate for measuring workplace concentrations of NO; however, the nitrite ion is unstable in the pH range (pH 1-2) used during analysis (8.4.).

Method no. ID-190 uses the TEA-IMS sampling tube/chromate oxidizer approach. Samples are analyzed by IC.

1.2. Principle

A known volume of air is drawn through the sampling device which captures any nitrogen dioxide (NO2) in the sampled air and also converts any NO to nitrite ion (NO2-). The sampling device consists of three glass tubes connected in series. The front and back tubes contain TEA-IMS, the middle or oxidizer tube contains an inert carrier impregnated with a chromate salt. The first TEA-IMS tube does not capture NO; this tube is only used to capture and convert to NO2- any NO2 present in the sampled air. The middle tube oxidizes the sampled NO to NO2. The back TEA-IMS tube then captures and converts this NO2 to NO2-. Both TEA-IMS samples are desorbed using an aqueous triethanolamine (TEA) solution and analyzed as NO2- by IC. The front tube analytical results are reported as NO2 and the back tube as NO.

The conversion mechanism of NO2 gas to NO2- has been proposed by Gold (8.5.). The following is Gold's proposal for the reaction of equivalent amounts of NO2 and TEA in an aqueous solution:

2NO2<=> N2O4

N2O4 + (HOCH2CH2)3N --> (HOCH2CH2)3NNO+NO3-

(HOCH2CH2)3NNO+NO3- + H2O --> (HOCH2CH2)3NH+NO3- + HNO2

HNO2 --> H+ + NO2-

Nitrogen dioxide disproportionates to NO2- and nitrate (NO3-) in the presence of TEA and water. The NO2- formed from the above reaction can be analyzed via conventional analytical methods (8.1.-8.4., 8.6.-8.7.) including IC. Unfortunately NO3- is found in the commercial TEA-IMS sorbent as a significant contaminant. This contamination ruled out further research to also measure this NO2-TEA disproportionation product by IC.

This reaction path requires a stoichiometric factor of 0.5 for the conversion of
gaseous NO2 to NO2-. Experiments indicate the stoichiometric factor of 0.5 is seen only when NO2 concentrations are greater than 10 ppm (8.5., 8.8.-8.9.). The conversion factor has been experimentally determined to average approximately 0.6 to 0.7 when concentrations are below 10 ppm (8.1.-8.3., 8.5.-8.9.). The deviation from ideal stoichiometry is believed to be due to competing reactions; however, evidence to support a competing mechanism has not been found (8.5.).

1.3. Advantages and Disadvantages
1.3.1. This method has adequate sensitivity for determining compliance with the OSHA Time Weighted Average (TWA) Permissible Exposure Limit (PEL) for workplace exposures to NO.

1.3.2. The sampling device can be used to simultaneously collect NO and NO2; however, results for NO2 may not reflect short-term exposures (see Section 5.2. for more details).

1.3.3. The analysis is simple, rapid, easily automated and is specific for NO2-.

1.3.4. After analytical sample preparation, NO exposures (as nitrite ion) can also be determined by colorimetric or polarographic analytical techniques (8.1.-8.3.).

1.3.5. A disadvantage is the potential interference from large amounts of soluble chloride salts present in commercial molecular sieve. Prior to TEA impregnation, the molecular sieve should be washed with deionized water (DI H2O) to remove any soluble chloride salts.

1.3.6. Another disadvantage is the need for a concentration-dependent conversion factor when calculating results.
1.4. Physical properties (8.10., 8.11.)

Nitric oxide (CAS No. 10102-43-9), one of several oxides of nitrogen, is a colorless gas. A deep blue color is usually noted when NO is in the liquid state and a bluish-white color when solid. Other physical characteristics of NO are:

Formula weight 30.01
Specific gravity 1.27 at -150.2 C (as liquid)
Melting point -163.6 C
Boiling point -151.8 C
Vapor density 1.04 (air = 1)
Solubility 4.6 mL NO in 100 mL H2O
Synonyms nitrogen monoxide*,
  mononitrogen monoxide
*Nitrogen monoxide has also been used as a synonym for nitrous oxide (N2O).

1.5. Some industrial sources for potential nitric oxide exposures are:
agricultural silos
arc or gas welding (esp. confined space operations)
electroplating plants
food and textile bleaching
jewelry manufacturing
metal nitrosyl carbonyl production
nitric acid production
nitrogen fertilizer production
nitro-explosive production
nitrosyl halide production
pickling plants
Nitrogen dioxide and nitric oxide usually exist together in industrial settings. Nitric oxide is reactive in air and produces NO2 according to the following equations (8.10.):

2NO + O2 ----> 2NO2

d(NO2)/dt= K(O2)(NO)2

(K is a temperature dependent constant. At 20 C, K = 14.8 X 109)

An experimental approximation of the NO/NO2 distribution found in various industrial operations is shown (8.10.):

Source % NO2 % NO

Carbon arc 9 91
Oxyacetylene torch 8 92
Cellulose nitrate combustion 19 81
Diesel exhaust 35 65
Dynamite blast 52 48
Acid dipping 78 22

The potential for exposure to both NO2 and NO should be considered because NO is easily oxidized to NO2 and both oxides are likely to coexist in industrial settings.

1.6. Toxicology (8.11.-8.14.)

Information listed within this section is a synopsis of current knowledge of the physiological effects of nitric oxide and is not intended to be used as a basis for OSHA policy.

1.6.1. Nitric oxide is classified as a respiratory irritant. The main route of exposure is inhalation; however, physiological damage can also occur eyes or skin.

The term "silo-fillers' disease" has been used to describe exposure to nitric as well as other nitrogen oxides. The national population-at-risk for exposure to nitrogen oxides has been estimated by NIOSH to be approximately 950,000 employees (National Occupational Hazard Survey, 1972-74). When encountering either NO or NO2 at high concentrations, both species will usually be present. Little scientific data is available regarding exposures to NO only. The majority of collected data concerns exposure to NO2 since NO appears to be only one-fifth as toxic as NO2 at low concentrations. Symptoms immediately following NO exposure are usually mild or not apparent. Severe symptoms may not appear up to 72 hours after exposure.

1.6.2. Mild exposures to NO can result in symptoms such as:

cough shortness of breath
painful breathing chest pains
increased breathing rate weakness

More severe exposures (>100 ppm) are characterized by pulmonary edema , cyanosis, pneumonia, severe methemoglobinemia, respiratory failure, and death.

1.6.3. The IDLH (Immediately Dangerous to Life or Health) concentration is 100 ppm NO. The LCLo (Lethal Concentration - Low) for inhalation by mice is 320 ppm.

1.6.4.Mechanism for toxicity:

Nitric oxide is slightly soluble in water and forms nitrous and nitric acid. This reaction occurs with lung tissue and produces respiratory irritation and edema. Alkali present in the lung tissue neutralizes the nitrous and nitric acids to nitrite and nitrate salts which are then absorbed into the bloodstream. The end result is the formation of nitroxy-hemoglobin complexes and methemoglobin in the circulatory system.

The formation of hemoglobin complexes is thought to contribute to the toxicity of NO but is not considered to be the sole source of the toxic reaction. The respiratory damage from nitrous and nitric acid appears to be more significant.
2. Range, Detection Limit and Sensitivity

The analytical parameters and limits of this method have been previously described (8.8.). Brief descriptions are provided in Section 3 below.

3. Method Performance

This method was evaluated in the concentration range of 13.0 to 50.5 ppm. Air volumes of approximately 6 L and flow rates of about 0.025 L/min were used. Samples were collected for 240 min. Sample results were calculated using the concentration-dependent conversion factors mentioned in Section 7. Listed on the cover page (CVT, bias, overall error) and below are evaluation data taken from the backup report (8.9.).

Qualitative detection limit1: 0.08 g/mL (as NO2-)
0.11 ppm NO (6 L air volume)
Quantitative detection limit1: 0.23 g/mL (as NO2-)
0.32 ppm NO (6 L air volume)
Sensitivity (1 to 30 g/mL nitrite):
Hewlett-Packard2 239,000 area counts per
1 g/mL NO2-
Dionex2 10,000 area counts per
1 g/mL NO2-
Collection efficiency3 100%
Breakthrough none at levels tested3
Sample storage at least 30 days (20-25 C)

1 Detector setting = 3 microsiemens, sample loop = 50 L (8.8.)
2 A model 3357 data reduction system (Hewlett-Packard, Avondale, PA) (1 area unit = 0.25 microvolt-second) was used during first part of evaluation. An AutoIon 400 data reduction system (Dionex, Sunnyvale, CA) was used for later analyses.
3 Collection efficiency samples were taken using a concentration of 50.5 ppm NO for 240 min, 50% RH, and 0.025 L/min. Breakthrough tests were performed at 25 C, 50% RH, and a flow rate of 0.025 L/min. Samples were collected at a concentration of 200 ppm for 60, 120, 180, and 240 min.

4. Interferences
4.1. When other compounds are known or suspected to be present in the sampled air, such information should be transmitted to the laboratory with the sample.

4.2. Any compound that has the same retention time as nitrite, when using the operating conditions described, is an interference.

4.3. Interferences may be minimized by changing the eluent concentration, column characteristics, and/or pump flow rate.

4.4. If there is an unresolvable interference, alternate polarographic or colorimetric methods may be used (8.1.-8.3.).

4.5. Contaminant anions normally found in molecular sieve, such as NO3-, SO42-, and PO43-, do not interfere. Large amounts (greater than 4 to 5 g/mL) of Cl- can interfere.
5. Sampling
5.1. Equipment
5.1.1. A three tube sampling device is commercially available (NO/NO2 sampling tubes, Cat. No. 226-40-special order, water-washed, SKC, Eighty Four, PA) and can be used to simultaneously sample NO2 and NO, or sample only NO2. This device consists of three flame-sealed glass tubes:
1) Nitrogen dioxide is collected in the first tube which contains 400 mg TEA-IMS.
2) The second (oxidizer) tube converts NO to NO2 and contains approximately 1 g of a chromate compound impregnated on an inert carrier.
3) The last 400 mg TEA-IMS packed tube collects the converted NO2.
All molecular sieve used for tube packing must be washed with DI H2O before impregnation with TEA. The dimensions of each TEA-IMS tube are 7-mm o.d., 5-mm i.d., and 70-mm long. A 3-mm portion of silylated glass wool is placed in the front and rear of each tube. The dimensions of the oxidizer tube are 7-mm o.d., 5-mm i.d., and 110-mm long .

When the three tubes are connected in series as shown below, NO2 and NO can be collected simultaneously. The first TEA-IMS tube must be in place to prevent the collection of NO2 by the second TEA-IMS tube.


Text Version: The first tube in the Three-Tube Sampling Device is a nitrogen dioxide (NO2) sampling tube (TEA-IMS Tube). The second tube in the series is an oxidizer tube, and the third is another NO2 sampling tube that is identical to the first tube. The three tubes are connected with short lengths of plastic tubing (Tygon or equivalent). The three tubes should be connected as close to one another as possible. The sampling device is connected to the sampling pump with flexible plastic tubing. The set of three tubes that compose the sampling device is available from SKC, Inc. as catalog 226-40.

5.1.2. Personal sampling pumps capable of sampling at a flow rate of approximately 0.025 L/min are used.

5.1.3. A stopwatch and bubble tube or meter are used to calibrate pumps. A sampling device is placed in-line during flow rate calibration.

5.1.4. Various lengths of Tygon tubing are used to connect the sampling tubes and pump together.
5.2. Sampling Procedure

Note: If sampling for both NO2 and NO is necessary, two separate pumps and sampling devices should be used. The differences in OSHA exposure limits [the NO2 PEL is a 1 ppm Short-Term Exposure Limit (8.15.). Nitric oxide is a TWA PEL.] and flow rates dictates a need for a separate assessment of NO2. Nitric oxide is collected at a 0.025 L/min pump flow rate. Nitrogen dioxide can be collected at this flow rate; however, a longer sampling time will be necessary to collect a detectable amount of NO2 than for a short-term measurement. Concentrations of NO2 may vary in the workplace during a longer sampling period.

5.2.1. Calibrate the sampling pumps to a flow rate of 0.025 L/min.

5.2.2. Connect the sampling device to the pump. The different sampling schemes are listed:
a) Sampling for NO2 only: - Use a single TEA-IMS tube (8.8.).
b) Sampling for both NO and NO2: The three-tube device is used. The device must be assembled as shown above.
Label the first tube "NO2".
Label the tube following the oxidizer section "NO".
5.2.3. Place the sampling tube or device in the breathing zone of the employee.

5.2.4. Collect the sample at the listed flow rates and sampling times:

a) For NO2 only: 0.200 L/min for at least 15 min (8.8.) per sample.
b) For both NO and NO2: 0.025 L/min for 4 h per sample (Note: The front ube of the three-tube device can be submitted for NO2 analysis; however, analytical results may not represent short-term exposures).

5.2.5. The maximum recommended air volume is 6 L per NO sample.

Take enough samples for NO to cover the workshift.

Note: One oxidizer tube per sample is sufficient for concentration ranges of NO usually encountered in industrial settings. A color change from orange to blue-green will be noticeable if the oxidizer is depleted.

6. Analysis
6.1. Precautions
6.1.1. Refer to instrument and standard operating procedure (SOP) (8.16.) manuals for proper operation.

6.1.2. Observe laboratory safety regulations and practices.

6.1.3. Sulfuric acid (H2SO4) can cause severe burns. Wear protective eyewear, gloves, and labcoat when using concentrated H2SO4.
6.2. Equipment
6.2.1. Ion chromatograph (Model 2010 or 4000, Dionex, Sunnyvale, CA) equipped with a conductivity detector.

6.2.2. Automatic sampler (Model AS-1, Dionex) and 0.5 mL sample vials.

6.2.3. Laboratory automation system: Ion chromatograph interfaced to a data reduction and control system (AutoIon 400 or 450, Dionex).

6.2.4. Micromembrane suppressor, anion (Model AMMS-1, Dionex).

6.2.5. Separator and guard columns, anion (Model HPIC-AS4A and AG4A, Dionex).

6.2.6. Disposable syringes (1 mL) and filters.

Note: Some syringe pre-filters are not cation- or anion-free. Tests should be done with blank solutions first to determine suitability for the analyte being determined.

6.2.7. Erlenmeyer flasks, 25-mL, or scintillation vials, 20-mL.

6.2.8. Miscellaneous volumetric glassware: Micropipettes, volumetric flasks, graduated cylinders, and beakers.

6.2.9. Analytical balance (0.01 mg).
6.3. Reagents - All chemicals should be at least reagent grade.
6.3.1. Deionized water (DI H2O) with a specific conductance of less than 10 microsiemens.

6.3.2. Triethanolamine [(HOCH2CH2)3N]
sodium carbonate (Na2CO3)
sodium bicarbonate (NaHCO3)
sulfuric acid (H2SO4, concentrated 95 to 98%)
sodium nitrite (NaNO2)

6.3.3. Liquid desorber (1.5% TEA):
Dissolve 15 g TEA in a 1-L volumetric flask which contains approximately 500 mL DI H2O. Add 0.5 mL n-butanol and then dilute to volume with DI H2O.

6.3.4. Eluent (2.0 mM Na2CO3/1.0 mM NaHCO3):
Dissolve 0.848 g Na2CO3 and 0.336 g NaHCO3 in 4.0 L DI H2O.

6.3.5. Regeneration solution (0.02 N H2SO4):
Place 1.14 mL concentrated H2SO4 into a 2-L volumetric flask which contains about 500 mL DI H2O. Dilute to volume with DI H2O.

6.3.6. Nitrite stock standard (1,000 g/mL):
Dissolve 1.5000 g NaNO2 and dilute to the mark with DI H2O in a 1-L volumetric flask. Prepare every three months.

6.3.7. Nitrite standard (100 g/mL):
Dilute 10 mL of 1,000 g/mL nitrite stock standard to 100 mL with liquid desorber. Prepare monthly.

6.3.8. Nitrite standard (10 g/mL):
Dilute 10 mL of 100 g/mL nitrite stock standard to 100 mL with liquid desorber. Prepare weekly.

6.3.9. Nitrite standard (1 g/mL):
Dilute 10 mL of 10 g/mL nitrite stock standard to 100 mL with liquid desorber. Prepare daily.
6.4. Working Standard Preparation
6.4.1. Nitrite working standards (10-mL final volumes) may be prepared in the ranges specified below:

Working Std Standard Aliquot
Solution g/mL
0.5 1 5
1 1 *
3 10 3
6 10 6
10 10 *
30 100 3
50 100 5

* Already prepared in Section 6.3.

6.4.2. Pipette appropriate aliquots of standard solutions (prepared in Section 6.3.) into 10-mL volumetric flasks and dilute to volume with liquid desorber.

6.4.3. Pipette a 0.5- to 0.6-mL portion of each standard solution into separate automatic sampler vials. Place a 0.5-mL filter cap into each vial. The large exposed filter portion of the cap should face the standard solution.

6.4.4. Prepare a reagent blank from the liquid desorber solution.
6.5. Sample Preparation
6.5.1. Identify which tube is the collected NO2 sample and which is NO. Analyze these two tubes as separate samples.

6.5.2. Discard the oxidizer tube appropriately. This tube contains a chromate salt and may be considered a hazardous waste. Local regulations or restrictions should be consulted before disposal.

6.5.3. Clean the 25-mL Erlenmeyer flasks or scintillation vials by rinsing with DI H2O.

6.5.4. Carefully remove the glass wool plugs from the sample tubes, making sure no sorbent is lost in the process. Transfer each TEA-IMS section to individually labeled 25-mL Erlenmeyer flasks or scintillation vials.

6.5.5. Add 10 mL of liquid desorber to each flask containing NO samples, shake vigorously for about 30 s. Allow the solution to stand for at least 1 h. (Note: Add 3 mL to NO2 samples - see reference 8.8. for further details regarding NO2 analysis and result calculations)

6.5.6. If the sample solutions contain suspended particulate, remove the particles using a pre-filter and syringe. Fill the 0.5-mL automatic sampler vials with sample solutions and push a filtercap into each vial. Label the vials.

6.5.7. Load the automatic sampler with labeled samples, standards and blanks.
6.6. Analytical Procedure

Set up the ion chromatography and analyze the samples and standards in accordance with the SOP (8.16.). Typical operating conditions for equipment mentioned in Section 6.2. are listed below.
Ion chromatograph
Eluent: 2.0 mM Na2CO3/1.0 mM NaHCO3
Column temperature: ambient
Sample injection loop: 50 L

Pump pressure: approximately 1,000 psi
Flow rate: 2 mL/min

Run time: 6 min
Average retention time: approximately 2 min
7. Calculations
7.1. Obtain hard copies of chromatograms from a printer. A typical chromatogram is shown in Figure 1.

7.2. Prepare a concentration-response curve by plotting the concentration of the standards in g/mL (or g/sample if the same volumes are used for samples and standards) versus peak areas or peak heights. Calculate sample concentrations from the curve and blank correct all samples.

7.3. The concentration of NO in each air sample is expressed in ppm and is calculated as:

ppm NO = MV g/mL NO2 solution volume conversion GF
formula weight air volume

MV (Molar Volume) = 24.45 (25 C and 760 mmHg)
g/mL NO2 = blank corrected sample result
Conversion [NO2 (gas)/NO2-] = varies with concentration*
GF (Gravimetric factor NO/NO2) = 0.6522
Formula Weight (NO) = 30.01

*The conversion of gaseous NO2 to NO2- is concentration dependent. The final concentration of NO should be calculated using whichever example given below is appropriate:

Below 10 ppm NO

From 0 to 10 ppm, the average ratio has been experimentally determined to be (8.1.-8.3., 8.5.-8.9.):

1 g NO2 (gas) = 0.630 g NO2-

or conversely:

1 g NO2- = 1.587 g NO2 (gas)

Simplifying the equation and calculating the ppm NO using a 10-mL sample volume gives:
ppm NO = g/mL NO2 10 mL 0.843
air volume, L

Above 10 ppm NO

Above 10 ppm NO, the expected stoichiometric factor of 0.5 mole of nitrite to 1 mole of nitrogen dioxide gas is seen (8.5., 8.8.-8.9.). Therefore, the following calculation should be used for sample results above 10 ppm and a 10-mL solution volume:
ppm NO = g/mL NO2 10 mL 1.063
air volume, L

7.4. Reporting Results

Report all results to the industrial hygienist as ppm nitric oxide.
8. References
8.1. National Institute for Occupational Safety and Health (NIOSH): NIOSH Manual of Analytical Methods, 2nd ed., Vol. 4 (DHEW/NIOSH Pub. No. 78-175, Method No. S321). Cincinnati, OH. 1978.

8.2. Willey, M.A., C.S. McCammon, Jr., and L.J. Doemeny: A Solid Sorbent Personal Sampling Method for the Simultaneous Collection of Nitrogen Dioxide and Nitric Oxide in Air. Am. Ind. Hyg. Assoc. J. 38:358-363 (1977).

8.3. Occupational Safety and Health Administration Analytical Laboratory: OSHA Analytical Methods Manual (USDOL/OSHA-SLCAL Method No. ID-109). Cincinnati, OH: American Conference of Governmental Industrial Hygienists (Pub. No. ISBN: 0-936712-66-X), 1985.

8.4. Chang, S.K., R. Kozenianskas, and G.W. Harrington: Determination of Nitrite Ion Using Differential Pulse Polarography. Anal. Chem. 49: 2272-2275 (1977).

8.5. Gold, A.: Stoichiometry of Nitrogen Dioxide Determination in Triethanolamine Trapping Solution. Anal. Chem. 49:1448-50 (1977).

8.6. Blacker, J.H.: Triethanolamine for Collecting Nitrogen Dioxide in the TLV Range. Am. Ind. Hyg. Assoc. J. 34:390 (1973).

8.7. Saltzman, B.E.: Colorimetric Microdetermination of Nitrogen Dioxide in the Atmosphere. Anal. Chem. 26:1949 (1954).

8.8. Occupational Safety and Health Administration Technical Center: Determination of Nitrogen Dioxide in Workplace Atmospheres (Ion Chromatography) by J.C. Ku (USDOL/OSHA-SLTC Method No. ID-182). Salt Lake City UT. Revised 1991.

8.9. Occupational Safety and Health Administration Technical Center: Nitric Oxide Backup Data Report (ID-190) by J.C. Ku. Salt Lake City, UT. Revised 1991.

8.10. National Institute for Occupational Safety and Health: Criteria for a Recommended Standard...Occupational Exposure to Oxides of Nitrogen (Nitrogen Dioxide and Nitric Oxide) (DHEW/NIOSH Pub. No. 76-149). Cincinnati, OH: NIOSH, 1976.

8.11. Braker, W. and A.L. Mossman: Matheson Gas Data Book. 5th ed. East Rutherford, NJ: Matheson Gas Products, 1971. pp. 405-410.

8.12. Merchant, J.A. Ed.: Occupational Respiratory Diseases (DHHS/NIOSH Pub. No. 86-102). Cincinnati, OH: NIOSH, 1986. pp. 590-594.

8.13. American Conference of Governmental Industrial Hygienists: Documentation of the Threshold Limit Values and Biological Exposure Indices. 5th ed. Cincinnati, OH: ACGIH, 1986. pp. 435-436.

8.14. Specialty Gas Department: Material Safety Data Sheet for Nitric Oxide. Allentown, PA: Air Products, 1982.

8.15. "Air Contaminants; Final Rule": Federal Register 54:12 (19 Jan. 1989). pp. 2521-2523.

8.16. Occupational Safety and Health Administration Technical Center: Standard Operating Procedure - Ion Chromatography. Salt Lake City, UT. In progress (unpublished).
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