||2 ppm (6 mg/m3)
||A sample is collected by drawing air through an open face air monitoring cassette containing two glass fiber filters, each of which is coated with 2,4-dinitrophenylhydrazine and phosphoric acid. The sample is extracted with acetonitrile and analyzed by HPLC using a UV detector.
|Recommended air volume
and sampling rate:
|6 L at 0.1 L/min
|Reliable quantitation limit:
||32 ppb (93 µg/m3)
|Standard error of estimate
at the target concentration:
||Store samples at -20°C upon receipt at the laboratory. If such storage is not possible, samples must be analyzed within 9 days after collection. (Section 1.2.5) Keep the samples in the dark whenever possible as a precaution against photodecomposition.
|Status of method:
||Evaluated method. This method has been subjected to the established evaluation procedures of the Organic Methods Evaluation Branch.
|Date: April 1990
||Chemist: Warren Hendricks
Organic Methods Evaluation Branch
OSHA Analytical Laboratory
Salt Lake City, Utah
1. General Discussion
2. Sampling Procedure
This work was performed because there was no fully evaluated OSHA method for the sampling and analysis of crotonaldehyde.
Experiments performed at the OSHA Analytical Laboratory showed that crotonaldehyde could be collected directly on Carbosieve
S-III adsorbent but that recovery from samples used in an ambient temperature storage test was only 60% after just three days of storage.
An effort was made to extend the sampling method used by OSHA for the collection of acrolein and formaldehyde (Ref. 5.1) to include crotonaldehyde. The method is based on the reaction of
2-(hydroxymethyl)piperidine (2-HMP) with the aldehyde. Preliminary experiments showed that the reaction rate between crotonaldehyde and 2-HMP was not fast enough for air sampling.
The sampling device used by OSHA to monitor glutaraldehyde (Ref. 5.2) was tested to determine if it would also efficiently collect and derivatize crotonaldehyde. That method requires sample collection using glass fiber filters which have been coated with
2,4-dinitrophenylhydrazine (DNPH) and phosphoric acid. DNPH is a widely used derivatizing reagent for the determination of aldehydes and ketones. The reaction between crotonaldehyde and DNPH is presented below:
CH3CH=CHCHO + (O2N)2C6H3NHNH2
Initial laboratory experiments showed that the sampling device was effective for the collection and derivatization of crotonaldehyde. The DNPH method was evaluated and it is the basis of this method.
The analysis is performed by HPLC using UV detection. Two
crotonaldehyde-DNPH peaks are observed. The detector responses for the two peaks are added and the sum is used in subsequent calculations.
1.1.2. Toxic effects (This section is for information only and should not be taken as the basis of OSHA policy.)
Crotonaldehyde can produce toxic effects following ingestion, inhalation, and adsorption through the eyes or skin. It is an irritant to the eyes, nose, and throat. It can also cause deep lung irritation effects which are similar to, but less severe than, those of phosgene and acrolein. At least one case of sensitization has been reported. The 30-min LC50 for rats is has been reported to be as low as 600 ppm. (Refs. 5.3 and 5.4)
Crotonaldehyde has been shown to cause liver tumors in laboratory rats (Ref. 5.5).
Crotonaldehyde has been identified by the German MAK Commission as a chemical suspected of having carcinogenic potential (Ref. 5.6).
1.1.3. Workplace exposure
Crotonaldehyde can exist as either the trans or the cis isomer. Commercial crotonaldehyde is more than 95% trans isomer. The largest use for crotonaldehyde is in the manufacture of n-butanol. It is also used to produce sorbic acid, 3-methoxybutanol, and crotonic acid. Miscellaneous uses and suggested uses include: manufacture of dyestuffs, sedatives, pesticides, and flavoring agents; solvent for mineral and lubricating oils; bactericide and a warning agent in fuels; leather tanning and in preparation of tanning materials. It is also
used in the rubber and polymer industries. (Refs. 5.4 and 5.7) No data was found regarding the size of the worker population potentially exposed to crotonaldehyde.
1.1.4. Physical properties (Refs. 5.3 and 5.4)
||123-73-9 (trans isomer)
4170-30-3 (inhibited solution, usually contains about 10% water)
The following physical properties are for CAS no. 123-73-9.
||colorless, flammable liquid with a pungent odor, turns pale
yellow when exposed to air or light
||0.8531 at 20°C
||102°C at 101 kPa (760 mmHg)
||4 kPa (30 mmHg) at 20°C
||55°F (open cup)
||2.95 and 15.5% by vol. in air
||β-methylacrolein; propylene aldehyde; crotonic aldehyde; 2-butenal
The analyte air concentrations listed throughout this method are based on an air volume of 6 L and a solvent extraction volume of 3.0 mL. Air concentrations listed in ppm are referenced to 25°C and 101 kPa (760 mmHg). The analyte concentrations are listed as crotonaldehyde even though the derivative is the actual species analyzed.
1.2. Limit defining parameters
1.2.1. Detection limit of the analytical procedure
The detection limit of the analytical procedure is 2.85 ng per injection. This is the amount of crotonaldehyde which will give derivative peaks with heights about 5 times the height of the baseline noise. (Section 4.1)
1.2.2. Detection limit of the overall procedure
The detection limit of the overall procedure is 0.56 µg per sample (32 ppb or 93 µg/m3). This is the amount of crotonaldehyde spiked on the sampling device which allows recovery
of an amount of analyte equivalent to the detection limit of the analytical procedure. (Section 4.2)
1.2.3. Reliable quantitation limit
The reliable quantitation limit is 0.56 µg per sample (32 ppb or 93 µg/m3). This is the smallest amount of analyte which can be quantitated within the requirements of a recovery
of at least 75% and a precision (±1.96 SD) of ±25% or better. (Section 4.3)
The reliable quantitation limit and detection limits reported in the method are based upon optimization of the instrument for the smallest possible amount of analyte. When the target concentration of an analyte is exceptionally higher than these limits, they may not be attainable at
the routine operating parameters.
1.2.4. Instrument response to the analyte
The instrument response over the concentration range of 0.5 to 2 times the target concentration is linear. (Section 4.4)
The recovery of crotonaldehyde from samples used in an 18-day storage test remained above 75% for the first 9 days of storage when the samples were stored at about 22°C. (Section 4.5 and regression line of Figure 4.5.1). The recovery of crotonaldehyde from samples used in an 18-day storage test remained above 99% when the samples were stored at -20°C (Section 4.5).
1.2.6. Precision (analytical procedure)
The pooled coefficient of variation obtained from replicate determinations of analytical standards at 0.5, 1, and 2 times the target concentration is 0.014. (Section 4.6)
1.2.7. Precision (overall procedure)
The precision at the 95% confidence level for the 18-day ambient temperature storage test is ±14.9%. (Section 4.7) This includes an additional ±5% for pump error.
Six samples, collected from a controlled test atmosphere, were submitted to the OSHA Analytical Laboratory for analysis. The samples and a draft copy of this procedure were assigned to a chemist who was unassociated with this evaluation. No individual sample deviated from its theoretical value by more than the ±14.9% precision reported in Section 1.2.7. (Section 4.8)
This sampling and analytical procedure provides a simple and convenient means to monitor occupational exposure to crotonaldehyde.
1.4.1. Recovery of crotonaldehyde from samples used in an ambient temperature storage test fell
below 75% after 9 days of storage.
1.4.2. The coated filters are not commercially available.
3. Analytical Procedure
2.1.1 Samples are collected by use of a personal sampling pump that can be calibrated to within ±5% of the recommended flow rate with the sampling device in line.
2.1.2. A sample is collected using an open face air monitoring cassette containing 2 glass fiber filters. The filters are separated and retained using cassette center sections (Figure 4.11). Each filter is coated with DNPH and phosphoric acid. Instructions for the preparation of the coated filters and assembly of the sampler are given in Section 4.11 of this method.
No sampling reagents are required.
2.3.1. Remove the inlet section (cover) and the end plug on the exit section of the air monitoring cassette so that sampling is performed open face.
2.4. Sampler capacity
2.3.2. Attach the sampling device to the sampling pump with flexible, plastic tubing such that the front filter of the sampler is exposed directly to the atmosphere.
2.3.3. Attach the open face air monitoring cassette vertically (face down) in the worker's breathing zone in such a manner that it does not impede work performance or safety.
2.3.4. Remove the sampling device after sampling for the appropriate time. Replace the inlet section (cover) and the end plug on the exit section of the air monitoring cassette. Wrap the sample end-to-end with an official OSHA seal (Form 21).
2.3.5. Ship samples to the laboratory within a day after collection or store them at -20°C (about 0°F) until shipment. Samples do not require refrigerated shipment under normal circumstances. Keep the samples in the dark whenever possible as a precaution against
2.3.6. Submit at least one blank with each set of samples. The blank should be handled the same as the other samples except that no air is drawn through it.
2.3.7. List any potential interferences on the sample data sheet.
2.4.1. Sampler capacity was evaluated by sampling controlled test atmospheres with several of the recommended sampling devices for increasing periods of time. Percent breakthrough was measured as the amount of crotonaldehyde found on the back filter relative to the total
amount collected on the entire sampling device. Five-percent breakthrough was used as evidence of saturation of the front filter. The crotonaldehyde content of the test atmospheres was 12
mg/m3 and the relative humidity was 76% at 26°C. Five-percent breakthrough was determined to occur after sampling for 87 min at 0.1 L/min. (Section 4.9)
2.5. Extraction efficiency
2.4.2. An additional sampler capacity experiment was performed at reduced relative humidity to determine if low humidity had an effect on capacity. Five samples were collected for 1 h at 0.1 L/min from a controlled test atmosphere containing 12 mg/m3 of crotonaldehyde
at 36% relative humidity and 26°C. The average amount of crotonaldehyde recovered from the five samples was 97% of theoretical and the average breakthrough was 0.2%.
2.5.1. The extraction efficiency for crotonaldehyde from DNPH coated glass fiber filters at the target concentration was 96.6%. (Section 4.10)
2.6. Recommended air volume and sampling rate
2.5.2. Extracted samples remain stable for at least 16 h. (Section 4.10)
2.6.1. For long-term samples, collect 6 L at 0.1 L/min.
2.7. Interferences (sampling)
2.6.2. For short-term samples, collect 1.5 L at 0.1 L/min.
2.6.3. When short-term samples are required, the reliable quantitation limit becomes larger. For example, the reliable quantitation limit is 130 ppb (373 µg/m3) for crotonaldehyde when
1.5 L of air is collected.
2.7.1. Any substance, present in the sampled air, that is capable of reacting with DNPH and thereby depleting the derivatizing reagent is a potential interference. Many aldehydes and ketones are capable of reacting with DNPH.
2.8. Safety precautions (sampling)
2.7.2. Suspected interferences should be reported to the laboratory with submitted samples.
2.8.1. Attach the sampling equipment to the worker in such a manner that it will not interfere with work performance or safety.
2.8.2. Follow all safety practices that apply to the work area being sampled.
4. Backup Data
3.1.1. A high-performance liquid chromatograph (HPLC) equipped with a UV detector and a manual or automatic sample injector. The following Waters Associates equipment was used in this evaluation: a Model 6000A HPLC pump, a Model 440 UV detector, and a WISP 710B automatic sample injector.
3.1.2. An HPLC column capable of resolving the crotonaldehyde-DNPH derivative from interferences. Either a DuPont Zorbax CN column (4.6-mm i.d. × 25 cm) or a J.T. Baker Bakerbond CN column (4.6-mm i.d. × 25 cm) can be used. Both columns were used in this evaluation.
3.1.3. An electronic integrator or some other suitable means to measure detector response. A Hewlett-Packard Model 3357 Data System was used in this evaluation.
3.1.4. Vials, 4-mL glass with Teflon-lined septum caps.
3.1.5. Volumetric flasks, pipets and syringes for preparing standards, making dilutions and performing injections.
3.1.6. Pipets, disposable, Pasteur-type.
3.1.7. A tube rotator or other suitable means to agitate the samples during extraction. A Fisher Roto-Rack tube rotator was used for this evaluation.
3.2.1. Acetonitrile, HPLC grade. American Burdick and Jackson acetonitrile UV was used in this evaluation.
3.3. Standard preparation
3.2.2. Water, HPLC grade. Water from a Millipore Milli-Q water filtration system was used in this evaluation.
3.2.3. Phosphoric acid, reagent grade. "Baker Analyzed" Reagent grade 85% phosphoric acid was used in this evaluation.
3.2.4. Crotonaldehyde. Aldrich Chemical Company, predominately trans, 99+% Gold Label grade crotonaldehyde, lot no. 06226CT, was used in this evaluation.
3.2.5. 2,4-Dinitrophenylhydrazine (DNPH). DNPH (70%), lot no. 1707LJ, was obtained from Aldrich Chemical Company and was recrystallized from hot acetonitrile for use in this evaluation.
3.2.6. Analytical standard preparation solution. This solution is prepared by diluting 0.33 g of recrystallized DNPH and 0.9 mL of phosphoric acid to 250 mL with acetonitrile.
3.3.1. Prepare analytical standards about 24 h before the air samples are to be analyzed so that the ratio of the crotonaldehyde-DNPH isomers can equilibrate. Do not reduce the equilibration time. As a precaution against photo-decomposition, standards and samples should be kept in the dark whenever possible.
3.4. Sample preparation
3.3.2. Prepare crotonaldehyde stock standard solutions by diluting 99% crotonaldehyde with acetonitrile. A standard containing 3.35 mg/mL of crotonaldehyde was prepared by diluting 169.2 mg of the 99% material to 50 mL with acetonitrile.
3.3.3. Place 3.0-mL aliquots of analytical standard preparation solution (Section 3.2.6) into each of several 4-mL glass vials. Seal each vial with a Teflon-lined septum cap.
3.3.4. Prepare analytical standards by injecting appropriate volumes of crotonaldehyde stock standard solutions (Section 3.3.2) into the sealed 4-mL vials. A standard containing 33.5 µg of crotonaldehyde was prepared by injecting 10 µL of the
3.35-mg/mL crotonaldehyde solution into a vial containing 3.0 mL of analytical standard preparation solution. This standard was approximately equivalent to a 2 ppm air sample.
3.3.5. Prepare a sufficient number of standards to generate a calibration curve. Analytical standard concentrations must bracket sample concentrations.
3.4.1. Open the air monitoring cassette and remove the front coated filter. Transfer the filter to a 4-mL glass vial. Do not fold, wad, or crumple the filter. Place the back filter in a separate vial.
3.4.2. Add 3.0 mL of acetonitrile to each vial.
3.4.3. Seal the vials with Teflon-lined septum caps and place them on the tube rotator. Rotate the samples for 1 h at 60 rpm. Samples do not require the 24-h equilibration time as do standards.
3.5.1. HPLC conditions
3.6. Interferences (analytical)
Standards have approximately a 1 to 1 ratio of the two derivative peaks following the required 24 h equilibration time. Air samples may contain predominantly the 9.2 min peak depending on their storage history.
||J.T. Baker Bakerbond CN, 25 cm × 4.6-mm i.d.
||40% acetonitrile in water containing 0.1% phosphoric acid (v/v/v)
||6.5 and 9.2 min
3.5.2. A chromatogram at the target concentration is shown in Figure 3.5.2.
3.5.3. Use a suitable method such as electronic integration to measure detector response (peak areas or heights).
3.5.4. Program the integrator to add the detector responses of the two crotonaldehyde-DNPH isomer peaks together.
3.5.5. Prepare a calibration curve by plotting the summed integrator result for each standard solution against its respective actual concentration (in micrograms per standard). Determine the
best-fit line through the data points by curve fitting. Sample results must be bracketed by standard concentrations.
3.6.1. Any compoud having a similar retention time as the crotonaldehyde-DNPH derivatives is a potential interference.
3.6.2. HPLC parameters (mobile phase composition, column, analytical wavelength, etc.) may be changed to circumvent interferences.
3.6.3. Retention time on a single column is not proof of chemical identity. Analysis using an alternate HPLC column, detection at another wavelength, comparison of absorbance response ratios, and structure determination by mass spectrometry are additional means of identification.
3.7.1. The concentration (micrograms of crotonaldehyde per sample) of samples is determined from the calibration curve. If crotonaldehyde is found on the back filter, it is added to the amount found on the front filter. Blank corrections should be performed before adding the results together.
3.8. Safety precautions (analytical)
3.7.2. The crotonaldehyde air concentration can be expressed using the following equation:
mg/m3 = A / (B)(E)
||µg/sample from Section 3.7.1.
||liters of air sampled
||extraction efficiency (decimal form)
3.7.3. The following equation can be used to convert crotonaldehyde results in mg/m3 to ppm at 25°C and 101 kPa (760 mmHg):
ppm = (mg/m3)(24.46) / 70.l
||result from Section 3.7.2.
||molar volume at 101 kPa (760 mmHg) and 25°C
||molecular weight of crotonaldehyde
3.8.1. Avoid skin contact and inhalation of all chemicals.
3.8.2. Restrict the use of all chemicals to a fume hood.
3.8.3. Wear safety glasses and a lab coat in all lab areas.
4.1. Detection limit of the analytical procedure
The injection size recommended in the analytical procedure (15 µL) was used to determine the detection limit of the analytical procedure. The detection limit of the analytical procedure was 2.85 ng per injection. This was the amount of crotonaldehyde that gave derivative peaks with heights about 5 times the height of the baseline noise. This detection limit was determined by the analysis of a standard containing 0.187 µg/mL crotonaldehyde. Figure 4.1 is a chromatogram of the detection limit of the analytical procedure.
4.2. Detection limit of the overall procedure
The detection limit of the overall procedure is 0.56 µg per sample (32 ppb or 93 µg/m3). The injection size recommended in the analytical procedure (15 µL) was used in the determination of the detection limit of the overall procedure. Six vials, each containing a coated glass fiber filter, were each liquid spiked with 0.56 µg of crotonaldehyde. The samples were extracted about 16 h after being spiked.
Detection Limit of the Overall Procedure
4.3. Reliable quantitation limit data
The reliable quantitation limit is also 0.56 µg per sample (32 ppb or
93 µg/m3). The injection size
recommended in the analytical procedure (15 µL) was used in the determination of the reliable quantitation limit. Because the recovery of crotonaldehyde from spiked samples (Section 4.2) was greater than 75% and also because the precision (±1.96 SD) was less than ±25%, the detection
limit of the overall procedure and reliable quantitation limit are the same.
Reliable Quantitation Limit
(based on samples and data of Table 4.2.)
4.4. Instrument response to crotonaldehyde
The instrument response to crotonaldehyde over the range of 0.5 to 2 times the target concentration is linear with a slope of 117361 area counts per microgram per milliliter. The response to crotonaldehyde was determined by multiple injections of standards. The data in Table 4.4. is presented graphically in Figure 4.4.
Instrument Response to Crotonaldehyde
|× target concn
4.5. Storage test
Eighteen samples were collected on each of two consecutive days by sampling test atmospheres containing an average of 6.5 mg/m3 crotonaldehyde for 1 h at 0.1 L/min. The average relative humidity of the atmospheres was 80% at 25°C. Eighteen of the samples were stored in a freezer at
-20°C and the other eighteen were stored in the dark at ambient temperature (about 22°C). Every few days, three samples were
selected from each of the two storage sets and analyzed. The storage data are also presented graphically in Figures 4.5.1 and 4.5.2.
4.6. Precision (analytical method)
The precision of the analytical procedure is defined as the pooled coefficient of variation determined from replicate injections of crotonaldehyde standards at 0.5, 1, and 2 times the target concentration.
Precision of the Analytical Method
(based on the data of Table 4.4.)
|× target concn
| = 0.014
1 standard deviation is in area counts
4.7. Precision (overall procedure)
The precision of the overall procedure is determined from the storage data. The determination of the standard error of estimate (SEE) for a regression line plotted through the graphed storage data allows the inclusion of storage time as one of the factors affecting overall precision. The SEE is similar to the standard deviation except it is a measure of dispersion of data about a regression line instead of about a mean. It is determined with the following equation:
|Σ(YOBS - YEST)2
|n - k
total no. of data points
2 for linear regression
3 for quadratic regression
||observed % recovery at a given time
||estimated % recovery from the regression line at the same given time
An additional ±5% for pump error is added to the SEE by the addition of variances. The precision at the 95% confidence level is obtained by multiplying the SEE (with sampling error included) by 1.96 (the
z-statistic from the standard normal distribution at the 95% confidence level). The 95% confidence intervals are drawn about their respective regression lines in the storage graphs as shown in Figure 4.5.1. The data for Figure 4.5.1. was used to determine the SEE of ±7.6% for crotonaldehyde.
Six samples, collected from a controlled test atmosphere were assigned to a chemist unassociated with this study. The samples were stored at ambient temperature for three days before submission to the laboratory for analysis. The intent of the delay was to simulate sample shipment from the
field to the laboratory. The samples were analyzed after 47 days of additional storage at about -20°C. The sample results are corrected for extraction efficiency.
No sample result had a percent deviation greater than the precision of the overall procedure, which was ±14.9%.
4.9. Sampler capacity
Sampler capacity was evaluated by sampling controlled test atmospheres with several of the recommended sampling devices for increasing periods of time. The crotonaldehyde content of the test atmospheres was 12 mg/m3 and the relative humidity was 76% at 26°C. Percent breakthrough was measured as the relative amounts of crotonaldehyde collected on the front and back filters of the sampling device. Five-percent breakthrough was defined to occur when 5% of the total amount of crotonaldehyde collected on the entire sampling device was found on the back filter. Five-percent breakthrough was graphically determined to occur after sampling for 87 min at 0.1 L/min. The results of the breakthrough test are also presented in Figure 4.9.
Sampler Capacity Data
4.10. Extraction efficiency and stability of extracted samples
The extraction efficiency for crotonaldehyde was determined by liquid spiking each of six DNPH coated glass fibers contained in separate glass vials with 20 µL of a solution containing 1.675 mg/mL of crotonaldehyde in acetonitrile. These samples were stored at room temperature for 1 h
and then extracted and analyzed. The average extraction efficiency was 96.6%. Following the initial analysis, the samples were immediately resealed and reanalyzed about 16 h later using freshly prepared standards. The average of the reanalyzed samples was 97.8% of the original analysis.
4.11. Procedure to coat glass fiber filters with DNPH/phosphoric acid and assembly of the sampling device
4.12. Generation of controlled test atmospheres
220.127.116.11. Miscellaneous glassware: 250-mL volumetric flask, 30-, 50-, and 150-mL beakers, pipets, etc.
18.104.22.168. Plastic air monitoring cassettes, for 37-mm diameter filters.
Unassembled 3-piece cassettes and extra center support sections were obtained from Millipore for use in this evaluation.
22.214.171.124. Acetonitrile, HPLC grade. American Burdick and Jackson acetonitrile UV was used in this evaluation.
126.96.36.199. 2,4-Dinitrophenylhydrazine (DNPH). DNPH (70%), lot No. 1707 LJ,
obtained from Aldrich Chemical Company, was recrystallized from hot
acetonitrile for use in this evaluation.
188.8.131.52. Glass fiber filters, 37-mm diameter Gelman Sciences Type A glass fiber filters, lot No. 8318, were used in this evaluation.
184.108.40.206. Phosphoric acid, reagent grade. "Baker analyzed" Reagent grade 85% phosphoric acid was used in this evaluation.
220.127.116.11. DNPH/phosphoric acid solution. Prepare this solution by diluting 2 g of recrystallized DNPH and 5 mL of 85% phosphoric acid to 250 mL with
(CAUTION! Evaporation of acetonitrile must be performed in a fume hood.)
Place a glass fiber filter on a 30-mL beaker, or some other suitable support, so that only the outside edge of the filter is supported. Pipet 0.5 mL of the DNPH solution (Section 18.104.22.168) onto the surface of the filter. Make sure that the filter is completely saturated with the solution. Allow the acetonitrile to evaporate. Store prepared filters in a tightly sealed container at -20°C. Filters prepared and stored as described remain usable for at least a month.
Assemble the sampling device by placing a coated filter in the outlet section of the air monitoring cassette. Next, place a center support section on the first filter. Now, put another coated filter on the center support section and another center support section on top of that filter. Complete the assembly by placing the inlet section on the center support
section. Plug the outlet and inlet openings with plastic end plugs. An exploded view of the air sampler is shown in Figure 4.11. Put the air sampler on a table top with the outlet section down. Press on the top of the air sampler with sufficient force to seal the cassette. Use masking tape or shrink bands to further seal the two center and the outlet sections of the cassette. Store the assembled air sampler at reduced temperature (if possible) when there is a delay of more than a day or two before sampling.
The controlled test atmospheres which were used in this evaluation were generated by pumping a crotonaldehyde/water solution into a heated glass manifold with a Sage Instruments Model 355 Syringe Pump. The crotonaldehyde/water solution was volatilized and then diluted with heated air. The dilution air was metered into the heated glass manifold using a precision, calibrated rotameter. The air was humidified, if desired, by passing it through a water bubbler prior to its entering the heated glass manifold. The water bubbler was contained in a
temperature-controlled water bath. The relative humidity of the dilution air could be varied by changing the temperature of the water
bath. If dry dilution air was required, the water bubbler was not used. The relative humidity of the test atmosphere was nionitored, after mixing, with a YSI Model 91 Dew Point Hygrometer. The test atmosphere passed
through a manifold from which samples could be collected.
The crotonaldehyde concentration of the test atmosphere was adjusted to the desired level by varying the aldehyde concentration of the crotonaldehyde/water solution.
5.1. "OSHA Analytical Methods Manual"; U.S. Department of Labor, Occupational Safety and Health Administration; OSHA Analytical Laboratory: Salt Lake City, UT, 1985; Method 52; American Conference of Governmental Industrial Hygienists (ACGIH): Cincinnati, ISBN: 0-936712-66-X.
5.2 Hendricks, W. "OSHA Method No. 64; Glutaraldehyde" OSHA Analytical Laboratory, unpublished, Salt Lake City, UT 84165, June 1987.
5.3. "Documentation of the Threshold Limit Values and Biological Indices", 5th ed.; American Conference of Governmental Industrial Hygienists (ACGIH): Cincinnati, ISBN: 0-036712-68-6, 1986; p 149.
5.4. "NIOSH/OSHA Occupational Health Guidelines for Chemical Hazards", U.S. Dept. of Health and Human Services, Public Health Services, Center for Disease Control, NIOSH and U.S. Dept. of Labor, OSHA: U.S. Government Printing Office Washington, DC, Jan 1981, Crotonaldehyde, DHHS (NIOSH) Publ. No. 81-123.
5.5. Chung, F.; Tanaka, T.; and Hecht, S. Cancer Res. 1986, 46, 1285-1289.
5.6. "Appendix to the Documentation of the Threshold Limit Values and Biological Indices", 5th ed.; American Conference of Governmental Industrial Hygienists (ACGIH): Cincinnati, ISBN: 0-036712-68-6, 1986; p A-5(86).
5.7. Baxter, W. In "Kirk-Othmer Encyclopedia of Chemical Technology", 3rd ed.; Grayson, M., Ed.; John Wiley & Sons, New York, 1979, Vol. 7, pp 207-218.