ACETOPHENONE
Method number: |
PV2003 |
|
Matrix: |
Air |
|
Target concentration: |
100 ppm |
|
Procedure: |
Samples are collected by drawing a known volume of air through a
Tenax GC tube. Samples are desorbed with a solvent mixture of 5:95
isopropanol:carbon disulfide and analyzed by gas chromatography with
a flame ionization detector. |
|
Recommended air volume and sampling rate: |
12.0 liters at 0.1 Lpm |
|
Status of Method: |
Stop gap method. This method has been only partially evaluated
and is presented for information and trial use. |
Date: 7/20/82 |
Chemist: Wayne
Potter |
Service Branch I OSHA Technical Center Salt Lake
City, Utah
1. General Discussion
1.1. Background
1.1.1. History of procedure
Recently, the OSHA Analytical Laboratory received a set of field
samples that required analysis for acetophenone. The air samples had
been collected on charcoal tubes and isopropanol impingers.
Desorption studies were done on charcoal tubes using acetone, carbon
disulfide, 5:95 isopropanol:carbon disulfide, and methylene chloride
as desorbing solvents. The best results were obtained with 5:95
isopropanol:carbon disulfide, but the recovery was only 68%, which
indicated that charcoal tubes should not be recommended for the
collection of acetophenone air samples. An evaluation of isopropanol
impingers was not performed because it was preferable to find an
adsorbent procedure for sample collection. NIOSH method 291 for
a-chloroacetophenone uses
Tenax GC tubes. The Tenax GC tubes were tried for acetophenone, and
appeared to be a suitable method of collection.
1.1.2. Toxic effects
(This section is for information only and should not be taken as
the basis of OSHA policy.)
Acetophenone is a narcotic in high concentrations (Ref. 5.1). The
oral LD50 for acetophenone in
rats is 3 g/kg. Acetophenone is reported to be capable of causing
dermatitis to humans following skin contact (Ref. 5.3). Animal data
indicates that acetophenone may cause eye irritation and possibly
transient corneal injury (Ref. 5.4).
1.1.3. Potential workplace exposure
No workplace exposure level could be found in the literature, but
acetophenone is used in the following processes: perfumery, solvent,
intermediate for pharmaceuticals, resin, polymerization catalyst,
and flavoring (Ref.5.1)
1.1.4. Physical properties (ref. 5.1)
Synonyms: |
phenyl methyl ketone; hypnone;
acetylbenzene |
Molecular weight: |
120.15 |
Density: |
1.0281 |
Flash point |
82.2°C (180°F) (COC) |
Boiling point: |
202°C |
Freezing point: |
19.7°C |
Solubility: |
slightly soluble in water, freely soluble in alcohol,
chloroform, ether, fatty oils, and glycerol. |
Description: |
Combustible, colorless liquid, with sweet, pungent odor
and taste. |
Molecular structure: |
C6H5COCH3 |
1.2. Limit defining parameters
1.2.1. Detection limit of the analytical procedure is 20.6
ng/injection. This is the amount of analyte which will give a peak
whose height is approximately five times the baseline noise.
1.2.2. Sensitivity
The sensitivity of the analytical procedure over a concentration
range of 10.28 to 1028.1 µg/mL is 407297 area units per µg/mL of
acetophenone. The sensitivity is determined by the slope of the
calibration curve. (See Figure 2.)
2. Sampling Procedure
2.1. Apparatus
2.1.1. A calibrated personal sampling pump whose flow can be
determined with ± 5% of the recommended flow.
2.1.2. Tenax GC tubes: glass tube with both ends flame sealed, 7
cm long with a 6 mm O.D. and a 4 mm I.D., containing 2 sections of
Tenax GC separated by a 2 mm portion of urethane foam. The absorbing
section contains 30 mg of Tenax GC, the backup section 15 mg. A 3 mm
portion of urethane foam is placed between the outlet end of the
tube and the backup section. A plug of silylated glass wool is
placed in front of the absorbing section.
2.2. Reagents
2.2.1. None required.
2.3. Sampling technique
2.3.1 Immediately before sampling, break the ends of the Tenax
GC tubes. All tubes must be from the same lot.
2.3.2. Connect the tube to the sampling pump with flexible
tubing. The backup section of the Tenax GC tubes should be
positioned nearer the sampling pump.
2.3.3. The tubes should be placed in a vertical position during
sampling to minimize channeling.
2.3.4. Air being sampled should not pass through any hose or
tubing before entering the Tenax GC tubes.
2.3.5. Seal the Tenax GC tubes with plastic caps immediately
after sampling. Seal each sample with official OSHA label length
wise.
2.3.6. With each batch of samples, submit at least one blank tube
from the same lot used for samples. This tube should be subjected to
exactly the same handling as the samples (break, seal, transport)
except that no air is drawn through it.
2.3.7. Transport the samples (and corresponding paperwork) to the
laboratory for analysis.
2.3.8. If bulk samples are submitted for analysis, they should be
transported in glass containers with teflon-lined caps.
These samples must not be put in the same container used for the
Tenax GC tubes.
2.4. Desorption efficiency
The average desorption efficiency from the Tenax GC tubes spiked
with 1.028 mg of acetophenone was 99.1%.
|
Average |
Sample |
Treatment |
Recovery |
Recovery |
|
1 |
No Air |
99.51 |
|
2 |
No Air |
100.99 |
99.1 |
3 |
No Air |
99.29 |
|
4 |
No Air |
98.25 |
|
5 |
No Air |
97.68 |
|
2.5. Retention efficiency
Eight Tenax GC tubes were spiked with 1.028 mg of acetophenone.
Twelve liters of dry air were drawn through four of the tubes at 0.1
Lpm. Twelve liters of humid air (about 85% relative humidity) were
drawn through the other four tubes at 0.1 Lpm.
|
Average |
Sample |
Treatment |
% Recovery |
% Recovery |
1 |
12 L Dry Air |
100.89 |
2 |
" |
99.79 |
99.3 |
3 |
" |
95.72 |
4 |
" |
99.93 |
|
5 |
12 L Humid Air |
104.50 |
6 |
" |
102.08 |
99.7 |
7 |
" |
l06.57 |
8 |
" |
85.54 |
2.6. Sample storage
Four Tenax GC tubes were spiked with 1.028 mg of acetophenone. Two
tubes were stored in a refrigerator for six days and two tubes were
stored at ambient temperature for six days.
|
Storage |
|
Average |
Sample |
Days |
Treatment |
% Recovery |
% Recovery |
|
1 |
6 |
Refrigerator |
97.95 |
2 |
6 |
" |
93.55 |
95.8 |
|
3 |
6 |
Ambient |
96.13 |
96.7 |
4 |
6 |
" |
97.22 |
2.7. Recommended air volume and sampling rate.
2.7.1. The recommended air volume is 12.0 liters.
2.7.2. The recommended sampling rate is 0.1 liters per minute.
2.8. Interferences
2.8.1. It is important to be aware of other components in the
atmosphere which may interfere with the collection of the analyte.
2.9. Safety precautions
2.9.1. Care must be taken when opening the sealed ends of the
Tenax GC tubes to avoid serious cuts to the hands.
2.9.2. Safety glasses should be worn when opening the sealed ends
of the Tenax GC tubes to avoid injury to the eyes from glass
splinters.
2.9.3. Attach the sampling equipment to the worker in such a
manner that it will not interfere with work performance of the
employee.
2.9.4. Follow all safety practices that apply to the work area
being sampled.
3. Analytical procedure
3.l. Apparatus
3.1.1. Gas chromatograph equipped with a flame ionization
detector.
3.1.2. GC column capable of separating the solvent, acetophenone
and an internal standard (n-hexylbenzene). The column used for
validation studies was: 10 ft × 1/8 inch stainless steel with 3%
2100 100/120 Supelcoport.
3.1.3. An electronic integrator or some other suitable method of
measuring peak areas.
3.1.4. Two milliliter vials with teflon-lined caps.
3.1.5. Two microliter syringes for sample injections.
3.1.6. Volumetric flasks, 5-mL and other convenient
sizes for preparing standards.
3.1.7. Pipettes for dispensing desorbing reagent. The Glenco
1-mL dispenser is adequate and convenient.
3.2. Reagents
3.2.1. Carbon disulfide, reagent grade.
3.2.2. Isopropyl alcohol, reagent grade.
3.2.3. An internal standard, such as n-hexylbenzene, reagent
grade.
3.2.4. Desorbing reagent - 1 uL internal standard/1 mL of 5% IPA
in CS2.
3.2.5. Acetophenone, reagent grade.
3.2.6. Chromatographic quality nitrogen, hydrogen, and air.
3.3. Standard preparation
3.3.l. Standard of acetophenone is prepared by injecting 5 ul of
acetophenone into a 5-mL volumetric flask of the
desorbing reagent and making it to volume.
3.3.2. A calibration curve is prepared by making dilutions with
the desorbing reagent.
3.4. Sample preparation
3.4.1 The front and back section of each sample are transferred
to separate 2-mL vials.
3.4.2. Each sample is desorbed with 1.0 mL of desorbing reagent.
3.4.3. The vials are sealed immediately and allowed to desorb for
30 minutes with occasional shaking.
3.5. Analysis
3.5.1. GC conditions
Flow rates (mL/min) |
Temperature (°C) |
Nitrogen |
- 25 |
Injector |
- 200 |
Hydrogen |
- 20 |
Detector |
- 250 |
Air |
- 300 |
Column |
- 150° |
Injection size - 2.0 ul |
Elution time - 1:4
minutes |
3.5.2. Chromatogram
See Figure 1.
3.5.3. Peak areas are measured by an integrator or other suitable
means.
3.5.4. An internal standard procedure is used. The integrator is
calibrated to report results in ppm for a 12 liter air sample after
correction for desorption efficiency.
3.6. Interferences
3.6.l. Any compound having the general retention time of the
analyte of the internal standard used is an interference. Possible
interferences should be listed on the sample data sheet. GC
parameters should be adjusted if necessary so these interferences
will pose no problems.
3.6.2. Retention time data on a single column is not considered
proof of chemical identity. Samples over the PEL should be confirmed
by GC/Mass Spec or other suitable means.
3.7. Calculations
3.7.1. The equivalent ppm air concentration of analytical
standards based on 12 liter air sample, and 1 mL desorbing solution
is calculated in the following manner:
X µg/mL (24.45) (1 mL)
(mw) (12 L) |
=
ppm |
where |
X µg/mL |
= |
concentration of the analytical standard. |
|
24.45 |
= |
Molar volume (liter/mole) at 25°C and 760 mm Hg |
|
MW |
= |
Molecular weight = 120.15 |
|
1 mL |
= |
Desorption volume |
|
12 L |
= |
12 liter air sample |
3.7.2. Since the integrator was calibrated to report results in
ppm based on 12 L air sample, the following calculation is used:
ppm analyte = |
A - C
B / 12 |
where |
A |
= |
ppm on report |
|
C |
= |
ppm on report for blank |
|
B |
= |
air volume of sample (liters) |
3.7.3. This calculation is done for each section of the sampling
tube and the results added together.
3.8. Safety precautions
3.8.l. All handling of solvents should be done in a hood.
3.8.2. Avoid skin contact with all solvents.
3.8.3. Wear safety glasses at all times.
4. Recommendations for further study
4.1. Further work should be done on breakthrough.
4.2. Longer storage tests should be performed.
Figure 1
Figure 2
A bulk sample was analyzed by gas chromatography on a Varian 3400 with
a flame ionization detector. The analysis was for % methyl carbitol,
benzaldehyde, phenol, and acetophenone, with methanol as the solvent. The
column used was a 60 M DB-1 capillary column, 80°C for 2
minutes, then 5°/minute to 180°C.
5. References
5.1. "The Condensed Chemical Dictionary", 10th ed.; Hawley, G.G.,
ed.; Van Norstrand Reinhold Company, New York, 1981; p. 9.
5.2. "The Merck Index", 9th ed.; Windholz, Martha, ed.; Merck and
Company, Inc., New Jersey, 1976; p. 9.
5.3. "Spice Mill"; Katz, A.E.; 69, 1946; p. 46.
5.4. "Journal of Industrial Hygiene Toxicology"; Smyth, H.F. Jr.,
and Carpenter, C.P.; 30, 1948; p. 63.
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