1. General Discussion
1.1 Background
1.1.1 History of procedure over the
past several years the OSHA Laboratory has received requests to
analyze samples for "trimethylbenzene". These have primarily been air
samples collected on charcoal. Since several related aromatic
compounds are routinely collected on charcoal, desorbed with carbon
disulfide, and analyzed by gas chromatography, it was decided to try
the same with all three trimethylbenzenes. The three isomers are
1,2,3-, 1,2,4-, and 1,3,5-trimethylbenzene.
1.1.2 Toxic Effects
(This section is for information purposes and should not be taken as
the basis for OSHA policy.) Both the 1,2,4- and the 1,3,5- isomers are
(Ref 5.1) highly toxic by inhalation and by ingestion. Both are skin
and eye irritants. Both isomers are central nervous system depressants
and may cause respiratory disorders. The 1,2,4-isomer may also be
narcotic. Other effects of exposure to these compounds include
headache, tension, nervousness, inflammation and hemorrhaging of
mucous membranes, convulsions and ultimately death. No specific
information about the toxic effects of the 1,2,3-isomer was
available.
1.1.3. Potential workplace exposure: (Ref.
5.2)
1,2,4-Trimethylbenzene is used as a chemical intermediate
in the manufacture of trimellitic anhydride, pseudocumidine and
various dyes and pharmaceuticals. 1,3,5-Trimethylbenzene is used
as an intermediate in the production of anthraquinone vat dyes and
ultraviolet oxidation stabilizers for plastics. 1,2,3-Trimethylbenzene
is a precursor for a musk. 1,2,4-Trimethylbenzene is produced at about
22,500 tons/year in the United States. 'The other Trimethylbenzenes
are produced at much lower rates.
1.1.4 Physical
properties: (Ref. 5.3)
Compound: |
1,2,3 Trimethylbenzene |
1,2,4 Trimethylbenzene |
1,3,5 Trimethylbenzene |
Molecular Weight: |
120.186 (all isomers) |
|
Density: |
0.8944 |
0.8758 |
0.8652 |
Freezing Point: |
-25.37°C |
-43.8°C |
-44.7°C |
Boiling Point: |
176.1°C |
169.35°C |
164.7°C |
Odor: |
Characteristic of aromatic
hydrocarbons. |
Color: |
Each is a clear
liquid. |
Molecular Formula: |
C8H12 |
|
|
Flash Point (Tag closed cup): |
51°C |
46°C |
44°C |
CAS Number: |
526-73-8 |
96-63-6 |
108-67-8 |
IMIS Number: |
T205 |
T306 |
T407 |
|
(2505 for mixture of all
three) |
Structure: |
|
|
| 1.2 Limit
defining parameters
1.2.1 The detection limit of the
analytical procedure is 2 ng/injection for each isomer. This is the
smallest amount of analyte which will produce a peak height 5 times
the baseline noise.
1.2.2 The detection limit of the overall
procedure is 1 µg/sample for each isomer, assuming a 1 mL sample
volume, a 2 µL injection volume and nearly 100% retention and
desorption efficiencies. 1.3
Advantages
1.3.1 The sampling procedure is
convenient for both the industrial hygienist and the employee being
sampled.
1.3.2 No reagents and only a small amount of apparatus
are required for sampling.
1.3.3 Samples are convenient to
ship.
1.3.4 The analytical method is reproducible, sensitive
and does not require extensive handling of samples or
standards.
1.3.5 It is possible to analyze at the same time
other analytes which are collected and desorbed by the same procedure
and which are separable from the trimethylbenzenes by gas
chromatography, through the proper choice of column and GC
parameters.
1.3.6 Samples can be reanalyzed if
necessary. 1.4
Disadvantages
None were encountered during these studies.
2. Sampling procedure
2.1 Apparatus
2.1.1 A calibrated personal sampling
pump, the flow of which can be determined within ±5% at the
recommended flow.
2.1.2 Charcoal tubes: glass tube with both
ends flame sealed, 7 cm long with a 6mm O.D., and a 4 mm I.D.,
containing 2 sections of 20/40 mesh charcoal separated by a 2-mm
portion of urethane foam. The front section contains 100 mg of
charcoal, the backup section contains 50 mg. A plug of silane treated
glass wool is placed ahead of the front section and a 3-mm portion of
urethane foam is placed behind the backup section
2.2 Sampling technique
2.2.1 The ends of the tube are opened
immediately before sampling.
2.2.2 Connect the backup end of
the tube to the sampling pump with flexible tubing.
2.2.3 Tubes
should be placed in a vertical position to minimize
channeling.
2.2.4 Air being sampled should not pass through any
hose or tubing before entering the charcoal tube.
2.2.5 Place
plastic caps on each end of the tube immediately after sampling. Wrap
each sample lengthwise with OSHA Form-21.
2.2.6 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 ends, seal, & transport) except that no air is
drawn through it.
2.2.7 Send the samples (and corresponding
paperwork) to the laboratory for analysis.
2.2.9. If any bulk
samples are submitted for analysis they must be shipped in a separate
container from the air samples and blanks. 2.3 Desorption and/or Extraction
efficiency
Eighteen charcoal tubes and a blank were studied. Six
tubes were injected with 2.8 µL each of a 1/1/1 mixture (v/v/v) of the
isomers. The mixture was then diluted 9:1 (v/v) with carbon disulfide.
Each of six tubes were injected with 7.0 µL of this dilution and six
more tubes were injected with 1.4 µL. The tubes were refrigerated about
18 hours and then desorbed with 1 mL of 0.1% (v/v) n-hexylbenzene in
carbon disulfide. The following results were obtained.
TABLE
1 |
|
1,2,3-isomer 0.835 mg Spike |
1,2,4-isomer 0.817 mg Spike |
1,3,5-isomer 0.808 mg Spike |
|
1. |
92.340% |
94.693% |
96.797% |
2. |
95.651 |
98.666 |
101.239 |
3. |
92.228 |
94.662 |
96.857 |
4. |
95.944 |
98.477 |
100.566 |
5. |
90.102 |
92.432 |
94.375 |
6. |
90.986 |
93.591 |
95.868 |
Ave S.D. |
92.875% 2.412 |
95.420% 2.579 |
97.617% 2.707 |
|
|
1,2,3-ismoer 0.209 mg |
1,2,4-isomer 0.204 mg |
1,3,5-isomer 0.202 mg |
|
1. |
112.688% |
117.076% |
119.648% |
2. |
108.328 |
112.740 |
115.000 |
3. |
108.436 |
110.928 |
113.664 |
4. |
109.288 |
111.916 |
114.168 |
5. |
114.040 |
116.872 |
119.832 |
6. |
108.992 |
112.048 |
114.780 |
Ave S.D. |
110.295% 2.441 |
113.597% 2.680 |
116.182% 2.796 |
|
|
0.0417 mg |
0.0409 mg |
0.0404 mg |
|
1. |
111.440% |
117.560% |
116.160% |
2. |
102.680 |
110.400 |
106.900 |
3. |
106.320 |
114.700 |
111.580 |
4. |
107.060 |
111.300 |
113.420 |
5. |
110.680 |
116.160 |
115.920 |
6. |
112.360 |
119.760 |
119.860 |
Ave S.D. |
108.423% 3.714 |
114.980% 3.619 |
113.973% 4.456 | 2.4 Retention efficiency
A retention efficiency
study of six tubes, each injected with 2.8 µL of the 1/1/1 (v/v/v)
isomer mixture, and a blank was then performed. Each tube was exposed to
a 0.1 L/min flow of air of approximately 83% relative humidity at 23°C
for 100 minutes, corresponding to an air volume of about 10 L. These
data were obtained:
TABLE
2 |
|
1,2,3-isomer 0.835 mg Spike |
1,2,4-isomer 0.817 mg Spike |
1,3,5-isomer 0.808 mg Spike |
|
1. |
91.460% |
94.057% |
96.082% |
2. |
92.463 |
94.843 |
96.980 |
3. |
95.020 |
97.714 |
100.132 |
4. |
92.840 |
95.257 |
97.404 |
5. |
91.945 |
94.316 |
97.021 |
6 |
92.648 |
94.505 |
>96.544 |
Ave. |
92.648% |
95.115% |
97.3605% | These averages were nearly identical to desorption
efficiencies for the same loading of the corresponding isomers. Water
vapor appears to have very little effect in dislodging trimethylbenzene
from activated charcoal.
2.5. Storage
Two sets of six
samples, each injected with 1.4 µL of the isomer mixture, and one blank,
were prepared and stored under refrigeration for three days. One set was
exposed to humid air as was done with the retention study samples while
the other set was not. There was no loss on storage.
TABLE
3 |
No Air Drawn |
|
|
|
1,2,3-isomer 0.417 mg Spike |
1,2,4-isomer 0.409 mg Spike |
1,3,5-isomer 0.404 mg Spike |
|
1. |
90.762% |
93.722% |
95.996% |
2. |
91.360 |
94.332 |
96.504 |
3. |
93.198 |
96.270 |
98.384 |
4. |
91.878 |
95.216 |
97.476 |
5. |
95.754 |
99.244 |
101.642 |
6. |
90.672 |
92.150 |
95.668 |
Ave. |
92.271% |
95.156% |
97.612 |
|
Humid Air Drawn |
|
|
|
1,2,3-isomer 0.417 mg |
1,2,4-isomer 0.409 mg |
1,3,5-isomer 0.404 mg |
|
1. |
91.726% |
93.598 |
96.276 |
2. |
92.750 |
96.595 |
99.209 |
3. |
96.309 |
99.930 |
102.286 |
4. |
99.050 |
102.286 |
105.060 |
5. |
94.915 |
97.717 |
100.458 |
6. |
93.965 |
96.911 |
99.544 |
Ave. |
94.786% |
97.896% |
100.472% | 2.6 Air volume and sampling rate studied
2.6.1 The air volume studied is 10
L.
2.6.2 The sampling rate studied is 0.1 liters per
minute. 2.7 Suspected
interferences should be listed on sample data sheets.
2.8 Safety
precautions
2.8.1 Sampling equipment should be
placed on an employee in a manner that does not interfere with work
performance or safety.
2.8.2 Safety glasses should be worn at
all times.
2.8.3 All safety procedures that apply to the
workplace being sampled should be followed.
3. Analytical
Method
3.1 Apparatus
3.1.1 Gas chromatograph equipped with
a flame ionization detector.
3.1.2 GC column capable of
separating the solvent, an internal standard and three
trimethylbenzenes from each other and from any
interferences.
3.1.3 An electronic integrator or some other
suitable means of measuring detector response.
3.1.4
Two-milliliter vials with Teflon-lines caps.
3.1.5.A syringe of
2 µL or other convenient size for sample injection.
3.1.6 A
repipet for accurately dispensing a known volume of desorbing solution
to all the samples. In this work a 1 mL Glenco dispenser was
used.
3.1.7 A syringe of 10 µL or other convenient size to
inject pure standards into volumetric flasks.
3.1.8 Volumetric
flasks of 5 mL or other convenient size in which to prepare
standards. 3.2
Reagents
3.2.1 Nitrogen, hydrogen and oxygen of
GC grade purity.
3.2.2 Carbon disulfide, reagent
grade.
3.2.3 An internal standard, which elutes after the
analytes and their most likely contaminants. Reagent grade
n-hexylbenzene seems to be the best choice.
3.2.4 Analytes,
reagent grade. 1,2,4-and 1,3,4-trimethylbenzene are readily
available at 99% purity each. However, there seems to be a
problem in obtaining 1,2,3-trimethylbenzene above 90X purity. It
appears to contain significant amounts of the 1,2,4-isomer as well as
other aromatic compounds. 3.3
Standard preparation
3.3.1 Standards of the
trimethylbenzenes are prepared by injecting a known volume of each
isomer, usually 5 µL, into a volumetric flask, usually 5 mL, partly
filled with the desorbing solution (carbon disulfide plus internal
standard), then filling the flask to the mark and mixing the analytes
with the desorbing solution by a few successive inversions of the
flask.
3.3.3 By preparing standards of various concentrations
and running them, a calibration curve may be prepared.
3.3.4 At
least two initial standards which are theoretically equal and are
within ±5% agreement must be prepared and run. 3.4 Sample preparation
3.4.1 The front and back sections of
charcoal from each tube are transferred to separate
vials.
3.4.2 To each vial is added 1mL of
desorbant.
3.4.3 Each vial is sealed immediately and allowed to
desorb for 30 minutes with occasional shaking. 3.5 Analysis
3.5.1 Gas chromatographic
conditions
Injection size : 2.0
µL
Injector temperature: 200°C
Nitrogen flow rate: 25
mL min.
Detector temperature: 250°C
Hydrogen flow
rate: 40 mL min.
Air : 300 mL/ min.
Detector: Flame
ionization
Column: 101 × 1/811 FFAP/Chrom. WAW
Oven
Program: 120°C/6 min, 5°C increase /min, 150°C/5
min
Attenuation: 7²
Instrument: Hewlett-Packard
5840
Elution times:
1,3,5-trimethylbenzene: 5.37
min.
1,2,4-trimethylbenzene: 6.30
min.
1,2,3-trimethylbenzene: 7.82 min.
n-hexylbenzene
(ISTD): 12.70 min. 3.5.2
Chromatogram
3.5.3
Detector response is measured by electronic integration of peak areas
or other suitable means.
3.5.4 An internal standard is used to
compensate for small differences in injection sizes. The integrator is
calibrated in ppm for a 10L air volume after correction for desorption
efficiency.
3.5.5 Precision
A precision study, involving
six injections each of standards at four, twice, once, one-half, and
one-tenth of the target concentration was performed.
TABLE 4 |
4X Target |
|
|
|
1,2,3-isomer 0.835 mg/mL |
1,2,4-isomer 0.817 mg/mL |
1,3,5-isomer 0.808 mg/mL |
|
1. |
101.743 |
100.917 |
100.548 |
2. |
99.833 |
99.549 |
99.303 |
3. |
99.833 |
99.334 |
99.092 |
4. |
99.621 |
98.800 |
94.411 |
5. |
98.127 |
97.906 |
97.605 |
6. |
98.131 |
97.875 |
97.640 |
ave. S.D. C.V |
99.513 1.336 1.343 |
99.064 1.146 1.157 |
98.766 1.124 1.138 |
|
2X Target |
|
|
|
1,2,3-isomer 0.417 mg/mL |
1,2,4-isomer 0.409 mg/mL |
1,3,5-isomer 0.404 mg/mL |
|
1. |
48.554 |
48.122 |
84.195 |
2. |
48.772 |
48.892 |
48.728 |
3. |
49.189 |
49.386 |
49.198 |
4. |
48.952 |
48.638 |
48.766 |
5. |
48.769 |
48.808 |
48.703 |
6. |
48.905 |
49.046 |
48.962 |
ave. S.D. C.V. |
48.845 0.221 0.454 |
48.815 0.424 0.868 |
48.759 0.334 0.684 |
|
1X Target |
|
|
|
1,2,3-isomer |
1,2,4-isomer |
1,3,5-isomer |
|
1. |
24.309 |
24.168 |
24.095 |
2. |
24.356 |
24.269 |
24.179 |
3. |
24.186 |
24.089 |
23.988 |
4. |
24.169 |
24.113 |
24.016 |
5. |
24.323 |
24.289 |
24.153 |
6. |
24.280 |
24.217 |
24.052 |
ave. S.D. C.V. |
24.270 0.076 0.314 |
24.191 0.082 0.338 |
24.080 0.076 0.315 |
|
0.1X Target |
|
|
|
1,2,3-isomer 0.0417 mg/mL |
1,2,4-isomer 0.0409 mg/mL |
1,3,5-isomer 0.0404mmg/mL |
|
1. |
3.298 |
3.407 |
3.257 |
2. |
3.312 |
3.446 |
3.253 |
3. |
3.293 |
3.422 |
3.247 |
4. |
3.684 |
3.711 |
3.535 |
5. |
3.679 |
3.867 |
3.604 |
6. |
3.645 |
3.742 |
3.559 |
ave. S.D. C.V. |
3.485 0.202 5.804 |
3.599 0.198 5.508 |
3.409 0.173 5.082 | 3.6 Interferences
3.6.1 Any compound which produces a
peak which partially or completely overlaps a peak produced by an
analyte or the internal standard is an analytical
interference. Possible interferences should be listed on the
sample data sheet. GC parameters should be adusted in whatever way
necessary to eliminate any such interference.
3.6.2 Since the
title compounds are most frequently derived from coal tar naphthas,
other alkylated benzenes, styrenes and cycloalkylated benzenes which
have similar boiling points and/or molecular formulae may be
interferences. Many such compounds are theoretically possible, but
relatively few are available in a high degree of purity.
3.6.3
Retention time data on a single column does not alone prove chemical
identity. Samples over the target concentration must be confirmed by
GC/Mass Spec or other conclusive means. 3.7 Calculations
3.7.1 To calculate the ppm of analyte,
based on a 10 L air volume. and a 1 mL desorption volume, in
standards.
ppm = |
1 µL/mL
× 1 mL × p × 24.46 × 1000 L
10 L × 1 m³ × DE MW | 24.46 = # liters/mole of any gas at 25°C and 760
mmHg. MW = molecular weight p = Density of
analyte 1 mL = Recommended desorption volume 10 L =
Assumed air volume DE = Desorption efficiency
3.7.2
Printed values for samples are calculated by:
actual ppm = |
printout - printout blank
(acutal air volume) / 10 L | 3.8 Safety precautions
3.8.1 All solvents should be handled
in a hood.
3.8.2 Skin contact with any solvent is to be
avoided.
3.8.3 Safety glasses are to be worn at all
times. 4.
Recommendations for further study
4.1 Further work should be done to
eliminate interferences, since there are many possible interferences.
Capillary columns could be investigated.
4.2 Additional work
should be done with each isomer separately to determine whether any
given isomer contains trace amounts of any other isomer. This can't be
seen when all three are mixed. 5.
References
5.1 Material Safety Data Sheets for
1,2,4- and 1,3,5-Trimethylbenzene from OCIS file.
5.2 Kirk-Othmer
Encyclopedia of Chemical Technology (1982), exec.ed. Martin Grayson,
vol. 18, pp. 881.5.
5.3 CRC Handbook of Chemistry and Physics,
53rd Edition, ed. by Robert C. Weast, pp. C-165-6.
|