Method number: |
PV2020 |
|
Matrix: |
Air |
|
Target concentration: |
1.5 ppm (10 mg/m3) |
|
Procedure: |
Samples are collected by drawing a known volume of air
through a charcoal tube. Samples are desorbed with 1 mL of 1:99 dimethyl
formamide:carbon disulfide (DMF:CS2 ) for 30 minutes with shaking
and analyzed by gas chromatography using a flame ionization
detector (GC-FID). |
|
Recommended air volume and sampling rate: |
20 L at 0.2 L/min |
|
Reliable quantitation limit: |
0.013 ppm (0.088 mg/m3) |
|
Special requirements: |
Samples should be refrigerated after sampling as soon
as possible, and analyzed within two weeks. |
|
Status of method: |
Partially Evaluated Method. This method has been
subjected to established evaluation procedures, and is presented for
information and trial use. |
|
Date: September, 1995 |
Chemist: Mary E. Eide |
Organic Service Branch I
OSHA Salt Lake Technical Center
Salt Lake City, UT 84165-0200
1. General Discussion
1.1 Background
1.1.1 History
The OSHA SLTC recently received samples collected on charcoal tubes
requesting analysis for dimethyl glutarate (DMG). A desorption study
with carbon disulfide showed low recovery, 71%, when 218 µg were spiked.
A desorption study using a solution of 1:99 dimethyl formamide:carbon
disulfide (DMF:CS2 ) showed an average of 94.5% recovery over
the concentration range of 21.8 to 436 µg DMG. The retention study
showed no loss when 20 L at 0.2 L/min of humid air (80% RH at 21°C) was
drawn through the tubes. Storage studied indicate a small loss of
recovery with samples taken in humid air, recoveries were 89.8% for
refrigerated samples and 88.0% for ambient samples, while dry samples
had recoveries of 96.1% for refrigerated samples and 94.7% for ambient
samples. This indicates that samples should be refrigerated after sampling.
1.1.2 Toxic effects (This section is for information only and should
not be taken as the basis of OSHA policy.) (Ref. 5.1)
DMG is a human skin, eye, and mucous membrane irritant. Worker exposure by
inhalation or through skin contact has been observed to cause blurred vision. There is
no PEL or TLV for DMG, but DuPont recommends an AEL (Acceptable Exposure Limit)
of 1.5 ppm or 10 mg/m3 for an 8 hour TWA. Animal toxicology studies with a mixture of
dimethyl glutarate, dimethyl adipate, and dimethyl succinate indicates that the mixture
is a mild to severe skin irritant, depending on the animal tested. The mixture is an eye
and mucous membrane irritant. Rats exposed to 60 ppm for 4 hours had transient
corneal opacity and transient increases in the distance from the cornea to the anterior
surface of the lens of the eye.
1.1.3 Workplace exposure (Ref. 5.1)
DMG is used in paint, enamel, varnish, lacquer, and thinner formulations. DMG is used
as a paint stripper and remover. DMG is used in polyamide and polyester resins and plasticizers.
1.1.4 Physical properties and other descriptive information (Ref. 5.1, 5.2, and 5.3)
Synonyms: |
Dimethyl pentanedioate; Glutaric acid, dimethyl
ester; Methyl glutarate; Pentanedioic acid, dimethyl ester |
CAS number: |
1119-40-0 |
IMIS: |
D636 |
Molecular weight: |
160.17 |
Flash point: |
103°C (218°F)(cc) |
Boiling point: |
93-94.5°C |
Melting point: |
-42.5°C |
Odor: |
faint agreeable odor |
Color: |
clear liquid |
Density: |
1.0876 (d204) |
Autoignition temperature: |
365°C (689°F) |
Molecular formula: |
C7H12O4 |
Structural formula: |
 |
The analyte air concentrations throughout this method are based on the
recommended sampling and analytical parameters. Air concentrations
listed in ppm are referenced to 25°C and 101.3 kPa (760 mmHg).
1.2 Limit defining parameters
1.2.1 Detection limit of the overall procedure (DLOP)
The detection limit of the overall procedure is 0.527 µg per sample (0.004
ppm or 0.026 mg/m3). This is the amount of analyte spiked
on the sampler that will give a response that is significantly different
from the background response of a sampler blank.
The DLOP is defined as the concentration of analyte that gives a
response (YDLOP) that is significantly different (three
standard deviations (SDBR)) from the background response
(YBR).
YDLOP - YBR = 3(SDBR)
The direct measurement of YBR and SDBR in
chromatographic methods is typically inconvenient, and difficult
because YBR is usually extremely low. inconvenient, and
difficult because YBR is usually extremely low. Estimates
of these parameters can be made with data obtained from the analysis
of a series of samples whose responses are in the vicinity of the
background response. The regression curve obtained for a plot of
instrument response versus concentration of analyte will usually be
linear. Assuming SDBR and the precision of data about the
curve are similar, the standard error of estimate (SEE) for the
regression curve can be substituted for SDBR in the above
equation. The following calculations derive a formula for the DLOP:
SEE |
= |
√ |
|
Σ(Yobs - Yest)2 |
|
n - k |
Yobs |
= observed response |
Yest |
= estimated response from regression curve |
n |
= total no. of data points |
k |
= 2 for a linear regression curve |
A |
= analytical sensitivity (slope) |
At point YDLOP on the regression curve
YDLOP = A(DLOP) +YBR
therefore
Substituting 3(SEE) + YBR for YDLOP gives
The DLOP is measured as mass per sample and expressed as equivalent air
concentrations, based on the recommended sampling parameters. Ten
samplers were spiked with equal descending increments of analyte, such
that the lowest sampler loading was 1.09 µg/sample. This is the amount,
when spiked on a sampler, that would produce a peak approximately 10
times the background response for the sample blank. These spiked
samplers, and the sample blank were analyzed with the recommended
analytical parameters, and the data obtained used to calculate the
required parameters (A and SEE) for the calculation of the DLOP. Values
of 102.9 and 18.07 were obtained for A and SEE respectively. DLOP was
calculated to be 0.527 µg/sample (0.004 ppm or 0.026 mg/m3).
Table 1.2.1 Detection Limit of the Overall Procedure
|
mass per sample |
area counts |
(µg) |
(µV-s) |
|
0 |
0 |
1.09 |
134 |
2.17 |
289 |
3.26 |
389 |
4.35 |
477 |
5.44 |
599 |
6.52 |
701 |
7.61 |
825 |
8.70 |
907 |
9.78 |
1066 |
10.9 |
1168 |
|
Figure 1.2.1. Plot of data to determine the DLOP/RQL.
1.2.2 Reliable quantitation limit (RQL)
The reliable quantitation limit is 1.76 µg per sample (0.013 ppm).
This is the amount of analyte spiked on a sampler that will give a
signal that is considered the lower limit for precise quantitative
measurements.
The RQL is considered the lower limit for precise quantitative
measurements. It is determined from the regression line data
obtained for the calculation of the DLOP (Section 1.2.1), providing
at least 75% of the analyte is recovered. The RQL is defined as the
concentration of analyte that gives a response (YRQL) such
that
YRQL - YBR = 10 (SDBR)
therefore
RQL = 1.76µg per sample (0.013 ppm)
Figure 1.2.2. Plot of data to determine the RQL.
Figure 1.2.3. Chromatogram of the RQL.
Table 1.2.2 Reliable Quantitation Limit
|
mass per sample |
mass recovered |
recovery |
(µg) |
(µg) |
(%) |
|
1.09 |
1.03 |
94.5 |
2.17 |
2.00 |
92.0 |
3.26 |
3.19 |
97.9 |
4.35 |
4.09 |
94.0 |
5.44 |
5.03 |
92.5 |
6.52 |
6.12 |
93.9 |
7.61 |
7.30 |
95.9 |
8.70 |
8.03 |
92.3 |
9.78 |
9.44 |
96.5 |
10.9 |
10.4 |
95.4 |
|
2. Sampling Procedure
2.1 Apparatus
2.1.1 Samples are collected using a personal sampling pump calibrated,
with the sampling device attached, to within ±5% of the recommended flow rate.
2.1.2 Samples are collected with tubes 7 cm × 4 mm i.d. × 6 mm o.d.
glass sampling tubes packed with two sections of charcoal, lot 120.
The front section contains 100 mg and the back section contains 50
mg of charcoal, lot 120. The sections are held in place with glass
wool plugs and are separated by a urethane foam plug. For this
evaluation, commercially prepared sampling tubes were purchased from
SKC Inc., (Eighty Four PA) catalog No. 226-01, Lot 120.
2.2 Technique
2.2.1 Immediately before sampling, break off the ends of the sampling tube. All tubes should be from the same lot.
2.2.2 Attach the sampling tube to the pump with flexible tubing. It is desirable to utilize sampling tube holders which have a protective
cover to shield the employee from the sharp, jagged end of the sampling tube. Position the tube so that sampled air passes through
the front section of the tube first.
2.2.3 Air being sampled should not pass through any hose or tubing before entering the sampling tube.
2.2.4 Attach the sampler vertically with the front section pointing downward, in the worker's breathing zone, and positioned so it does
not impede work performance or safety.
2.2.5 After sampling for the appropriate time, remove the sample and seal the tube with plastic end caps. Wrap each sample
end-to-end with a Form OSHA-21 seal.
2.2.6 Submit at least one blank sample with each set of samples. Handle the blank sample in the same manner as the other samples
except draw no air through it.
2.2.7 Record sample volumes (in liters of air) for each sample, along with any potential interferences.
2.2.8 Ship any bulk samples separate from the air samples.
2.2.9 Submit the samples to the laboratory for analysis as soon as possible after sampling. If delay is unavoidable, store the
samples in a refrigerator.
2.3 Desorption efficiency
The desorption efficiencies of DMG were determined by liquid-spiking
the charcoal tubes with the analytes at 0.1 to 2 times the target
concentration. The loadings on the tubes were 21.9, 109, 218,
and 436 µg of DMG. These samples were stored overnight at ambient
temperature and then desorbed with 1 mL of 1:99 DMF:CS2
with 0.25 µL/mL p-cymene internal standard, and analyzed
by GC-FID. The average desorption efficiency over the studied range was 94.8%.
Table 2.3 Desorption Efficiency of DMG
|
|
% Recovery |
|
|
0.1 X |
0.5 X |
1.0 X |
2.0 X |
Tube # |
21.9µg |
109µg |
218µg |
436µg |
|
1 |
95.6 |
96.4 |
96.1 |
93.9 |
2 |
92.7 |
93.6 |
93.0 |
93.7 |
3 |
94.5 |
94.0 |
95.8 |
96.2 |
4 |
93.1 |
94.6 |
97.2 |
94.9 |
5 |
92.7 |
94.8 |
95.6 |
95.3 |
6 |
93.4 |
95.5 |
96.7 |
96.1 |
average |
93.7 |
94.8 |
95.7 |
95.0 |
overall average |
94.8 |
|
standard |
±1.34 |
|
deviation |
|
|
2.4 Retention efficiency
The glass wool in front of the front section of the charcoal tube
was pulled towards the end, away from the charcoal, and spiked
with 436 µg (3 ppm) DMG, and then the tubes had 20 L humid air
(80% RH at 21°C) pulled through them at 0.2 L/min. The glass wool
was spiked to determine if DMG would volatize off the glass wool
and collect on the charcoal. They were opened, desorbed, and
analyzed by GC-FID. The retention efficiency averaged 94.4%.
There was no DMG found on the glass wool, indicating that it all
vaporized off. There was no DMG on the back sections of the tubes,
indicating that no breakthrough occured.
Table 2.4 Retention Efficiency of DMG
|
Tube # |
% Recovered |
|
|
Glass |
Front |
Back |
Total |
|
wool |
section |
section |
|
|
1 |
0.0 |
93.8 |
0.0 |
93.8 |
2 |
0.0 |
96.6 |
0.0 |
96.6 |
3 |
0.0 |
96.0 |
0.0 |
96.0 |
4 |
0.0 |
95.6 |
0.0 |
95.6 |
5 |
0.0 |
94.6 |
0.0 |
94.6 |
6 |
0.0 |
90.0 |
0.0 |
90.0 |
|
average |
94.4 |
|
2.5 Sample storage
The front sections of twelve sampling tubes were each spiked with 436 µg (3 ppm) of DMG, then
six tubes were stored in the refrigerator (-10°C), and six were stored at room
temperature 23°C. Twelve more tubes were spiked with 436 µg (3 ppm) of DMG, and then had 20
liters of humid air (80% RH at 21°C) drawn through them, afterwards six tubes were stored in
the refrigerator (-10°C), and six were stored at room temperature 23°C. Three of
each type of samples were analyzed after 7 days and the remaining three samples of each type
after 14 days. The amounts recovered indicate that humidity affects the ability of charcoal to retain DMG.
Table 2.5 Storage Test for DMG
|
Time |
% Recovery |
% Recovery |
% Recovery |
% Recovery |
(days) |
Humid |
Humid |
Dry |
Dry |
|
Ambient |
Refrigerated |
Ambient |
Refrigerated |
|
7 |
88.1 |
89.6 |
94.7 |
98.2 |
7 |
87.7 |
90.8 |
95.0 |
95.5 |
7 |
87.6 |
91.8 |
93.9 |
95.1 |
14 |
88.0 |
89.5 |
93.1 |
96.8 |
14 |
86.8 |
88.2 |
94.9 |
95.5 |
14 |
89.6 |
89.0 |
96.7 |
95.7 |
Average |
88.0 |
89.8 |
96.7 |
96.1 |
|
2.6 Recommended air volume and sampling rate.
Based on the data collected in this evaluation, 20 L air samples
should be collected at a sampling rate of 0.1 L/min, with a maximum
rate of 0.2 L/min.
2.7 Interferences (sampling)
2.7.1 It is not known if any compounds will severely interfere with
the collection of DMG on the sampling tubes. In general, the presence
of other contaminant vapors in the air will reduce the capacity of
the charcoal tube to collect DMG.
2.7.2 Suspected interferences should be reported to the laboratory with submitted samples.
2.8 Safety precautions (sampling)
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.
2.8.3 Wear eye protection when breaking the ends of the glass sampling tubes.
3. Analytical Procedure
3.1 Apparatus
3.1.1 The instrument used in this study was a gas chromatograph equipped with a flame ionization detector, specifically a Hewlett Packard model 5890.
3.1.2 A GC column capable of separating the analyte from any interferences. The column used in this study was a 60 meter
capillary column with a 0.5 µ coating of DB-WAX, with an I.D. of 0.32 mm.
3.1.3 An electronic integrator or some suitable method of measuring peak areas.
3.1.4 Two milliliter vials with TeflonTM-lined caps.
3.1.5 A 10 µL syringe or other convenient size for sample injection.
3.1.6 Pipets for dispensing the desorbing solution. A Repipet® dispenser was used in this study.
3.1.7 Volumetric flasks - 5 or 10 mL and other convenient sizes for preparing standards.
3.2 Reagents
3.2.1 GC grade nitrogen, hydrogen, and air.
3.2.2 Dimethyl glutarate, Reagent grade
3.2.3 Carbon disulfide, Reagent grade
3.2.4 Dimethyl formamide, Reagent grade
3.2.5 p-Cymene, Reagent grade (internal standard)
3.2.6 Desorbing solution was 1:99 DMF:carbon disulfide with 0.25 µL/mL p-cymene internal standard.
3.3 Standard preparation
3.3.1 At least two separate stock standards are prepared by diluting
a known quantity of DMG with the desorbing solution of 1:99 DMF:carbon
disulfide with 0.25 µL/mL p-cymene internal standard. The
concentration of these stock standards was 0.2 µL/mL or 218 µg/mL.
3.3.2 A third standard at a higher concentration was prepared to
check the linearity of the calibration. For this study, two
analytical standards were prepared at a concentration of 0.2 µL/mL
(218 µg/mL), and one at 1 µL/mL (1088 µg/mL) DMG in the desorbing solution.
3.4 Sample preparation
3.4.1 Sample tubes are opened and the front and back section of each tube are placed in separate 2 mL vials.
3.4.2 Each section is desorbed with 1 mL of the desorbing solution of 1:99 DMF:carbon disulfide with 0.25 µL/mL p-cymene internal standard.
3.4.3 The vials are sealed immediately and allowed to desorb for 30 minutes with constant shaking.
3.5 Analysis
3.5.1 Gas chromatograph conditions.
Injection size: |
1 µL |
|
Flow rates (mL/min) |
|
Nitrogen (make-up): |
30 |
Hydrogen(carrier): |
2 |
Hydrogen(detector): |
40 |
Air: |
420 |
|
Temperatures (°C) |
|
Injector: |
200 |
Detector: |
220 |
Column: |
50° for 2 min then 10°/min to 170° for 15 min |
Figure 3.5.1 Chromatogram of an analytical standard at the target concentration.
Peak identification: (1) carbon disulfide, (2) p-cymene, (3) DMF, and
(4) dimethyl glutarate.
3.5.2 Peak areas are measured by an integrator or other suitable means.
3.6 Interferences (analytical)
3.6.1 Any compound that produces a response and has a similar retention
time as the analyte is a potential interference. If any potential
interferences were reported, they should be considered before samples
are desorbed. Generally, chromatographic conditions can be altered
to separate an interference from the analyte.
Figure 3.6.1 A mass spectra of dimethyl glutarate (DMG).
3.6.2 When necessary, the identity or purity of an analyte peak may
be confirmed by GC-mass spectrometer or by another analytical procedure.
3.7 Calculations
3.7.1 The instrument was calibrated with a standard of 218 µg/mL DMG
in the desorbing solution. The linearity of the calibration was
checked with a standard of 1088 µg/mL.
3.7.2 If the calibration is non-linear, two or more standard at
different concentrations must be analyzed, bracketing the samples,
so a calibration curve can be plotted and sample values obtained.
3.7.3 To calculate the concentration of analyte in the air sample the following formulas are used:
(µg/m) (desorption volume) (desorption efficiency) |
= mass of analyte in sample |
(mass of analyte in sample) molecular weight |
= number of moles of analyte |
(number of moles of analyte) |
(molar volume at 25°C & 760mm) |
= |
volume the analyte will occupy at 25°C & 760mm |
(volume analyte occupies) (106)* (air volume) |
= ppm |
* All units must cancel.
3.7.4 The above equations can be consolidated to the following formula.
(µg/mL)(DV)(24.46)(106)(g)(mg) (20 L)(DE)(MW)(1000mg)(1000µg) |
= ppm |
µg/mL | = | concentration of analyte in sample or standard |
24.46 | = | Molar volume (liters/mole) at 25° and 760 mm Hg. |
MW | = | Molecular weight (g/mole) |
DV | = | Desorption volume |
20 L | = | 20 liter air sample |
DE | = | Desorption efficiency |
3.7.5 This calculation is done for each section of the sampling tube and the results added together.
3.8 Safety precautions (analytical)
3.8.1 Avoid skin contact and inhalation of all chemicals.
3.8.2 Wear safety glasses, gloves and a lab coat at all times while in the laboratory areas.
4. Recommendations for Further Study
Collection studies need to be performed from a dynamically generated test atmosphere.
5. References
5.1 Trade names Database on CCINFO CD-ROM Disc 95-2, Canadian Centre
for Occupational Health and Safety, Hamilton, Ontario.
5.2 Lide, D.R., "Handbook of Chemistry and Physics", 73rd Edition,
CRC Press Inc., Boca Raton FL, 1992, p. 3-258.
5.3 Windholz, M., "The Merck Index", Eleventh Edition, Merck & Co., Rahway NJ, 1989, p. 4373.
|