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DIMETHAZONE |
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Method number: |
PV2066 |
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Matrix: |
Air |
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Target Concentration: |
1 mg/m3 (arbitrary) There is no OSHA
permissible exposure level (PEL) or ACGIH threshold limit value
(TLV) for dimethazone. |
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Procedure: |
Samples are collected by drawing known volumes of air through
OSHA versatile sampler (OVS-2) tubes, each containing a
glass fiber filter and two sections of XAD-2 adsorbent.
Samples are desorbed with toluene and analyzed by gas chromatography
(GC) using an electron capture detector (ECD). |
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Recommended air volume and sampling rate: |
60 L at 1.0 L/min |
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Detection limit of the overall procedure (based on the
recommended air volume and the analytical detection limit): |
23 µg/m3 |
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Status of method: |
Stopgap method. This method has been only partially evaluated
and is presented for information and trial use. |
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Date: January 1989 (final draft) |
Chemist: Duane Lee |
Carcinogen and Pesticide Branch OSHA Analytical
Laboratory Salt Lake City, Utah 84115-1802
- General Discussion
1.1 Background
1.1.1 History of procedure
The OSHA Analytical Laboratory received a set of samples requesting
the analysis of dimethazone. The samples had been collected of
OVS-2 tubes. This report describes the analytical method
developed.
1.1.2 Toxic effects (This section is for information only and
should not be taken as the basis of OSHA policy.) The acute oral
LD50 is 1369 mg/kg for female rats and 2077
mg/kg for male rats. (Ref.
5.1)
1.1.3 Potential workplace exposure
Dimethazone is a selective herbicide for weed control in soybeans.
No estimate of worker exposure to dimethazone could be found. (Ref.
5.1)
1.1.4 Physical properties (Ref.
5.1)
Molecular weight: |
239.7 (calculated) |
Molecular formula: |
C12H14NO2Cl |
CAS #: |
81777-89-1 |
IMIS number: |
C229 |
Specific gravity: |
1.192 at 20°C |
Flash point: |
157-167°C |
Solubility: |
soluble in toluene; in water, 1100 ppm |
Chemical name: |
2-(2-chlorophenyl)methyl-4,4-dimethyl-3-isoxazolidinone |
Synonyms: |
Command, FMC 57020 |
Description: |
light brown viscous liquid; white solid (observed from EPA
standard) |
Structure: |
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1.2 Limit defining parameters The detection limit of the
analytical procedure, including a 5:1 split ratio, is 0.09 ng per
injection. This is the amount of analyte which will give a peak whose
height is approximately five times the baseline noise. (Figure
1.)
- Sampling procedure
2.1 Apparatus
2.1.1 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 OVS-2 tubes, which are specially made 13 mm o.d.
glass tubes that are tapered to 6 mm o.d., packed with a
140-mg backup section, a 270-mg sampling
section of cleaned XAD-2 adsorbent and a 13 mm diameter
glass fiber filter. The backup section is retained by two foam plugs
and the sampling section is between one foam plug and the glass fiber
filter. The glass fiber filter is held ne×t to the sampling section by
a polytetrafluoroethylene (PTFE) retainer. (Figure
2.)
2.2 Reagents No sampling reagents are required.
2.3 Sampling technique
2.3.1 Immediately before sampling, remove the plastic caps from the
OVS-2 tube.
2.3.2 Attach the small end of the tube to the sampling pump with
flexible tubing.
2.3.3 Attach the tube vertically in the employee's breathing zone
in such a manner that it does not impede work performance.
2.3.4 After sampling for the appropriate time, remove the tube and
seal with plastic caps.
2.3.5 Wrap each sample end-to-end with an OSHA seal
(Form 21).
2.3.6 Record the air volume for each sample, and list any possible
interferences.
2.3.7 Submit at least one blank for each set of samples. Handle the
blank in the same manner as the samples, except no air is drawn
through it.
2.3.8 Submit bulk samples for analysis in a separate
container.
2.4 Desorption efficiency (glass fiber filter and XAD-2
adsorbent)
Six vials each containing a 13-mm glass fiber filter and
270-mg of XAD-2 adsorbent were each liquid
spiked on the glass fiber filter with 15 µL of a 4.12 mg/mL dimethazone
standard. These were allowed to dry and then capped with
Teflon-lined caps and placed in a drawer over night. The
next day the samples were each desorbed with 3 mL of toluene, shaken for
30 min and then analyzed as in Section
3. The results are listed in the Table below.
Table 2.4 Desorption Efficiency
|
Sample # |
Amount Spiked, µg |
Amount Found, µg |
Recovered, % |
|
EX1 EX2 EX3 EX4 EX5 EX6 |
61.8 61.8 61.8 61.8 61.8 61.8 |
61.5 63.9 63.7 62.4 58.4 57.9 |
99.5 103.4 103.1 101.0 94.5
93.7 |
|
|
average |
99.2 |
|
2.5 Retention efficiency
Eighteen OVS-2 tubes were each liquid spiked with 15 µL
of a 4.12 mg/mL dimethazone standard on the glass fiber filter. These
were allowed to dry and then 240 L of humid air (~80% relative humidity)
were drawn through each tube at 1 L/min. Twelve of the tubes were stored
in a drawer at ambient temperature and Six of the tubes were stored in a
freezer. The next day 6 of the tubes from the drawer were each desorbed
with 3 mL of toluene, shaken for 30 min and then analyzed as in Section
3. The results are listed in the Table below.
Table 2.5 Retention Efficiency
|
Sample # |
Amount Spiked, µg |
Amount Found, µg |
Recovered, % |
|
R1 R2 R3 R4 R5 R6 |
61.8 61.8 61.8 61.8 61.8 61.8 |
60.9 62.7 63.2 59.3 56.0 55.6 |
98.5 101.5 102.3
96.0 90.6 90.0 |
|
|
average |
96.5 |
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2.6 Sample storage
After 6 days of storage, 6 tubes, 3 from the ambient storage group
and 3 from the freezer storage group, were each desorbed with 3 mL of
toluene, shaken for 30 min and then analyzed as in Section
3. After 9 days of storage, the remaining tubes were desorbed and
analyzed. The results are given in the Tables
below.
Table 2.6.1 Ambient Storage
|
Sample # |
Amount Spiked, µg |
Amount Found, µg |
Recovered, % |
|
6 6 6 9 9 9 |
61.8 61.8 61.8 61.8 61.8 61.8 |
60.7 62.7 61.3 65.7 59.5 58.8 |
98.2 101.5 99.2 106.3
96.3 95.1 |
|
|
average of Day 6 average of Day 9 |
99.6 99.2 |
|
Table 2.6.2 Freezer Storage
|
Sample # |
Amount Spiked, µg |
Amount Found, µg |
Recovered, % |
|
6 6 6 9 9 9 |
61.8 61.8 61.8 61.8 61.8 61.8 |
60.5 57.7 54.5 55.5 52.6 51.7 |
97.9 93.4 88.2 89.8 85.1 83.7 |
|
|
average of Day 6 average of Day 9 |
93.2 86.2 |
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2.7 Recommended air volume and sampling rate
2.7.1 The recommended air volume is 60 L.
2.7.2 The recommended flow rate is 1.0
L/min.
2.8 Interferences (sampling)
It is not known if any compounds will interfere with the collection
of dimethazone. Any suspected interference should be reported to the
laboratory.
2.9 Safety precautions (sampling)
2.9.1 Attach the sampling equipment in such a manner that it will
not impede work performance or employee safety.
2.9.2 Follow all safety practices that apply to the work area being
sampled.
- Analytical procedure
3.1 Apparatus
3.1.1 A balance capable of weighing to the nearest tenth of a
milligram. A Mettler HL52 balance was used in this evaluation.
3.1.2 A mechanical shaker.
3.1.3 A GC equipped with an ECD. A Hewlett Packard (HP) 5890 was
used in this evaluation.
3.1.4 A GC column capable of separating dimethazone from any
interferences. A 10 m × 0.32 mm i.d. (1.0 µm film) DB-5
capillary column was used in this evaluation.
3.1.5 An electronic integrator, or some other suitable means for
measuring detector response. The Hewlett-Packard 3357
Laboratory Data System was used in this evaluation.
3.1.6 Volumetric flasks and pipets.
3.1.7 Vials, 2-mL.
3.2 Reagents
3.2.1 Toluene, reagent grade.
3.2.2 Dimethazone, reagent grade. A standard obtained from EPA (EPA
# F815, 99.9% purity) was used in this
evaluation.
3.3 Standard preparation
Prepare dimethazone stock standards by weighing 10 to 14 mg of
dimethazone. Transfer the dimethazone to separate 10-mL
volumetric flasks, and add toluene to the mark. Make working range
standards of 0.4 to 50 µg/mL by pipet dilutions of the stock standards
with toluene. Store stock and dilute standards in a freezer.
3.4 Sample preparation
3.4.1 Transfer the 13-mm glass fiber filter and the
270-mg sampling section of the tube to a
4-mL vial. Place the first foam plug and the
140-mg section in a separate vial. A small glass funnel
can be used to facilitate the transfer of the adsorbent. Discard the
rear foam plug. Do not discard the glass sampling tube; it can be
reused.
3.4.2 Add 3.0 mL of toluene to each vial and seal with a
Teflon-lined cap.
3.4.3 Shake the vials for 30 minutes on a mechanical shaker.
3.4.4 Transfer the samples to 2-mL vials for use on an
HP autosampler.
3.5 Analysis
3.5.1 Instrument conditions
Column: |
DB-5, 10 m × 0.32 mm i.d., 1.0 µm film |
Injector temperature: |
275°C |
Column temperature: |
145°C |
Detector temperature: |
300°C |
Gas flows: |
|
Column: |
8.6 mL/min hydrogen |
ECD make up: |
42 mL/min nitrogen |
Injection volume: |
1.0 µL |
Split ratio: |
5:1 |
Retention time: |
6.7 min |
3.5.2 Chromatogram (Figure
3.)
3.6 Interferences (analytical)
3.6.1 Any collected compound having a similar retention time to
that of the analyte is a potential interference.
3.6.2 GC conditions may be varied to circumvent interferences.
3.6.3 Retention time on a single column is not proof of chemical
identity. Analysis by an alternate GC column or confirmation by mass
spectrometry are additional means of
identification.
3.7 Calculations
3.7.1 Construct a calibration curve (Figure
4.) by plotting detector response versus concentration (µg/mL) of
dimethazone.
3.7.2 Determine the µg/mL of dimethazone in both sections of each
sample and blank from the calibration curve.
3.7.3 Blank correct each section by subtracting the µg/mL found in
the blank section from the µg/mL found in the sample section and then
add the sections together.
3.7.4 Determine the air concentration by using the following
formula.
mg
m3 |
= |
(µg/mL blank corrected)(desorption volume, mL)
(air volume, L)(desorption efficiency, decimal)
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3.8 Safety precautions (analytical)
3.8.1 Avoid skin contact and air exposure to dimethazone.
3.8.2 Avoid skin contact with all solvents.
3.8.3 Wear safety glasses at all times.
- Recommendation for further study
This method should be fully validated.
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Figure
1. Chromatogram of Dimethazone at the Detection
Limit
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Figure
2. OVS-2 Sampling Tube
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Figure
3. Chromatogram of Dimethazone
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Figure
4. Calibration Curve
- References
5.1 Farm Chemicals Handbook; Berg, Gordon
L. Ed.; Meister: Willoughby, Ohio, 1986; p C61.
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