RESMETHRIN
Method number: |
2052 |
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Matrix: |
Air |
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Target Concentration: |
0.34 mg/m3 (arbitrary) There is
neither an OSHA PEL nor an ACGIH TLV for resmethrin. |
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Procedure: |
Samples are collected by drawing known volumes of air through
OSHA versatile sampling tubes (OVS-2) containing a glass fiber
filter and two sections of XAD-2 adsorbent. Samples are
desorbed with acetonitrile and analyzed by high performance liquid
chromatography (HPLC) using an ultraviolet (UV) detector. |
|
Recommended air volume and sampling rate: |
60 L at 1 L/min |
|
Detection limit of the overall procedure (based on the
recommended air volume and the analytical detection limit): |
0.017 mg/m3 |
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Status of method: |
Stopgap method. This method has been partially evaluated and is
presented for information and trial use only. |
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Date: July 1989 (final draft) |
Chemist: James Pike |
Carcinogen And Pesticide Branch OSHA Analytical
Laboratory 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 with a request for the analysis of resmethrin. These air
samples had been collected on OVS-2 sampling tubes at a
flow rate of 1 L/min. This report describes the preliminary
validation of the sampling method and the development of an
analytical procedure for resmethrin.
1.1.2. Toxic effects (This section is for information only and
should not be taken as the basis of OSHA policy).
In rats the acute oral LD50 for
resmethrin (technical material) is 4240 mg/kg. In rabbits the acute
dermal LD50 is 2500 mg/kg. In guinea pigs skin sensitization is
negative (Ref. 5.1.).
1.1.3. Potential workplace exposure
Resmethrin is an insecticide. No estimate of the extent of worker
exposure could be found at this time.
1.1.4. Physical properties and other descriptive information
(Ref. 5.2. through 5.5.)
Chemical name: |
(5-Benzyl-3-fural)methyl-2, 2-di-methyl-3-(2-methyl-propenyl)cyclo-propanecarboxylate |
Synonyms: |
5-Benzyl-3-furylmethyl(IRS)-cis,
trans-chrysanthemate;
{5-(Phenyl-methyl)-3-furanyl}
methyl-2,2-di-methyl-3-(2-methyl-1-propenyl)
cyclo-propanecarboxylate; Benzofuroline;
Chrysron; Premgard; Pynosect; Pyretherm; Synthrin; FMC
17370 (discontinued by FMC); NIA 17370 (discontinued by
FMC) (Ref. 5.1. and 5.2.) |
CAS #: |
10453-86-8 |
IMIS #: |
2233 |
Molecular weight: |
338.45 |
Molecular formula: |
C22H2603 |
Appearance: |
Waxy off-white to tan solid |
Odor: |
Characteristic chrysamthemate |
Solubility: |
Insoluble in water, 10% soluble in kerosene,
very soluble in xylene, methylene chloride, isopropanol, and
aromatic hydrocarbons (Ref. 5.1.) |
UV scan: |
See Figure 3. |
Structure: |
|
1.2. Limit defining parameters
The detection limit of the analytical procedure is 10.1 ng per
injection. This is the amount of analyte which will give a peak whose
height is approximately five times the baseline noise. (See Figure 2.)
2. Sampling Procedure (Ref. 5.6. and 5.7.)
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 samplers, 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 of cleaned XAD-2 adsorbent, 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 13-mm glass
fiber filter. The glass fiber filter is held next to the sampling
section by a polytetrafluoroethylene (PTFE) retainer. (See Figure
5.)
2.2. Reagents
None
2.3. Sampling technique
2.3.1. Calibrate the pump to 1 L/min.
2.3.2. Attach the sampling device to the sampling pump inlet with
flexible, plastic tubing so that the large, front section of the
device is exposed directly to the atmosphere. Do not place any
tubing in front of the sampler.
2.3.3. Attach the sampler vertically (large end down) to the
worker's collar or within the breathing zone in such a manner that
it does not impede work performance.
2.3.4. After sampling for the appropriate time, remove the
sampling device and reseal the tube with plastic
end-caps. Wrap each sample end to end with a form
OSHA-21 seal.
2.3.5. 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.
2.3.6. Report any possible interferences to the laboratory at the
time the samples are submitted.
2.3.7. Ship samples as soon as possible in a suitable container
designed to prevent damage in transit.
2.3.9. Submit bulk samples for analysis in a container separate
from the air samples.
2.4. Extraction efficiency
Three "A-portions" from OVS-2 tubes (270 mg
XAD-2 plus 13-mm glass fiber filter) were
each liquid spiked with 40.4 µg of resmethrin and placed in separate
4-ml vials. Each sample was treated with 2.0 ml of
acetonitrile, sealed with a cap, allowed to extract for 1 hr. with
occasional vigorous shaking, and analyzed as per section 3.
Table 2.4. Extraction Efficiency of Resmethrin
|
Sample |
Resmethrin found |
Recovery |
|
EE-5 |
32.065 µg |
79.4% |
EE-6 |
33.094 mg |
81.9% |
EE-7 |
32.688 mg |
80.9% |
EE-8 |
blank |
---- |
|
|
Average recovery = 80.7% |
|
2.5. Retention efficiency
Three OVS-2 tubes were each liquid spiked with 80.8 µg
of resmethrin. Approximately 60 L of humid air (-70%) were drawn
through the tubes at 1 L/min. The retention study samples, along with
a blank, were then prepared and analyzed as per section 3. There was
less than 1% of breakthrough observed in this study. Breakthrough is
defined as the amount of analyte found on the backup portion of the
sampling tube divided by the total amount of analyte found on the
sampling tube.
Table 2.5. Retention Efficiency of Resmethrin
|
Sample |
Resmethrin found |
Recovery |
|
RS-5 |
65.423 µg |
81.0% |
RS-6 |
66.401 µg |
82.2% |
RS-7 |
62.962 µg |
77.9% |
RS-8 |
blank |
---- |
|
|
Average recovery = 80.4% |
|
2.6. Sample storage
Three OVS-2 tubes were each liquid spiked with 40.4 µg
of resmethrin, sealed with end caps, and stored at ambient temperature
for 21 days. The storage test samples were then extracted and analyzed
as per section 3.4.
Table 2.6. Storage Test of Resmethrin
|
Sample |
Resmethrin found |
Recovery |
|
ST-1 |
32.226 mg |
79.8% |
ST-2 |
32.435 mg |
80.3% |
ST-3 |
30.354 mg |
75.1% |
ST-4 |
blank |
---- |
|
|
Average recovery = 78.4% |
|
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 resmethrin. Suspected interferences 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 interfere with work performance or employee safety.
2.9.2. Follow all safety practices that apply to the work area
being sampled.
3. Analytical Procedure (Ref. 5.7.)
3.1. Apparatus
3.1.1. A calibrated balance capable of determining a weight to
the nearest 100 µg. A Mettler HL52 balance was used in this
evaluation to prepare the concentrated standards.
3.1.2. Volumetric flasks, pipets, and syringes of various
convenient sizes for preparing standards, making dilutions and
making injections.
3.1.3. A high performance liquid chromatograph equipped with a
variable wavelength UV detector, manual or automatic injector, and
strip chart recorder. A Hewlett-Packard 1084B HPLC,
interfaced with a Du Pont UV Spectrophotometer was used for this
evaluation.
3.1.4. An HPLC column capable of separating resmethrin from any
interferences. A (25 cm × 4.6 mm i.d.) Du Pont Zorbax ODS (5 micron)
column was used for this evaluation.
3.1.5. An electronic integrator, or some other suitable method
for measuring detector response. The Hewlett-Packard
3357 Laboratory Data System was used for this evaluation.
3.1.6. Glass vials, 4-ml with
rubber-lined caps
3.1.7. Glass vials, 2-mL with
Teflon-lined septa
3.2. Reagents
3.2.1. Acetonitrile (AcN), HPLC grade
3.2.2. Water, HPLC grade. A Millipore Milli-Q system
was used to prepare the water for this evaluation.
3.2.5. Resmethrin, (EPA Reference standard #6055). A 99.5% pure
standard from EPA was used for this evaluation.
3.3. Standard preparation
Prepare two stock standard solutions by adding acetonitrile to
preweighed amounts of resmethrin (20 to 30 mg) in 10-mL
volumetric flasks. Prepare working range standards by pipet dilutions
of previous standards. Store stock and dilute standards in freezer.
3.4. Sample preparation
3.4.1. Transfer the glass fiber filter and the
270-mg portion of XAD-2 from the sampling
tube to a 4-ml glass vial. Place the first foam plug
and the 140-mg portion in a separate vial. A small
glass funnel can be used to facilitate the the transfer of the
adsorbent. Discard the rear foam plug. Do not discard the glass
sampling tube; it can be reused after it has been cleaned.
3.4.2. Add 2.0 ml of acetonitrile to each vial and seal with
rubber lined caps.
3.4.3. Allow the samples to extract for one hour with occasional
vigorous shaking.
3.4.4. Where necessary for automation, transfer aliquots of
samples to 2-ml vials for use in an autosampler, and
seal with PTFE-lined septa.
3.5. Analysis
3.5.1. Instrument conditions
Column: |
Du Pont Zorbax ODS, 5-µm, (25 cm ×
4.6 mm i.d.) |
Column temperature: |
50°C |
Mobile phase: |
AcN/H2O 75:25 |
Mobile phase temperature: |
50°C |
Flow rate: |
1.5 mL/min |
Detector wavelength: |
233 nm |
Retention time: |
5.7 min |
Injection volume: |
20 µL |
3.5.2. Chromatogram (See Figure 1.)
3.5.3. Intersperse the analytical standards, including a
detection limit standard, with the samples in the analytical
sequence.
3.6. Interferences (analytical)
3.6.1. Any collected compound soluble in acetonitrile that has a
similar retention time and absorbs at 233 nm is an interference.
Generally, chromatographic conditions can be altered to separate
interferences from the analyte.
3.6.2. Retention time alone is not proof of chemical identity.
Confirmation of chemical identity by other means such as GC Mass
Spectrometry, detector response ratioing or chromatography by an
alternate column should be sought when possible.
3.7. Calculations
3.7.1. By using a suitable method, such electronic integration,
measure the detector response.
3.7.2. Use an external or internal standard procedure to prepare
a calibration curve using analytical standards over a range of
concentrations (See Figure 4). Bracket the samples with analytical
standards.
3.7.3. Construct a calibration curve by plotting detector
response versus standard concentration. (See Figure 4.)
3.7.4. Determine the concentration of resmethrin in each section
of a sample from the calibration curve. If resmethrin is found on
the backup section, add it to the amount on the front section. Make
blank corrections for each section before adding the results
together.
3.7.5. The air concentration is then determined by:
mg/m3 = |
(µg/mL in sample) × (extraction
volume, mL)
(air volume, L) × (extraction efficiency,
decimal) |
3.8. Safety precautions (analytical)
3.8.1. Avoid exposure to all standards.
3.8.2. Avoid skin contact with all solvents.
3.8.3. Wear safety glasses in the laboratory at all times.
4. Recommendation for Further Study
A fully validated sampling and analytical method should be developed.
Figure 1. Chromatogram of Resmethrin
Figure 2. Detection limit of Analytical Procedure for Resmethrin
Figure 3. UV Scan of Resmethrin
Figure 4. Calibration Curve of Resmethrin
Figure 5. OVS-2 Sampling Device
5. References
5.1. Meister, R. T., Ed.; "Farm Chemicals Handbook '85", 71st ed.;
Meister Publishing: Willowby, OH, 1985; p C203.
5.2 Ouellett, R. P. and King, J. A.; "Chemical Week Pesticides
Register"; McGraw-Hill Book Company: New York, NY, 1977;
p. 266.
5.3. Wiswesser, W. J., Ed.; "Pesticide Index", 5th ed.;
Entomological Society of America: College Park, MD, 1976; p 198.
5.4. Watts, R. R., Ed.; "Analytical Reference Standards and
Supplemental Data for Pesticides and Other Organic Compounds"; Analyt
ical Chemistry Branch, Environmental Toxicology Division, Health
Effects Research Laboratory: Research Triangle Park, NC, Revised 1980;
p 85.
5.5. Tatken, R. L. and Lewis, R. J. Sr., Ed.; "Registry of Toxic
Effects of Chemical Substances"; U. S. Department of Health and Human
Services: Cincinnati, OH, 1986; DDH(NIOSH) Publication No.
86-103, 1, p 1032.
5.6. "Industrial Hygiene Technical Manual"; OSHA Instruction CPL
2-2.20A, U.S. Department of Labor, Chapter II: "Standard
Methods for Sgmpling Air Contaminants", 1984.
5.7 Burright, D.; "Carbaryl (Sevin)"; Method #58, Organic Methods
Evaluations Branch, OSHA Analytical Laboratory: Salt Lake City, UT,
July 1987; unpublished.
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