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Method no.: |
PV2102 |
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Control no.: |
T-PV2102-01-8709-CH |
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Matrix: |
Air |
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Target Concentration: |
5 mg/m3 (arbitrary). There is no OSHA PEL or
ACGIH TLV for Apron. |
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Procedure: |
Samples are collected by drawing 60 L of air through glass
fiber filters. Samples are extracted with acetonitrile and analyzed by high performance liquid chromatography (HPLC). |
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Recommended air volume and sampling rate
studied: |
60 L at 1 L/min |
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Detection limit of the overall procedure
based on the recommended air volume: |
0.02 mg/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: |
September 1987 |
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Chemist: |
Yihlin Chan |
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Carcinogen and Pesticide Branch
OSHA Analytical Laboratory
Sandy, Utah
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1. General discussion
1.1 Background
The OSHA Analytical Laboratory received a set of samples for which an analysis of Apron
was requested. The air samples had been collected on glass fiber filters at a flow rate of 1 L/min. This report
describes the analytical method developed for Apron and a preliminary validation of glass fiber filter as the
sampling medium.
1.2 Toxic effects (This section is for information only and should not be taken as the basis of OSHA policy.)
The oral LD50 of Apron is 669 mg/kg in rats. The acute dermal LD50 is >3100 mg/kg for rats.
It is relatively non-toxic to fish and wildlife. (Ref. 5.1)
1.3 Potential workplace exposure (Ref. 5.3)
Apron is used as a fungicide in agricultural applications. No estimate of worker exposure during its production,
formulation and use as a fungicide could be found.
1.4 Physical properties (Ref. 5.1 and 5.2)
Chemical name: |
N-(2,6-Dimethylphenyl)-N-(methoxyacetyl) -DL-alanine methyl ester |
Synonym: |
Apron 2E; CG 117; CGA 48988; Metalaxil; Ridomil; Ridomil 2E; Subdue;
Subdue 2E; Subdue 5SP; N-(Methoxyacetyl)-N-(2,6-xylyl)-DL-alanine methyl ester |
CAS no.: |
57837-19-1 |
Molecular formula: |
C15H21NO4 |
Molecular weight: |
279.37 |
Appearance: |
White crystals |
Melting point: |
71-72°C |
Vapor pressure: |
2.2×10-6 mmHg at 20°C |
Structure:
Solubility: |
Solubility in water at 20°C: 7.1 g/L. Readily soluble in most
organic solvents. |
UV scan: |
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1.5 Detection limit of the analytical procedure
The detection limit of the analytical procedure is 4.3 ng per injection.
2. Sampling procedure
2.1 Apparatus and reagents
2.1.1 A personal sampling pump that can be calibrated to within 5% of the recommended flow
rate.
2.1.2 Glass fiber filter, 37-mm diameter, Gelman Type A, or equivalent.
2.1.3 Filter holder for 37-mm filters, Millipore M000037A0, or equivalent.
2.2 Sampling procedure
Use standard air sampling technique as specified in OSHA Instruction CPL 2-2.20A, Chapter II:
Standard Methods for Sampling Air Contaminants.
2.3 Recommended air volume and sampling rate
2.3.1 The recommended air volume is 60 L.
2.3.2 The recommended sampling rate is 1 L/min.
2.4 Extraction efficiency
Three glass fiber filters were each spiked with 16.35 µg of Apron. The filters were
extracted with 5.0 mL of acetonitrile and analyzed. The average recovery of Apron was 100.4%.
Sample |
Apron recovered |
Recovery |
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YC1 |
16.07 µg |
98.3% |
YC2 |
16.60 µg |
101.5% |
YC3 |
16.56 µg |
101.3% |
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Average |
= 100.4% |
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2.5 Retention efficiency
Three glass fiber filters were each spiked with 16.35 µg of Apron. Humid air (50% RH, 183 L @
1 L/min) was drawn through the filters. The filters were extracted with 5.0 mL of acetonitrile and analyzed. The
average recovery of Apron was 97.9%.
Sample |
Apron recovered |
Recovery |
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YC7 |
15.46 µg |
94.6% |
YC8 |
16.40 µg |
100.3% |
YC9 |
16.13 µg |
98.7% |
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Average |
= 97.9% |
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2.5 Storage
Three glass fiber filters were each spiked with 16.35 µg of Apron. Humid air (50% RH, 183 min
@ 1 L/min) was drawn through the filters. The filters were stored at room temperature for 5 days, extracted with
acetonitrile, and analyzed. The average recovery of Apron was 104.9%.
Sample |
Apron recovered |
Recovery |
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YC10 |
17.05 µg |
104.3% |
YC11 |
17.05 µg |
104.3% |
YC12 |
17.33 µg |
106.0% |
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Average |
= 104.9% |
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2.6 Interferences
There are no known interferences to the sampling procedure.
3. Analytical method
3.1 Apparatus
3.1.1 High performance liquid chromatograph.
3.1.2 Alltech C18 column or equivalent.
3.1.3 UV detector.
3.1.4 Stripchart recorder.
3.2 Reagents
3.2.1 Water, HPLC grade.
3.2.2 Acetonitrile, HPLC grade.
3.2.3 Apron (Ridomil), EPA standard # F701.
3.3 Standard preparation
Weigh 2 to 4 mg of Apron in a 10-mL volumetric flask. Add acetonitrile to the mark.
Dilute with acetonitrile to a suitable working range.
3.4 Sample preparation
Samples were extracted with 5.0 mL of acetonitrile, 30 minutes on a mechanical
shaker.
3.5 Analysis
3.5.1 Instrument conditions
Column: |
Alltech C18 |
Mobile phase: |
60% acetonitrile, 40% water |
Detector: |
198 nm (primary), 214 nm |
Flow rate: |
1.0 mL/min |
Injection size: |
25 µL |
Retention time: |
7.0 min |
3.5.2 Chromatogram
Figure 1. HPLC Chromatogram of Apron.
3.6 Interferences
3.6.1 Any collected compound that has the same retention time as Apron and absorbs at 198 and
214 nm is an interference.
3.6.2 HPLC parameters may be varied to circumvent most interferences.
3.6.3 Retention time alone is not proof of a chemical identity. Confirmation by other means should be sought when
possible.
3.7 Calculations
3.7.1 A calibration curve is constructed by plotting standard concentrations versus detector
response.
3.7.2 The concentration of a sample is determined from the calibration curve.
Figure 2. Calibration curve of Apron.
3.7.3 The air concentration is determined by the formula:
mg/m3 = |
(µg/mL)(5 mL) |
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(air volume,
L)(extraction efficiency) |
4. Recommendations for further study
The method should be fully validated.
5. References
5.1 Registry of Toxic Effects of Chemical Substances, 1983-84 Supplement, DHHS (NIOSH)
Publication No. 86-103, Cincinnati, Ohio, 1986.
5.2 Merck Index, Tenth Edition, Merck & Co., Rahway, N.J., 1983.
5.3 Farm Chemicals Handbook, Meister Publishing, Willoughby, Ohio, 1981.
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