(MEK PEROXIDE)
OSHA Analytical Laboratory Salt Lake City, Utah 1. General Discussion
Airborne methyl ethyl ketone peroxide (MEK peroxide) was first determined by collecting in a midget impinger containing dimethyl phthalate (DMP). (Ref. 5.1.) A portion of the solution was treated with diphenylcarbazide and the absorbance of the resulting color complex was measured at 565 nm. A bubbler containing an acid solution of titanium tetrachloride has also been used. (Ref. 5.2.) NIOSH Methods P&CAM 331 and 3508 (Refs. 5.3. and 5.4.) are based on the former procedure. However, these colorimetric methods are prone to interference and they do not differentiate the isomeric forms of MEK peroxide shown below.
A misconception of the true identity of MEK peroxide is prevalent in IH literature. For example, both ACGIH (Ref. 5.5.) and NIOSH (Refs. 5.3. and 5.4.) assign cyclic dimer as the structure for MEK peroxide when it has been shown conclusively (Refs. 5.6. and 5.7.) that the main components of the commonly used industrial MEK peroxide are monomer and dimer and that the cyclic dimer is not present. Preparing analytical standards of the two isomers was a major obstacle since MEK peroxide with known concentrations of monomer and dimer is not available commercially. In this evaluation, the preparation of monomer and dimer for analytical standards was accomplished by modifying a procedure reported in the literature (Ref. 5.8.). A two-column HPLC method, based on the reaction between hydroperoxide and triphenylphosphin (Ref. 5.9.), has been developed (Ref. 5.10.) to quantitate the MEK peroxide monomer and the dimer separately. But the method suffers from a long run time as it requires dual injections and a column wash. An HPLC method using electrochemlcal detection has been reported, (Refs. 5.11. and 5.12.) but the dissolved oxygen in the sample interfered with detection of the dimer. The analytical procedure of this method was adapted from the literature (Ref. 5.13.). It is an HPLC/postcolumn derivatization method using a sodium iodide/acetic acid system where the MEK peroxide monomer and dimer can be analyzed within a 10-min run time. XAD-4 adsorbent was selected as the sampling medium because it has previously been found to be suitable for collecting airborne MEK peroxide (Ref. 5.10.). The ACGIH has set a TLV (ceiling) of 0.2 ppm (1.5 mg/m3) for MEK peroxide. This value was selected for the target concentration. After most of the work in this evaluation had been done, OSHA published a new PEL (ceiling) of 0.7 ppm (5 mg/m3). The sampler of this method easily permits the collection of MEK peroxide at the new PEL. 1.1.2. Toxic effects (This section is for information only and should not be taken as the basis of OSHA policy.) Following is a direct quote from Ref. 5.14.
Mice given a total dose of (about) 7 mg methyl ethyl ketone peroxide developed malignant tumors, the first of which appeared after fifteen months. One subcutaneous sarcoma, three malignant lymphomas, and a pulmonary adenoma were noted in 34 of the 50 mice surviving exposure. Chemical burns of the gastrointestinal tract, as well as residual scarring and stricture of the esophagus, were noted in an individual surviving ingestion of two ounces of a 60% methyl ethyl ketone peroxide solution. 1.1.3. Workplace exposure Methyl ethyl ketone peroxide is used widely in the polymer industry for curing unsaturated polyester resins. According to the NIOSH National Occupational Exposure Surveys of 1972 and 1982, workers in the following industries (with standard industrial code) are most likely to be exposed to MEK peroxide: boat building and repairing (SIC 3732), cut stone and stone products (SIC 3281), pressed and blown glass (SIC 3229), terrazzo, tile, marble, mosaic (SIC 1743), household furniture (SIC 2519), and transportation equipment and supply (SIC 5088). 1.1.4. Physical properties and other descriptive information (Ref. 5.15. unless noted otherwise)
In this method, MEK peroxide from K&K was used in preparing validation samples. The composition was 26.0% monomer and 20.7% dimer. Unless specifically stated, the analyte amounts throughout this method are the sum of the monomer and the dimer. The analyte air concentrations are based on the recommended sampling and analytical parameters.
The detection limit of the analytical procedure is 31 ng per injection. This is the amount of analytes which gave MEK peroxide monomer and dimer peaks with heights about 5 times the baseline noise. (Section 4.1.) 1.2.2. Detection limit of the overall procedure The detection limit of the overall procedure is 4.51 µg per sample (0.30 mg/m3). This is the amount of analyte spiked on the sampling device which allows recovery of an amount equivalent to the detection limit of the analytical procedure. (Section 4.2.) 1.2.3. Reliable quantitation limit The reliable quantitation limit is 4.51 µg per sample (0.30 mg/m3). This is the smallest amount of MEK peroxide spiked on the sampling device which can be quantitated within the requirements of a recovery of at least 75% and a precision (±1.96 SD) of ±25% or better. (Section 4.3.)
The reliable quantitation limit and detection limits reported in the method are based upon optimization of the instrument for the smallest possible amount of the analyte. When the target concentration of the analyte is exceptionally higher than these limits, they may not be attainable at the routine operating parameters.
1.2.4. Instrument response to the analyte The instrument response over the concentration range of 0.5 to 2 times the target concentration is linear with a slope of 120700 area counts per µg/mL for MEK peroxide dimer and 113200 area counts per µg/mL for MEK peroxide monomer. (Section 4.4.) 1.2.5. Recovery The recovery of MEK peroxide from samples used in a 16-day storage test remained above 92.2% when the samples were stored in a freezer. (Section 4.5.) The recovery of an analyte from the collection medium during storage must be 75% or greater. 1.2.6. Precision (analytical procedure only) The pooled coefficient of variation obtained from replicate injections of analytical standards at 0.5, 1 and 2 times the target concentration is 0.027 for MEK peroxide dimer and 0.035 for MEK peroxide monomer. (Section 4.6.) 1.2.7. Precision (overall procedure) The precision at the 95% confidence level for the refrigerated 16-day storage test is ±14.5%. (Section 4.7.) This includes an additional ±5% for sampling error. The overall procedure must provide results at the target concentration that are ±25% or better at the 95% confidence level. 1.2.8. Reproducibility A draft copy of this procedure and six samples spiked with MEK
peroxide were given to a chemist unassociated with this evaluation.
The samples were analyzed after 7 days of storage at about
1.3. Advantages
1.3.2. Individual isomers of MEK peroxide can be determined. 1.4. Disadvantage Samples must be stored in a freezer until analysis. 2. Sampling Procedure
2.1.2. Glass sampling tubes each packed with an 80-mg front section and a 40-mg back section of XAD-4 adsorbent. XAD-4 sampling tubes from SKC, Inc. (catalog no. 226-30-11-04, Lot 146) were used in this evaluation. 2.2. Reagents No sampling reagents are required. 2.3. Sampling technique
2.3.2. After sampling, seal the tube with plastic end caps. Wrap the tube lengthwise with an official OSHA seal (Form 21). 2.3.3. Submit at least one blank with each set of samples. Handle the blank the same as the other samples except draw no air through it. 2.3.4. List any potential interferences on the sample data sheet. 2.4. Sampler capacity The sampler can be used to collect MEK peroxide at 10 times the target concentration for at least 8 times the recommended sampling time without breakthrough. (Section 4.9.) 2.5. Desorption efficiency and stability of desorbed samples
2.5.2. Desorbed samples remain stable for at least 24 h when stored at room temperature. 2.6. Recommended air volume and sampling rate
2.6.2. The recommended air sampling rate is 1 L/min. 2.7. Interferences (sampling) MEK peroxide is very labile. Heat, acids, bases, or trace amounts of metal ions will cause decomposition. 2.8. Safety precautions (sampling)
2.8.2. Follow all safety practices applicable to the work area being sampled. 3. Analytical Procedure
3.1.2. An HPLC column capable of separating MEK peroxide monomer and dimer from potential interferences. A 25-cm × 6-mm Bakerbond cyanopropyl column was used in this evaluation. A 25-cm × 6-mm Supelco LC18DB column was used in the alternate analytical conditions. 3.1.3. A postcolumn derivatization system. Two Waters 6000 pumps, pulse dampeners (part nos. 98060 and 25561), ninhydrin reaction coil and temperature controller were used in this study. A schematic of the HPLC/postcolumn system is illustrated in Figure 3.1.3. 3.1.4. An electronic integrator or other suitable means of measuring detector response. A Hewlett-Packard 3357 laboratory data system was used in this evaluation. 3.1.5. Four-milliliter vials with polytetrafluoroethylene (PTFE)-lined caps. New unsilinized vials were used in this evaluation. If old vials are to be used, they must be silanized. 3.1.6. Volumetric flasks and pipets, silanized. Sylon CT from Supelco was used in silanizing the glassware. The directions supplied with the reagent were followed. 3.2. Reagents
3.2.2. 2-Propanol (IPA) and isooctane, HPLC grade. 2-Propanol, Optima, and isooctane, Optima, both from Fisher Scientific Co., were used in this evaluation. 3.2.3. 10% Acetic acid solution: Dilute 100 mL of glacial acetic acid to 1 L with 2-propanol. 3.2.4. Sodium iodide solution: Dissolve 1 g of sodium iodide in 1 L of 2-propanol. 3.3. Standard preparation
3.3.2. Prepare stock standards by weighing 3 drops of MEK peroxide/DMP solution in 10-mL volumetric flasks and diluting to volume with 2-propanol. Prepare fresh stock standards daily. 3.3.3. Prepare analytical standards by further diluting stock standards with 2-propanol. 3.3.4. Prepare a sufficient number of standards to generate calibration curves. Analytical standard concentrations must bracket sample concentrations. 3.4. Sample preparation
3.4.2. Add 2.0 mL of 2-propanol to each vial. 3.4.3. Seal the vials with PTFE-lined caps and shake them on a mechanical shaker for 1 h. 3.5. Analysis
3.5.2. Alternate analytical conditions
3.5.3. Measure detector response using a suitable method such as electronic integration. 3.5.4. Prepare a calibration curve using several standards over a range of concentrations. Bracket the samples with analytical standards. 3.6. Interferences (analytical)
3.6.2. Hydrogen peroxide and dimethyl phthalate are not interferences. 3.6.3. A useful means of confirming the MEK peroxide is by electrochemical detector using reverse phase column (Section 3.5.2.). A GC/MS procedure would not be viable because MEK peroxide is thermally labile. 3.7. Calculations
3.7.2. Determine the concentrations of a sample, in micrograms of MEK peroxide monomer or dimer per milliliter, by comparing its detector responses to the calibration curves. 3.7.3. Perform blank corrections for each section. 3.7.4. The air concentration of MEK peroxide can be obtained by using the following equations:
Values in ppm are not calculated because they are dependent on the dimer/monomer ratio.
3.8. Safety precautions (analytical)
3.8.2. Restrict the use of all chemicals to a fume hood. 3.8.3. Wear safety glasses in all laboratory areas. 4. Backup Data
The detection limit of the analytical procedure is 31 ng per injection. It is based on a 15-µL injection of a 2.07 µg/mL standard (consisting of 0.92 µg/mL of MEK peroxide dimer and 1.15 µg/mL of MEK peroxide monomer.) This amount produced MEK peroxide monomer and dimer peaks whose heights were about 5 times the height of the baseline noise. A chromatogram of the detection limit of the analytical procedure is shown in Figure 4.1. 4.2. Detection limit of the overall procedure The detection limit of the overall procedure is 4.51 µg per sample (0.30 mg/m3). Six vials containing 80 mg of XAD-4 were each liquid spiked with 4.51 µg of MEK peroxide. The samples were desorbed 24 h later with 2 mL of 2-propanol.
4.3. Reliable quantitation limit The reliable quantitation limit is also 4.51 µg per sample (0.30 mg/m3). This was derived from the samples and data of Table 4.2. Because the recovery of MEK peroxide from the spiked samples was greater than 75% and the precision (1.96 SD) was less than ±25%, the detection limit of the overall procedure and reliable quantitation limit are the same.
Reliable Quantitation Limit (based on samples and data of Table 4.2.)
4.4. Instrument response to MEK peroxide The instrument response to MEK peroxide over the range of 0.5 to 2 times the target concentration is linear with a slope of 120700 area counts per µg/mL for the dimer and 113213 area counts per µg/mL for the monomer. The responses to MEK peroxide were determined by multiple injections of standards. The data in Tables 4.4.1. and 4.4.2. are presented graphically in Figures 4.4.1. and 4.4.2.
4.5. Storage data Thirty-six samples were generated by liquid-spiking 22.62 µg of MEK peroxide onto XAD-4 adsorbent tubes. Humid air (80% relative humidity at 24°C) was pulled through the tubes for 15 min at 1 L/min. Six tubes were analyzed the same day. Fifteen tubes were stored in a freezer (-25°C) and the other fifteen were stored in the dark at ambient temperature (about 22°C). Every few days over a 15-day period, three samples were selected from each of the two sets and analyzed. Another set of storage samples were prepared and analyzed over a 16-day period. The combined results are listed Table 4.5. There was no significant loss of MEK peroxide in the refrigerated samples, but those stored at ambient temperature suffered a significant loss. The storage data are also presented graphically in Figures 4.5.1. and 4.5.2.
Storage Test
4.6. Precision (analytical method only) The precision of the analytical procedure is 0.027 for MEK peroxide dimer and 0.035 for MEK peroxide monomer. The precision of the analytical procedure is defined as the pooled coefficient of variation determined from replicate injections of MEK peroxide standards at 0.5, 1 and 2 times the target concentration.
Precision of the Analytical Method for MEK Peroxide Dimer (based on the data of Table 4.4.1.)
Precision of the Analytical Method for MEK Peroxide Monomer (based on the data of Table 4.4.2.)
4.7. Precision (overall procedure) The precision of the overall procedure is determined from the storage data. The determination of the standard error of estimate (SEE) for a regression line plotted through the graphed storage data allows the inclusion of storage time as one of the factors affecting overall precision. The SEE is similar to the standard deviation except it is a measure of dispersion of data about a regression line instead of about a mean. It is determined with the following equation:
An additional ±5% for pump error is added to the SEE by the
addition of variances. The precision at the 95% confidence level is
obtained by multiplying the SEE (with pump error included) by 1.96
(the 4.8. Reproducibility data Six samples, liquid spiked with MEK peroxide, were given to a chemist unassociated with this study. The samples were analyzed after being stored for 7 days at about -25°C. No sample result had a percent deviation greater than the precision of the overall procedure, which was ±14.5%.
Reproducibility Data
4.9. Sampler capacity Aerosol generation was found to be unsuitable for preparing a standard atmosphere of MEK peroxide because it drastically changes the latter's composition. The sampler capacity was tested by the following method. A plug of glass wool was placed upstream of an XAD-4 tube. The back section of the tube was removed. Another XAD-4 tube was placed downstream. Humid air (80% RH at 22°C) was pulled through the train at 1 L/min. At 15-min intervals, 229 µg of MEK peroxide was spiked onto the glass wool and the downstream XAD-4 tube was replaced with a new one. This simulates an atmosphere of 15.3 mg/m3 MEK peroxide which is about 10 times the target concentration. The test was conducted for a total of 120 min, 8 times the recommended sampling time. At the end of the test, all 8 downstream tubes as well as the front tube were analyzed. Essentially all of the MEK peroxide was collected on the front tube. The sampler capacity is at least 8 times the recommended sampling volume at 10 times the target concentration.
Breakthrough Data at 10× Target Concentration
4.10. Desorption efficiency and stability of desorbed samples
The desorption efficiency (DE) of MEK peroxide was determined by liquid-spiking 80-mg portions of XAD-4 with MEK peroxide at 0.5, 1 and 2 times the target concentration. These samples were stored in a refrigerator overnight and then desorbed and analyzed. The average desorption efficiency over the studied range was 99.4%.
Desorption Efficiency of MEK Peroxide
4.10.2. Stability of desorbed samples The stability of desorbed samples was investigated by reanalyzing the 1 times the target concentration desorption samples about 24 h after the original analysis. The samples had been recapped and stored at room temperature. They were reanalyzed with fresh standards. The average of the reanalyzed samples relative to the average of the original analysis was 101.7%.
Stability of Desorbed Samples
4.11. Chromatograms A chromatogram at the detection limit of the analytical procedure is shown in Figure 4.1. and a chromatogram at the target concentration is shown in Figure 4.11.1. A chromatogram at target concentration under the alternate analytical conditions is shown in Figure 4.11.2. 4.12. Standardization of MEK peroxide solution
Round-bottomed flask 4.12.2. Reagents Hydrogen peroxide, 30% aqueous solution 4.12.3. Synthesis of MEK peroxide monomer Place methyl ethyl ketone (3.6 g, 0.05 mole) and 30% hydrogen peroxide (11.3 g, 0.1 mole) in a 20-mL scintillation vial. Cap the vial and shake to mix well. Let stand at room temperature overnight. Heat the vial in a 40°C water bath for 1 h. Dilute the mixture in 500 mL of methyl t-butyl ether and wash twice with a saturated aqueous solution of ammonium sulfate and twice with water. Dry over anhydrous magnesium sulfate and filter. Evaporate the filtrate under vacuum. The yield of the residue is approximatly 2 g. Add approximately an equal volume of dimethyl phthalate to the residue and store in a freezer. Determine the monomer concentration by iodometric titration. 4.12.4. Synthesis of MEK peroxide dimer Assemble a 500-mL round-bottom flask equipped with a stirring bar and a thermometer in an ice bath. Place methyl ethyl ketone (14.4 g, 0.2 mole) and 30% hydrogen peroxide (22.67 g, 0.2 mole) in the flask. Add sulfuric acid (0.49 g, 0.005 mole) slowly with stirring so that the temperature does not rise above 15°C. Continue stirring at room temperature overnight. Take up the mixture in 500 mL of hexane and wash twice with saturated aqueous solution of ammonium sulfate and three times with 300 mL of water. Dry over anhydrous magnesium sulfate and filter. Chill the filtrate in an 2-propanol/liquid nitrogen bath. Collect the precipitated white crystals. Recrystallize from hexane, mp 43-49°C. The yield is approximately 5 g. Determine the dimer purity by iodometric titration. It should be near 100%. Store in a freezer. 4.12.5. Iodometric titration of MEK peroxides (Ref. 5.16.) Standardize the 0.01 N sodium thiosulfate solution with a potassium dichromate primary standard. Prepare stock solutions of monomer and dimer in 2-propanol. The concentration should be approximately 5 mg/mL. Place 20 mL of 2-propanol, 2 mL of glacial acetic acid, and 0.5 g of potassium iodide in a 500-mL Erlenmeyer flask. Add 1.0 mL of the MEK peroxide stock solution. Allow the flask to stand in the dark for 15 min. Add 10 mL of water and titrate the solution with 0.01 N sodium thiosulfate solution. Perform blank corrections. Calculate the purity of the monomer and dimer as follows.
1 = MEK peroxide dimer, 2 = MEK peroxide monomer.
1 = MEK peroxide dimer, 2 = MEK peroxide monomer.
1 = MEK peroxide monomer, 2 = oxygen, 3 = MEK peroxide dimer.
5.2. Purnell, C.J., Martin, G.L., and Wolfson,
H., "Determination of Airborne Methyl Ethyl Ketone Peroxide in the
Glass Reinforced Plastics Industry", Ann. Occup. Hyg.,
1979, Vol. 22, No. 4, pp. 5.3. Method No. P&CAM 331 in "NIOSH Manual of Analytical Methods", 2nd edition, U.S. Department of Health, Education, and Welfare, Public Health Services, Center for Disease Control, NIOSH, DHEW(NIOSH) Publication No. 77-157-A. 5.4. Method No. 3508 in "NIOSH Manual of Analytical Methods", 3rd edition, 1985 Supplement, U.S. Department of Health and Human Services, Center for Disease Control, NIOSH; Cincinnati, OH, 1986. 5.5. "Documentation of the Threshold Limit Values and Biological Exposure Indices", American Conference of Governmental Industrial Hygienists Inc.: Cincinnati, OH, 5th ed. 1986. 5.6. Thomas, A., Jacyszyn, O., Schmitt, W. and Kolczynski, J., "Methyl Ethyl Ketone Peroxides, Relationship of Reactivity to Chemical Structure", 32nd Annual Technical Conference, 1977, Reinforced Plastics/Composites Institute, The Society of the Plastics Industry, Inc. 5.7. Cassoni, J.P., Harpell, G.A., Wang, P.C. and Zupa, A.H., "Use of Ketone Peroxides for Room Temperature Cure of Thermoset Resins", 32nd Annual Technical Conference, 1977, Reinforced Plastics/Composites Institute, The Society of the Plastics Industry, Inc. 5.8. Milas, N.A. and Golubovic, A., "Studies in Organic Peroxides. XXV. Preparation, Separation and Identification of Peroxides Derived from Methyl Ethyl Ketone and Hydrogen Peroxide", J. Am. Chem. Soc., 1959, 81, 5824-26. 5.9. Denney, D.B., Goodyear, W.F. and Goldstein, B., "Concerning the Mechanism of the Reduction of Hydroperoxides by Trisubstituted Phosphines and Trisubstituted Phosphites", J. Am. Chem. Soc., 1960, 82, 1393-195. 5.10. Shulsky, M., "Evaluation of Sampling and Analytical Methods Specific for Methyl Ethyl Ketone Peroxide", OSHA Analytical Laboratory, 1982. Unpublished. 5.11. Funk, M.O., Keller, M.B. and Levison, B., "Determination of Peroxides by High Performance Liquid Chromatography with Amperometric Detection", Anal. Chem., 1980, 52, 771-773. 5.12. Cummins, K., "Analysis of Methyl Ethyl Ketone Peroxide by HPLC and Detection by Electrochemical Reduction Using a Mercury-Gold Electrode", OSHA Analytical Laboratory, 1988. Unpublished. 5.13. Deelder, R.S., Kroll, M.G.F. and van den Berg, J.H.M., " Determination of Trace Amounts of Hydroperoxides by Column Liquid Chromatography and Colorimetric Detection", J. Chromatogr., 1976, 125, 307-314. 5.14. Sittig, M., "Handbook of Toxic and Hazardous Chemicals", Noyes Publications, Park Ridge, New Jersey, 1981. 5.15. Sweet, D.V., ed., "Registry of Toxic Effects of Chemical Substances", 1985-86 edition, U.S. Department of Health and Human Services, Government Printing Office, DHHS(NIOSH) Publication No. 87-114. 5.16. Johnson, R.M. and Siddiqi, I.W., The Determination of Organic Peroxides, Pergamon Press, Oxford, 1970.
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