ISOOCTYL ALCOHOL
Organic Service Branch I 1. General Discussion
OSHA promulgated an exposure standard for isooctyl alcohol in January, 1989, at a level of 50 ppm. This study was undertaken to gather the data necessary to verify the procedure we had been recommending. The procedure for collection (charcoal tubes) and analysis (GC/FID) of isooctyl alcohol described in this evaluation is basically that used in OSHA method 07.(Ref. 5.1.) Isooctyl alcohol contains several peaks that elute over a time range of 1 minute. A solution of 1 mL of 1:99 dimethyl formamide: carbon disulfide gives a constant desorption of 92.3% over the range of 0.25 mg to 2.49 mg. Isooctyl alcohol had good retention and storage efficiencies on charcoal tubes. 1.1.2. Potential workplace exposure (Ref. 5.2.) Isooctyl alcohol is used to form esters (such as phthalates) for plasticizing vinyl and other resins. 1.1.3. Toxic Effects (This section is for information purposes and should not be taken as the basis for OSHA policy.)
Toxilogical data for isooctyl alcohol was unavailable. Documentation of Threshold Limit Values
and Biological Exposure Indices contained data for 1.1.4. Physical properties (Ref. 5.3.):
1.2. Limit defining parameters
1.2.2. The overall detection limit is 0.78 ppm. (All ppm values in this study are based on a 10 L air volume.)
1.3.2. The analytical method is reproducible and sensitive. 1.3.3. Reanalysis of samples is possible. 1.3.4. It may be possible to analyze other compounds at the same time. 1.3.5. Interferences may be avoided by proper selection of column and GC parameters.
2.1.2. Charcoal tubes, lot 120, containing 100 mg adsorbing section with a 50 mg backup section separated by a 2 mm portion of urethane foam, with a silanized glass wool plug before the adsorbing section and a 3 mm plug of urethane foam at the back of the backup section. The ends are flame sealed and the glass tube containing the adsorbent is 7 cm long, with a 6 mm O.D. and 4 mm I.D., SKC tubes or equivalent.
2.2.2. Connect the charcoal tube to the sampling pump with flexible tubing. 2.2.3. Tubes should be placed in a vertical position to minimize channeling, with the smaller section towards the pump. 2.2.4. Air being sampled should not pass through any hose or tubing before entering the charcoal tube. 2.2.5. Seal the charcoal tube with plastic caps immediately after sampling. Seal each sample lengthwise with OSHA Form-21 sealing tape. 2.2.6. With each batch of samples, submit at least one blank tube from the same lot used for samples. This tube should be subjected to exactly the same handling as the samples (break ends, seal, & transport) except that no air is drawn through it. 2.2.7. Transport the samples (and corresponding paperwork) to the lab for analysis. 2.2.8. bulks submitted for analysis must be shipped in a separate mailing container from other samples.
Six tubes were liquid spiked at loadings of 0.25 mg (4.67 ppm), 0.83 mg (15.6 ppm), and 2.49 mg (46.7 ppm) isooctyl alcohol. They were allowed to equilibrate overnight at room temperature. They were opened, each section placed into a separate 2 mL vial, desorbed with 1 mL of 1:99 dimethyl formamide: carbon disulfide for 30 minutes with occasional shaking, and analyzed by GC-FID. The overall average was 92.3% recovered.(Table 1) Values for the retention efficiency and the storage study were corrected for the desorption efficiency.
Desorption Efficiency
2.4. Retention efficiency
Six tubes were liquid spiked with 2.49 mg (46.7 ppm) isooctyl alcohol, allowed to equilibrate overnight, and
then had 10 liters humid air (85% RH) pulled through them. They were opened, desorbed and analyzed by
Retention Efficiency
2.5. Storage Tubes were spiked with 2.49 mg (46.7 ppm) isooctyl alcohol and stored at room temperature until opened and analyzed. The recoveries averaged 102% for the 14 days stored.(Table 3)
Storage Study
2.6. Precision The precision was calculated using the area counts from six injections of each standard at concentrations of 0.25, 0.83, 2.49 mg/mL isooctyl alcohol in 1:99 dimethyl formamide: carbon disulfide. The pooled coefficient of variation was 0.0115.(Table 4)
Precision Study
where:
A(1), A(2),A(3),A(4) = # of injections at each level 2.7. Air volume and sampling rate studied
2.7.2. The sampling rate studied is 0.2 liters per minute.
Suspected interferences should be listed on sample data sheets. 2.9. Safety precautions
2.9.2. Safety glasses should be worn at all times. 2.9.3. Follow all safety practices that apply to the workplace being sampled. 3. Analytical method
3.1.2. GC column capable of separating the analyte and an internal standard from any interferences. The column used in this study was a 60 meter DB-WAX capillary column 1.0µ d.f., and 0.32 mm I.D. 3.1.3. An electronic integrator or some other suitable method of measuring peak areas. 3.1.4. Two milliliter vials with Teflon-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. The Glenco 1 mL dispenser was used in this method. 3.1.7. Volumetric flasks - 5 mL and other convenient sizes for preparing standards.
3.2.2. Isooctyl alcohol, Reagent grade 3.2.3. Carbon disulfide, Reagent grade 3.2.4. Dimethyl formamide, HPLC grade 3.2.5. p-Cymene, Reagent grade 3.2.6. The desorbing solution is 0.25 µL/mL p-cymene in 1:99 dimethyl formamide:carbon disulfide.
3.3.2. Each section is desorbed with 1 mL of desorbing solution. 3.3.3. The vials are sealed immediately and allowed to desorb for 30 minutes with occasional shaking.
3.4.2. At least two separate standards should be made. These standards should be within ± 5%, and then are averaged. 3.4.3. A third analytical standard should be prepared at a higher concentration to check for linearity of the calibration. For this study two standards at 1 µL/mL (0.830 mg/mL) and one standard at 4 µL/mL (3.32 mg/mL) isooctyl alcohol were used. 3.5. Analysis
3.5.2. Peak areas are measured by an integrator or other suitable means. The peak areas were summed. 3.6. Interferences (analytical)
3.6.2. Retention time data on a single column is not considered proof of chemical identity. Samples over the target concentration should be confirmed by GC/Mass Spec or other suitable means. 3.7. Calculations
3.7.2. The area counts for the samples are plotted with the calibration curve to obtain the concentration of isooctyl alcohol in solution. 3.7.3. To calculate the concentration of analyte in the air sample the following formulas are used:
* All units must cancel. 3.7.4. The above equations can be consolidated to form the following formula. To calculate the ppm of analyte in the sample based on a 10 liter air sample:
3.7.5. This calculation is done for each section of the sampling tube and the results added together. 3.8. Safety precautions
3.8.2. Avoid skin contact with all chemicals. 3.8.3. Wear safety glasses, gloves and a lab coat at all times. 4. Recommendations for further study Collection studies should be performed.
Figure 1. An analytical standard of 0.25 mg/mL isooctyl alcohol in 1:99 dimethyl formamide:carbon disulfide with 0.25 µL/mL 5. References
5.2. "Kirk-Othmer Encyclopedia of Chemical Technology", Second
Edition, John Wiley & Sons, Inc., New York, 1967, Vol. 14, 5.3. "Documentation of the Threshold Limit Values and Biological Exposure Indices", Fifth Edition, American Conference of Governmental Industrial Hygienists, Inc., Cincinnati, 1986, p. 332. 5.4. Chem Service, Inc., Material Safety Data Sheet (MSDS) for Isooctyl Alcohol, July 1991. |