RESORCINOL
Method number: |
PV2053 |
|
Matrix: |
Air |
|
Target concentration: |
10 ppm (45 mg/m3) OSHA TWA PEL 20 ppm (90
mg/m3) OSHA STEL (Note: These are the 1989 levels
which have subsequently been rescinded.) |
|
Procedure: |
Samples are collected by drawing a known volume of air through
an OVS-7 tube. Samples are desorbed with methanol and
analyzed by gas chromatography with a flame ionization detector
(GC-FID). |
|
Air volume and sampling rate studied: |
60 liters at 1.0 Lpm |
|
Status of method: |
Stopgap method. This method has been only partially evaluated
and is presented for information and trial use. |
|
Date: March, 1992 Revised: March, 1994 |
Chemist: Mary E.
Eide |
Organic Service Branch I OSHA Salt Lake Technical
Center Salt Lake City, Utah
1. General Discussion
1.1. Background
1.1.1. History of procedure
The OSHA Technical Center has received many requests for a
sampling and analytical procedure for resorcinol. OSHA promulgated
an exposure standard for resorcinol in January, 1989, at a level of
10 ppm TWA, and 20 ppm STEL. OSHA method 32 recommends collection of
phenol and cresol on XAD-7 tubes and desorption with
methanol (Ref. 5.1.). Resorcinol is related to these compounds, and
resorcinol occurs as a particulate as well as a vapor, so an
OVS-7 tube was tried. An OVS-7 tube is a
glass fiber filter in front of a 270 mg section of
XAD-7 resin followed by a 140 mg section of
XAD-7 resin. The desorption, retention and storage
studies all had good recoveries.
1.1.2. Potential workplace exposure (Ref. 5.2.)
Resorcinol is used in the tanning and dyeing industries; in the
manufacture of resins and resin adhesives, explosives, hexyl
resorcinol, p-aminosalicylic acid, cosmetics, and as an antiseptic
and topical antipruritic.
1.1.3. Toxic Effects (This section is for information purposes
and should not be taken as the basis for OSHA policy.)(Ref. 5.3.)
Resorcinol is a skin, eye, and mucous membrane irritant. Exposure
to resorcinol causes, with increasing exposure, skin burns,
cyanosis, methemoglobinemia, convulsions, and death. It was found to
be less toxic than phenol, but with similar toxic effects.
1.1.4. Physical properties (Ref. 5.2.):
Compound: |
|
Synonyms: |
1,3-Benzenediol; Resorcin;
m-Dihydroxybenzene; C.I. 76505; C.I. Developer 4;
C.I. Oxidation base 31; Developer O; Developer R; Developer
RS; Fouramine RS; Durafur developer G; Fourrine 79; Fourrine
EW; m-Hydroquinone;
3-Hydroxycyclohexadiene-l-one; m-Hydroxyphenol |
Molecular weight: |
110.11 |
Melting point: |
110°C |
Boiling point: |
280°C |
Flash point: |
127°C (261°F)(closed cup) |
Odor: |
phenolic |
Color: |
white, turns pink on exposure to light or
air |
Molecular formula: |
C6H6O2 |
CAS: |
108-46-3 |
IMIS: |
2221 |
RTECS: |
VG962500; 76367 |
DOT: |
UN2876 (Poison) |
1.2. Limit defining parameters
1.2.1. The detection limit of the analytical procedure is 8 µg
resorcinol. This is the smallest amount that could be detected under
normal operating conditions.
1.2.2. The overall detection limit is 0.0889 ppm. (All ppm
amounts in this study are based on a 20 L air volume.)
1.3. Advantages
1.3.1. The sampling procedure is convenient.
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.
1.4. Disadvantages
none known
2. Sampling procedure
2.1. Apparatus
2.1.1. A calibrated personal sampling pump, the flow of which
can be determined within ± 5% at the recommended flow.
2.1.2. An OVS-7 tube is a 13 mm glass fiber filter
in front of a 270 mg section of XAD-7 resin followed by
a 140 mg section of XAD-7 resin 15/50 mesh, with foam
plugs before and after the back XAD-7 section. The ends
are sealed with plastic caps.
2.2. Sampling technique
2.2.1. Open the ends of the OVS-7 tubes immediately
before sampling.
2.2.2. Connect OVS-7 tubes to the sampling pump with
flexible tubing.
2.2.3. Place the tubes 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 OVS-7 tubes.
2.2.5. Seal the OVS-7 tubes 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
container from other samples.
2.3. Desorption and Extraction efficiency
2.3.1. Six glass fiber filters were spiked at loadings of 0.298
mg (1.10 ppm), 1.49 mg (5.51 ppm), 2.98 mg (11.0 ppm), and 5.96 mg
(22.1 ppm) resorcinol. They were allowed to equilibrate overnight at
room temperature. They were opened, desorbed with 2 mL of methanol
for 30 minutes with shaking, and analyzed by GC-FID.
The overall average was l00%.(Table 1)
Table 1 Extraction Efficiency of Glass Fiber
Filters
|
Filter# |
|
% Recovered |
|
0.298 mg |
1.49 mg |
2.98 mg |
5.96 mg |
|
1 |
102 |
96.8 |
99.3 |
99.6 |
2 |
98.9 |
99.4 |
98.8 |
100 |
3 |
102 |
96.8 |
102 |
98.8 |
4 |
101 |
101 |
98.9 |
99.8 |
5 |
97.6 |
103 |
99.8 |
102 |
6 |
102 |
103 |
100 |
100 |
average |
101 |
100 |
99.8 |
100 |
|
overall average 100 |
|
standard deviation ±
1.78 |
|
|
2.3.2. Six front portions of XAD-7 resin from the
OVS-7 tubes were spiked at loadings of 89.9 µg (0.333
ppm), 450 µg (1.67 ppm), and 899 µg (3.33 ppm) resorcinol. They were
allowed to equilibrate overnight at room temperature. They were
opened, each section placed into a separate 2 mL vial, desorbed with
2 mL of methanol for 30 minutes with occasional shaking, and
analyzed by GC-FID. The overall average was 100%.(Table
2)
Table 2 Desorption Efficiency of XAD-7
|
Tube# |
|
% Recovered |
|
89.9 µg |
450 µg |
899 µg |
|
1 |
101 |
98.3 |
100 |
2 |
98.0 |
96.8 |
101 |
3 |
99.4 |
100 |
102 |
4 |
102 |
101 |
99.2 |
5 |
97.3 |
102 |
99.6 |
6 |
102 |
102 |
101 |
average |
100 |
100 |
100 |
overall average 100 |
|
standard deviation ±
1.71 |
|
|
2.4. Retention efficiency
Nine OVS-7 tubes had the glass fiber filter (GFF)
removed and placed above the Teflon spacer 1/2" above the front
XAD-7 resin section. The glass fiber filters were liquid
spiked with 5.96 mg (22.1 ppm) resorcinol, allowed to equilibrate
overnight, and then six tubes had 60 liters humid air (91% RH at 22°C)
and three had 180 liters humid air (87% RH at 21°C) pulled through
them. They were opened, desorbed and analyzed by GC-FID.
The retention efficiency averaged 99.7%. There was no resorcinol found
on the backup portions of the tubes.(Tables 3 and 4)
Table 3 Retention Efficiency with 60 liters Humid
Air
|
Tube # |
% Recovered |
% Recovered |
% Recovered |
Total |
|
GFF |
Front XAD-7 |
Back XAD-7 |
|
|
1 |
96.9 |
2.4 |
0.0 |
99.3 |
2 |
98.6 |
2.6 |
0.0 |
101 |
3 |
94.1 |
5.7 |
0.0 |
99.8 |
4 |
96.8 |
2.8 |
0.0 |
99.6 |
5 |
95.6 |
2.9 |
0.0 |
98.5 |
6 |
97.5 |
2.4 |
0.0 |
99.7 |
|
average |
99.7 |
|
Table 4 Retention Efficiency with 180 liters Humid
Air
|
Tube # |
% Recovered |
% Recovered |
% Recovered |
Total |
|
GFF |
Front XAD-7 |
Back XAD-7 |
|
|
1 |
91.8 |
7.8 |
0.0 |
99.6 |
2 |
92.0 |
7.4 |
0.0 |
99.4 |
3 |
93.0 |
7.2 |
0.0 |
100 |
|
average |
99.7 |
|
2.5. Storage
Tubes were spiked with 899 µg (9.98 ppm) resorcinol and stored at
room temperature until opened and analyzed. Since resorcinol may
decompose in light, half of the tubes were stored under room light,
and half were stored in darkness. The samples were found to be stable,
for the 14 days stored, under both conditions. The recoveries averaged
98.5%.(Table 5)
Table 5 Storage Study
|
Day |
% Recovered light |
% Recovered dark |
|
7 |
101 |
101 |
7 |
98.1 |
96.1 |
7 |
lost |
99.0 |
14 |
102 |
98.5 |
14 |
97.9 |
94.7 |
14 |
101 |
94.2 |
overall average |
98.5 |
|
|
2.6. Precision
The precision was calculated using the area counts from six
injections of each standard at concentrations of 89.9, 450, 899, and
1798 µg/mL resorcinol in the desorbing solution. The pooled
coefficient of variation was 0.00924.(Table 6)
Table 6 Precision Study
|
Injection |
|
Number |
89.9 µg/mL |
450 µg/mL |
899 µg/mL |
1798 µg/mL |
|
1 |
15459 |
84017 |
157575 |
300122 |
2 |
15037 |
84092 |
157999 |
298006 |
3 |
15436 |
83171 |
156893 |
300985 |
4 |
15610 |
82527 |
158541 |
298940 |
5 |
15068 |
82572 |
156349 |
299382 |
6 |
15323 |
82670 |
158489 |
300375 |
Average |
15322 |
83175 |
157641 |
299635 |
Standard |
|
Deviation |
± 228 |
720 |
882 |
1078 |
CV |
0.0149 |
0.00866 |
0.00560 |
0.00360 |
Pooled CV |
0.00924 |
|
|
where:
A(1), A(2),A(3),A(4) = # of injections at each
level CVl, CV2, CV3, CV4 = Coefficients at each level
2.7. Air volume and sampling rate studied
2.7.1. The air volume studied is 60 liters.
2.7.2. The sampling rate studied is 1.0 liters per minute.
2.8. Interferences
Suspected interferences should be listed on sample data sheets.
2.9. Safety precautions
2.9.1. Sampling equipment should be placed on an employee in a
manner that does not interfere with work performance or safety.
2.9.2. Safety glasses should be worn at all times in designated
areas.
2.9.3. Follow all safety practices that apply to the workplace
being sampled.
3. Analytical method
3.1. Apparatus
3.1.1. Gas chromatograph equipped with a flame ionization
detector. A HP5890 gas chromatograph was used in this study.
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 30 meter DB-225 capillary column, 0.25 µ
d.f., 0.32 mm I.D. An alternate column is a 60 meter
DB-1 capillary column, 1.0 µ d.f., 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 Reagents
3.2.1. Purified GC grade nitrogen, hydrogen, and air.
3.2.2. Resorcinol, Reagent grade
3.2.3. Methanol, HPLC grade
3.2.4. Dimethyl formamide, Reagent grade
3.2.5. Desorbing solution is methanol with 1 µL/mL dimethyl
formamide used as an internal standard.
3.3. Sample preparation
3.3.1. Sample tubes are opened and the glass fiber filter,
front, and back sections of each tube are placed in separate 4 mL
vials. If particulate analysis is not desired the glass fiber filter
is added to the vial containing the front section.
3.3.2. Each section is desorbed with 2 mL of the desorbing
solution.
3.3.3. The vials are sealed immediately and allowed to desorb for
30 minutes with occasional shaking.
3.3.4. An aliquot was removed and placed into 2 mL vials for
analysis with the autosampler. This step may not be necessary,
depending on the type of instrumentation used for analysis.
3.4. Standard preparation
3.4.1. Standards are prepared by diluting a known quantity of
resorcinol with the desorbing solution.
3.4.2. At least two separate stock standards should be made, and
dilutions bracketing the samples are prepared. In this study, the
analytical standards ranged from 8 to 5960 µg/mL resorcinol in the
desorbing solution.
3.5. Analysis
3.5.1. Gas chromatograph conditions DB-225
capillary column.
Flow rates (mL/min) |
Temperature (°C) |
Nitrogen(makeup) |
:30 |
Injector |
:240 |
Hydrogen(carrier) |
:1.5 |
Detector |
:240 |
Air |
:450 |
Column |
:110°-1 min |
Hydrogen(detector) |
:30 |
|
4°C/min-160°C |
Injection size |
:1 µL |
Elution time |
:22.566 min |
Chromatogram |
:(See Figure 1) |
3.5.2. Gas chromatograph conditions DB-1 capillary
column.
Flow rates (mL/min) |
Temperature (°C) |
Nitrogen(makeup) |
:30 |
Injector |
:220 |
Hydrogen(carrier) |
:1.5 |
Detector |
:240 |
Air |
:450 |
Column |
:80°-0 min |
Hydrogen(detector) |
:30 |
|
10°C/min-220°C |
Injection size |
:1 µL |
Elution time |
:14.077 min |
Chromatogram |
:(See Figure 2) |
3.5.3. Peak areas are measured by an integrator or other suitable
means.
3.6. Interferences (analytical)
3.6.1. Any compound having the general retention time of the
analyte or the internal standard used is an interference. Possible
interferences should be listed on the sample data sheet. GC
parameters should be adjusted if necessary so these interferences
will pose no problems.
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
3.7.1. A curve with area counts versus concentration is
calculated from the calibration standards.
3.7.2. The area counts for the samples are plotted with the
calibration curve to obtain the concentration of resorcinol in
solution.
3.7.3. To calculate the concentration of analyte in the air
sample the following formulas are used:
(µg/m) (desorption volume)
(desorption efficiency) |
= mass of analyte in
sample |
(mass of analyte in sample)
molecular weight |
= number of moles of
analyte |
(number of moles of
analyte) |
(molar volume at 25°C &
760mm) |
= |
volume the analyte
will occupy at 25°C & 760mm |
(volume analyte occupies)
(106)*
(air volume) |
= ppm |
* 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 20 liter air sample:
(µg/mL)(DV)(24.45)(106)
(60 L)(DE)(MW) |
× |
(g)
(1000 mg) |
× |
(mg)
(1000 µg) |
= ppm |
µg/mL |
= |
concentration of analyte in sample or standard |
24.45 |
= |
Molar volume (liters/mole) at 25° and 760 mm Hg. |
MW |
= |
Molecular weight (g/mole) |
DV |
= |
2 mL Desorption volume |
60 L |
= |
10 liter air sample |
DE |
= |
Desorption efficiency |
3.7.5. This calculation is done for each section of the sampling
tube and the results added together.
3.8. Safety precautions
3.8.1. All handling of solvents should be done in a hood.
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
A collection study should be performed.
Figure 1. An analytical standard of 450 µg/mL resorcinol
in methanol with 1 µL/mL dimethyl formamide internal
standard.
Figure 2. An analytical standard of 450 µg/mL resorcinol
in methanol with 1 µL/mL dimethyl formamide internal
standard.
5. References
5.1. Cummins,K., Method 32, "Phenol and Cresol", Organic Methods
Evaluation Branch, OSHA Salt Lake Technical Center, 1986.
5.2. Windholz, M., "The Merck Index", Eleventh Edition, Merck &
Co., Rahway N.J., 1989, p. 1176.
5.3. "Documentation of the Threshold Limit Values and Biological
Exposure Indices", Fifth Edition, American Conference of Governmental
Industrial Hygienists Inc., Cincinnati, OH, 1986, p. 511.
|