1. introduction
1.1 Scope
This method describes
the collection and analysis of airborne butyltin trichloride (BTTC) as
adapted from the standard test method of M & T Chemicals, Inc.
(Reference 1). The analysis is based on the organic solvent desorption
of glass fiber filters and the technique of graphite furnace atomic
absorption spectroscopy.
The collective threshold limit value
(TLV) for organotin compounds has been adopted at 0.1 mg/m³ in the
workplace environment. This procedure may be applied to other organotins
as well.
1.2 History and Background
Historically,
manufacturers have used SnCl2 in sensitizing glass and
plastic before metalizing. However, they have currently been using
butyltin trichloride for that purpose.
The particulate matter is
collected from air on a glass fiber filter, followed in line by an XAD-2
tube containing a synthetic amberlite resin. The entire GFF and backup
pad are removed from the cassette and extracted with toluene-acetic
acid.
Aliquots of both the GFF extract and the XAD extract are
introduced into the graphite furnace and the absorbance is read at
286.4nm.
1.3 Uses
Butyltin trichloride is used as a
manufacturing intermediate, a catalyst, and a stabilizer (Reference
2).
1.4 Physical and Chemical Properties
Appearance |
: |
Colorless to yellow liquid |
Sp. Gr. |
: |
1.17 (25/4°C) |
B.P. |
: |
101°C (12-mm) |
% Sn |
: |
42.1% (check stock analysis |
Mol. Wt. |
: |
282 | 2.
Range and Detection Limit
2.1 The lower analytical limit for
butyltin trichloride is 0.1 µg/L.
2.2 This is based on a
detection of 0.02 µg/mL for a graphite furnace analysis of BTTC as Sn in
toluene-acetic acid. 3. Precision
and Accuracy
Six glass fiber filters were spiked with l0 µL of 2880
ppm BTTC in toluene based on a 1/2 day air volume of 240 L and the OSHA
standard of 0.1 mg/m³. For these six samples the average recovery was
1.043, the standard deviation was 0.692, and the coefficient of variation
was 0.023.
4. Interferences
Other organotin compounds will
interfere if they are soluble in toluene-acetic acid. Inorganic tin
compounds are to be considered a potential interference if they are not
separated using the tropolone-toluene procedure.
5. Sampling
Procedure
The sample is collected on a glass fiber filter in series
with an XAD-2 tube at a flow rate of 1.0 to 1.5 L/min and a recommended
air volume of 250 L. The sample cassettes and tubes are plugged, sealed
with OSHA Form 21, and sent to the laboratory for analysis as soon as
possible.
6. Analytical Procedure
6.1 Apparatus
6.1.1 Sample
Collection
Personal sampling pumps
Glass fiber filter
sampling cassettes with backup pads XAD-2 tubes
6.1.2 Sample
Analysis
Laboratory Glassware to include volumetric flasks,
50-mL screw cap tubes, assorted pipets.
Atomic absorption
spectrophotometer with graphite furnace and electrodeless discharge
lamp for tin. 6.2. Reagents
All reagents should be ACS analyzed reagent grade or
better
6.2.1 Glacial Acetic Acid
6.2.2
Toluene
6.2.3 Stock Butyltin Trichloride
6.3 Safety Precautions (Reference
3)
6.3.1 Use caution when handling all
organotin compounds, toluene, and the glacial acetic acid. Butyltin
trichloride is a harmful liquid, readily absorbed through the skin,
corrosive, and combustible. Glacial acetic acid will cause severe
burns, is harmful if inhaled, and is combustible with a flashpoint of
103°F. Toluene is a flammable liquid and its vapors should not be
inhaled. Waste organics should be collected in a suitable marked
container and properly disposed. Always use rubber gloves and work in
a fume hood. Observe warning labels on reagent bottles.
6.3.2
Avoid using glassware with chips, stars, or sharp edges. Never pipet
any of these materials by mouth.
6.3.3 Before using the
graphite furnace, the analyst should read the operator's manual and be
familiar with the equipment. Ensure that the furnace tube is properly
seated, the contact rings are clean, the cooling water is circulating
sufficiently, and that the argon pressure will be constant for the
entire analysis.
Always wear safety glasses and never look at
the tube during atomization. Even during normal firing, the intense
light is harmful to the eyes.
Be aware of the high current
supplied to the furnace through the copper cables; check that the
insulating cover is in place over the terminals.
Since toxic
substances are vented by the furnace, a fume hood must be in operation
over the furnace.
6.3.4 Observe care with respect to harming
the equipment. Do not operate an EDL below its recommended wattage. Be
certain that the purge air is circulating when using the background
corrector. Do not operate any of the equipment without first reading
its instruction manual. 6.4
Glassware Preparation
6.4.1 All glassware must be
scrupulously cleaned with concentrated HCl by soaking for several
hours or overnight and then rinsing several times with deionized
water. Cleaning time for sample glassware may he shortened to rinsing
with concd. HCL, DI water, and then finally with toluene.
6.5 Standard Preparation
6.5.1 The procedure is to analyze the
tin in butyltin trichloride. Prepare the standards by dissolving
0.04751 grams of BTTC neat liquid in 40 mL glacial acetic acid and
dilute to 200 mL volume. This will be a 100 ppm stock solution as Sn,
assuming a theoretical tin content of 42.1%.
6.5.2 Prepare an
intermediate stock solution (10 ppm as Sn) by diluting 10 mL of the
100 ppm stock to volume with glacial acetic acid in a 100 mL
volumetric flask.
6.5.3 Prepare four working standards from the
10 ppm intermediate stock as follows:
Std
Prepared |
Std Soln
Used |
Aliquot |
Dil Vol |
|
1.0 ppm |
|
10.0 ppm |
|
10 mL |
|
100 mL |
|
0.5 ppm |
|
1.0 ppm |
|
25 mL |
|
50 mL |
|
0.1 ppm |
|
1.0 ppm |
|
5 mL |
|
50 mL |
|
0.05 ppm |
|
0.5 ppm |
|
5 mL |
|
50 mL |
| The 1.0 ppm working standard is diluted to volume with
toluene and the other three working working standards are diluted to
volume using 10% glacial acetic acid in toluene.
6.6 Sample Preparation
Transfer
the glass fiber filter and XAD-2 tube sections A and B to separate screw
cap tubes.
6.6.2 Pipet 5 mL of glacial acetic
acid into each screw cap tube, shake for 5 minutes, and let stand for
one hour.
6.6.3 Pipet 25 mL of toluene into each screw cap tube
and then shake for 30 minutes.
6.6.4 if subsequent dilutions
are necessary, use the toluene-acetic acid solution.
6.7 Analysis
The analysis is
done by graphite furnace atomic absorption spectrophotometry. Instrument
parameters for determining tin in toluene-acetic acid are as follows:
Atomic absorption spectrophotometer parameters
Sn wavelength |
286.4nm |
Integration time |
10 sec |
Slit width |
.7 low |
Mode |
Absorbance |
BGC |
on | Graphite furnace parameters
Step |
Temperature |
Ramp Time |
Hold Time |
Internal
Flow |
|
dry |
100°C |
|
30 sec |
|
10 sec |
|
30 mL/min |
|
char |
800°C |
|
30 sec |
|
10 sec |
|
30 mL/min |
|
atomize |
2500°C |
|
0 sec |
|
8 sec |
|
0 mL/min |
|
6.7.1 Chart Settings |
Range 10 = mV full scale Chart
= 20 mm/min | 6.7.2
Parameters are adjusted so that the 1.0 ppm working standard gives
near full-scale deflection on the chart. All calibration standards are
run at the beginning and end of the analysis; a standard is also run
after every five samples during the analysis. 6.8 Calculations
6.8.1 Either the OSHA Auto-AA program
or the Auto-Colorimetric program is used for the
calculations.
6.8.2 Results are reported as mg/m³ Sn based on
the total micrograms of organotin (as Sn) and the air volume.
7. Recovery Study
A
recovery study of BTTC from glass fiber filters and XAD-2 tubes was done
by desorption in toluene-acetic acid.
One milliliter of BTTC was
measured into a 250 mL volumetric flask, diluted to volume with toluene,
and mixed. Assuming the BTTC is 42.1% tin, this is equivalent to 2860 ppm
BTTC (as Sn). Six glass fiber filters were spiked with 10 µL of the 2860
PPM BTTC (or 28.8 µg).
The spiked filters were air dried on a large
white test tube rack and placed on a backup pad in a plastic cassette.
Each cassette was attached to a Dupont P-4000 air sampling pump with an
XAD-2 tube in line behind the filter cassette. A seventh cassette, tube,
and pump were set up to be used as an air blank. Between 200 and 300
liters of air was drawn through the filters and XAD tubes, after which the
filters and tubes were removed, placed into separate 50 mL screw cap
tubes, and desorbed with toluene-acetic acid according to the procedure
described in Section 6.6 for sample preparation. The samples were then
analyzes by graphite furnace and the statistical data are shown as
follows:
BTTC Recovery Study Results
|
GF-1 + BP = 20.14 +
9.02 |
= |
29.2 |
GF-2 + BP = 21.36 +
8.29 |
= |
29.6 |
GF-3 + BP = 20.78
+10.34 |
= |
31.1 |
GF-4 + BP = 21.75 +
8.80 |
= |
30.6 |
GF-5 + BP = 20.46 +
9.64 |
= |
30.1 |
GF-6 + BP = 21.49 +
8.29 |
= |
29.8 |
AVE. |
= |
30.1 |
|
|
|
Average Recovery |
= |
1.043 |
Standard Deviation |
= |
0.62 |
Coefficient of Variation |
= |
0.023 | For this recovery study, there was no BTTC detected in any
of the XAD-2 tubes and the backup pads were analyzed separately. In future
work the backup pads and glass fiber filters may be desorbed in the same
screw cap tube (i.e., analyzed together).
8. References
1.
"Determination of Butyl Organotin Compounds in Air Samples by AAS-Graphite
Furnace", Standard Test Methods, Method No. AA-62, M&T Chemicals,
Inc., June 6, 1984.
2. G.G. Hauley, Condensed Chemical Dictionary,
9th Edition, p. 142, 1977.
3. Bis(Tributyltin) Oxide, OSHA
Laboratory Method, Method No.ID-102-SG, Unpublished,
1984.
|