1. Introduction
1.1 Scope
This method describes the collection and
analysis Of airborne tributyltin fluoride (TBTF). It is applicable for
time-weighted average exposure evaluations. The analysis is based on the
technique of graphite furnace atomic absorption.
1.2 Physical
and Chemical Properties
(C4H9)3 SnF |
Mol. wt. |
- |
309.04 |
Crystal |
% Sn |
- |
3
8.41 | 2. Range
and Detection Limit
2.1 The lower analytical limit for TBTF is 0.1
µg/ml.
2.2 This is based on a detection limit of .02 µg/ml for
graphite furnace analysis of Sn as TBTF in 1-propanol. 3.
Precision and Accuracy
3.1 Precision |
S = 0.019 |
3.2 Coefficient of Variation |
CV = 0.019 |
3.3 Recovery |
Average mean recovery =
0.996 | The above are
based on recovery data for eighteen FWSB-PVC filters, spiked with TBTF
in 1-propanol at 1/2, 1, and 2× the PEL based on a 200 liter air volume
and 0.1 mg/m³ PEL. Six samples were spiked at each level. Refer to
addendum for data on recovery study. 4. Interferences
Other organotins would interfere if
they are insoluble in 1-propanol.
5. Sampling Procedure
The
sample is collected on a FWSB-PVC filter (0.8 µm, 37 nm diameter) at a
flow rate of 1-2 L/min.
The recommended air volume is 200 L.
The sample cassettes are plugged, sealed with OSHA tape, labeled,
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 AA sampling cassettes as
needed.
6.1.2 Sample analysis
Atomic absorption
spectrophotometer HGA graphite furnace Electrodeless discharge
lamp for Sn Laboratory glassware 6.2 Reagents
All reagents should be ACS analyzed
reagent grade or better.
6.2.1 1-Propanol
6.2.2 Stock
tributyltin fluoride 6.3 Safety
precautions
6.3.1 Use caution when handling
1-propanol and organotins. Tributyltin fluoride is a toxic compound.
Always wear rubber gloves and work under a fume hood. Waste organics
should be collected in a suitable marked container and properly
disposed of in the organic laboratory.
6.3.2 Avoid using
glassware with chips or sharp edges. Never pipette 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, and that cooling water is circulating. Do not exceed an
atomization temperature of 2750 degrees. Heating or cooling problems
could cause the tube to explode on atomization.
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 equipment without first reading its instruction
manual. 6.4 Glassware
Preparation
6.4.1 Clean the 50 mL volumetric
flasks by refluxing with 1:1 nitric acid. Thoroughly rinse all
glassware with D.I. water, invert, and allow to dry.
6.5 Standard Preparation
6.5.1 The procedure is to analyze the
tin in tributyl tin fluoride. Prepare the standards by diluting stock
TBTF in 1-propanol assuming a theoretical tin content of 38.41%.
6.5.2 Prepare a stock solution by weighing 0.26035 g TBTF into
a 100 ml volumetric flask, diluting to volume with 1-propanol and
mixing well. This is equivalent to 1000 ppm Sn.
From this, a 10
ppm Sn stock solution is made by two serial 10-fold
dilutions.
6.5.3 Working standards are prepared from the 10 ppm
Sn stock as follows:
|
Prepared std. |
Std. soln. used |
Aliquot |
Dil. vol. |
|
1.0 ppm |
10.0 ppm |
5 mL |
50 mL |
0.4 ppm |
10.0 ppm |
2 mL |
50 mL |
0.2 ppm |
1.0 ppm |
10 mL |
50 mL |
0.1 ppm |
1.0 ppm |
5 mL |
50 mL |
0.04 ppm |
1.0 ppm |
2 mL |
50 mL |
0.02 ppm |
1.0 ppm |
1 mL |
50
mL | 6.6 Sample
Preparation
Transfer the FWSB-PVC filter to a clean 50 mL
volumetric flask. Add 40 mL 1-propanol to each flask and sonicate for 5
minutes. Dilute to volume with 1-propanol and invert several times to
ensure thorough mixing.
6.7. Analysis
The analysis is done
by graphite furnace/AA. The instrumental parameters for determining Sn
in 1-propanol are as follows:
Atomic absorption
unit: |
|
Sn wavelength |
224.6 nm |
integ. time |
10 sec. |
slit width |
0.7 low |
signal |
Pk. Ht. |
mode |
Abs. |
BGC |
on |
Furnace parameters:
|
|
step |
temperature |
ramp time |
hold time |
internal flow |
|
dry |
100 C |
50 s |
40 s |
50 mL/min |
char |
800 C |
50 s |
20 s |
50 mL/min |
atomize |
2500 C |
0 s |
8 s |
30 mL/min |
|
(with HGA 500, program -10
chart and 0 read in atomization step) |
|
Chart = 5 mv scale, 20
mm/min | 6.7.2
Parameters are adjusted so that the 1.0 ppm standard gives a near
full-scale deflection on the chart. The entire series of standards is
run at the beginning and end of the analysis; a standard is also run
after every fourth or fifth sample during the analysis.
6.8 Calculations
6.8.1 The OSHA Auto Colorimetric program is used for the
calculations.
6.8.2 Results are reported as mg/m³ Sn.
Addendum
I
A recovery study of TBTF from FWSB-PVC filters by
desorption in 1-propanol was done.
0.27057 TBTF was weighed into a
100 ml volumetric, diluted to volume with 1- propanol, and mixed. Assuming
the TBTF is 38.41% Sn, this is 1039 ppm Sn as TBTF.
Six FWSB-PVC
filters were spiked at each level = 1/2, 1, and 2× the PEL based on a 200
liter air volume and 0.1 mg/m³ PEL. The spikes were made as
follows:
Std used (ppm Sn) |
Spike Vol. (µl) |
Sn (µg) |
PEL (multiple) |
|
1039 |
10 |
10 |
1/2 × |
1039 |
20 |
20 |
1 × |
1039 |
40 |
40 |
2
× | The filters were then
desorbed in 1-propanol, diluted to 50 mL, and run on the graphite furnace
as described in section 6.7. The mean standard deviation and coefficient
of variation for the recovery at each level using the OSHA "Precision and
Accuracy Data" program =
PEL (multiple) |
Mean Recovery |
Std. Dev. |
CV1 |
|
1/2 × |
1.016 |
0.025 |
0.024 |
1 × |
1.013 |
0.012 |
0.012 |
2 × |
0.960 |
0.020 |
0.021 | The mean
recoveries were then pooled =
Average mean recovery = 0.996 |
Standard Deviation = 0.019 |
Coefficient of variation =
0.019 | Addendum II*
A recovery study of the loss of TBTF
on FWSB-PVC filters due to volatility was done. A 40 µL spike of 1039 ppm
Sn as TBTF was placed on six filters and attached to six personal sampling
pumps (calibrated at 2 liters per minute). 200 liters of air (100 minutes)
were drawn through each. The filters were then placed into 50 mL
volumetric flasks, diluted to volume with 1-propanol, and run on the
graphite furnace as described in section 6.7. The recoveries are as
follows:
Sample |
Found |
Theor. |
Found/Theor. |
|
2× - 1A |
41.32 |
41.56 |
0.994 |
2× - 2A |
42.47 |
41.56 |
1.022 |
2× - 3A |
41.60 |
41.56 |
1.001 |
2× - 4A |
43.66 |
41.56 |
1.051 |
2× - 5A |
44.59 |
41.56 |
1.073 |
2× - 6A |
42.47 |
41.56 |
1.022 |
|