1. Introduction
1.1 Scope
This method describes the collection and
analysis of airborne tributyltin benzoate (TBTB). It is applicable for
time-weighted average exposure evaluations. The analysis is based on the
technique of graphite furnace atomic absorption.
1.3 Physical
and Chemical Properties
(C4H9)3
Sn(C7H502) |
mol. wt. |
- |
411.20 |
clear, yellow liquid |
% Sn |
- |
28.86 |
| 2. Range and Detection Limit
2.1 The lower analytical limit for TBTB is 0.1
µg/ml.
2.2 This is based on a detection limit of 0.02 µg/ml for
graphite furnace analysis of Sn as TBTB in
1-propanol. 3. Precision and
Accuracy
3.1 Precision |
S = 0.028 |
3.2 Coefficient of
Variation |
CV = 0.030 |
3.3 Recovery |
Average mean recovery = 1.01
| The above are based on
recovery data for eighteen FWSB-PVC filters, spiked with TBTB 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 soluble
in 1-propanol.
5. Sampling Procedure
The sample is collected
on a FWSB-PVC filter (0.8 µm, 37 mm 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 benzoate 6.3 Safety
precautions
6.3.1 Use caution when handling
1-propanol and organotins. Tributyltin benzoate 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 benzoate. Prepare the standards by diluting stock
TBTB in 1-propanol assuming a theoretical tin content of 28.86%.
6.5.2 Prepare a stock solution by weighing 0.3465 g TBTB into
a 100 ml volumetric flask, diluting to volume with 1-propanol and
mixing well. This is equivalent to 1,000 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, 20mm/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 TBTB from FWSB-PVC
filters by desorption in 1-propanol was done.
0.35659 TBTB was
weighed into a 100 mL volumetric, diluted to volume with 1-propanol, and
mixed. Assuming the TBTB is 28.86% Sn, this is 1,000 ppm Sn as TBTB.
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 (µg) |
Sn (µg) |
PEL (multiple) |
|
1,000 |
10 |
10 |
1/2 × |
1,000 |
20 |
20 |
1 × |
1,000 |
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 × |
1.092 |
0.031 |
0.032 |
1 × |
1.039 |
0.023 |
0.022 |
2 × |
1.095 |
0.030 |
0.035 | The mean recoveries were then pooled
=
Average mean recovery |
= |
1.01 |
Standard Deviation |
= |
0.028 |
Coefficient of variation |
= |
0.030 | Addendum II*
A recovery study of the loss of TBTB on
FWSB-PVC filters due to volatility was done. A 20 µL spike of 1,000 ppm
Sn as TBTB was placed on six filters and attached to six personnel
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.* |
Test-1 |
19.99 |
20.00 |
0.9995 |
Test-2 |
19.99 |
20.00 |
0.9995 |
Test-3 |
19.99 |
20.00 |
0.9995 |
Test-4 |
20.64 |
20.00 |
1.0320 |
Test-5 |
20.64 |
20.00 |
1.0320 |
Test-6 |
21.29 |
20.00 |
1.0645 |
|