1. Introduction
1.1 Scope
This method describes
the collection and analysis of airborne methyl tin mercaptide (MTM). 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
Appearance - clear yellow to light amber
liquid Specific gravity - 1.02 (at approx. 250 °C) Refractive
index - 1.5085 (at approx. 250 °C) % Sn - 11% Decomposes to form
tin oxides and sulfur dioxide Boiling point - not distillable 2.
Range and Detection Limit
2.1 The lower analytical limit for MTM
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 MTM in butyl cellusolve.
3. Precision and Accuracy
3.1 Precision
3.2
Coefficient of Variation
3.3 Recovery |
S = .020
CV = 0.023
Average mean
recovery = .874 | The
above are based on recovery data for eighteen impingers, spiked with MTM
in butyl cellusolve at .5×, 1×, and 2× the PEL based on a 150 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 butyl cellusolve. 5. Sampling Procedure
The sample is collected in an impinger
containing 15 mL butyl cellusolve at a flow rate of 1 L/min.
The
recommended air volume is 150 L.
The impingers are capped, 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 Impingers 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 Butyl cellusolve
(2-Butoxyethanol)
6.2.2 Stock methyl tin
mercaptide
6.2.3 Stock tin (1000 ppm), Scientific
Products, Fisher or equivalent 6.3 Safety precautions
6.3.1 Use caution when handling butyl
cellusolve and organotins. Methyl tin mercaptide is a toxic compound.
Always wear rubber gloves and work in 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 deionized water, invert, and allow to dry.
6.5 Standard preparation
6.5.1 The procedure is to analyze the
tin in methyl tin mercaptide. Prepare a 10 ppm Sn stock solution from
two serial 10-fold dilutions of 1000 ppm stock.
6.5.2
Working standards are prepared from the 10 ppm Sn stock as
follows:
Prepared std. |
Std. stock used |
Aliquot |
Dil. vol. |
2.0 ppm |
|
10 ppm |
|
10 mL |
|
50 mL |
1.0 ppm |
|
10 ppm |
|
5 mL |
|
50 mL |
0.2 ppm |
|
1 ppm |
|
10 mL |
|
50 mL |
0.1 ppm |
|
1 ppm |
|
5 mL |
|
50 mL |
0.04 ppm |
|
1 ppm |
|
2 mL |
|
50
mL | 6.6 Sample
preparation
Measure the volume of the impinger and record a
sample volume. Transfer into sampling cup and analyze directly on
graphite furnace. If off-scale, make all dilutions in butyl
cellusolve.
6.7 Analysis
The analysis is done by graphite
furnace/AA. The instrumental parameters for determining Sn in butyl
cellusolve are as follows:
Atomic absorption
unit:
Sn wavelength |
224.6 nm |
integ. time |
10 sec. |
slit width |
.7 low |
signal |
Pk. Ut. |
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 2.0
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 MTM in 15 mL impinger of butyl cellusolve was done. 0.240 g MTM
was weighed into a 1000 ml volumetric, diluted to volume with butyl
cellusolve, and mixed. Assuming MTM is 11% Sn, this is 26.4 ppm Sn as MTM.
From this a 13.2 ppm and a 6.6 ppm standard are also prepared. Six
impingers were spiked at each level = .5×, 1×, and 2× the OSHA PEL based
on a 150 liter air volume and 0.1 mg/m3 OSHA PEL. The spikes were made as
follows:
Sample |
Stock
std. |
ml.
aliquot |
final
vol. |
theor. Sn |
0.5×-l |
6.6 ppm |
1.0 mL |
15 mL |
0.44 ppm |
0.5×-2 |
6.6 ppm |
1.0 mL |
15 mL |
0.44 ppm |
0.5×-3 |
6.6 ppm |
1.0 mL |
15 mL |
0.44 ppm |
0.5×-4 |
6.6 ppm |
1.0 mL |
15 mL |
0.44 ppm |
0.5×-5 |
6.6 ppm |
1.0 mL |
15 mL |
0.44 ppm |
0.5×-6 |
6.6 ppm |
1.0 mL |
15 mL |
0.44 ppm |
|
|
|
|
|
1.0×-1 |
13.2 ppm |
1.0 mL |
15 mL |
0.88 ppm |
1.0×-2 |
13.2 ppm |
1.0 mL |
15 mL |
0.88 ppm |
1.0×-3 |
13.2 ppm |
1.0 mL |
15 mL |
0.88 ppm |
1.0×-4 |
13.2 ppm |
1.0 mL |
15 mL |
0.88 ppm |
1.0×-5 |
13.2 ppm |
1.0 mL |
15 mL |
0.88 ppm |
1.0×-6 |
13.2 ppm |
1.0 mL |
15 mL |
0.88 ppm |
|
|
|
|
|
2.0×-1 |
26.4 ppm |
1.0 mL |
15 mL |
1.76 ppm |
2.0×-2 |
26.4 ppm |
1.0 mL |
15 mL |
1.76 ppm |
2.0×-3 |
26.4 ppm |
1.0 mL |
15 mL |
1.76 ppm |
2.0×-4 |
26.4 ppm |
1.0 mL |
15 mL |
1.76 ppm |
2.0×-5 |
26.4 ppm |
1.0 mL |
15 mL |
1.76 ppm |
2.0×-6 |
26.4 ppm |
1.0 mL |
15 mL |
1.76
ppm | The mean standard deviation and coefficient of variation for
the recovery at each level using the OSHA "Precision and Accuracy Data"
program:
Level .5× (OSHA PEL)
µg taken |
µg found |
AMR |
|
0.44 |
0.38 |
0.864 |
N = 6 |
0.44 |
0.40 |
0.909 |
Mean = 0.875 |
0.44 |
0.38 |
0.864 |
Std Dev = 0.019 |
0.44 |
0.38 |
0.864 |
CV1 = 0.022 |
0.44 |
0.39 |
0.886 |
|
0.44 |
0.38 |
0.864 |
| Level 1× (OSHA PEL)
µg taken |
µg found |
AMR |
|
0.88 |
0.75 |
0.852 |
N = 6 |
0.88 |
0.75 |
0.852 |
Mean = 0.845 |
0.88 |
0.75 |
0.852 |
Std Dev = 0.020 |
0.88 |
0.74 |
0.841 |
CV1 = 0.024 |
0.88 |
0.71 |
0.807 |
|
0.88 |
0.76 |
0.864 |
| Level 2× (OSHA PEL)
µg taken |
µg found |
AMR |
|
1.76 |
1.57 |
0.892 |
N = 6 |
1.76 |
1.54 |
0.875 |
Mean = 0.901 |
1.76 |
1.56 |
0.886 |
Std Dev = 0.020 |
1.76 |
1.60 |
0.909 |
CV1 = 0.024 |
1.76 |
1.59 |
0.903 |
|
1.76 |
1.65 |
0.938 |
|
|