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Selenium
Related Information: Chemical Sampling - Selenium
| Method no.: |
ID-133SG |
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| Control no.: |
T-ID133SG-PV-01-0205-M |
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| Method Classification: |
Partially Validated |
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| Sampling Procedure: |
Collection Medium - 0.8 µm AA cellulose filter. |
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| Recommended air volume: |
100 liters (minimum) |
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| Sampling rate: |
2.0 liters per minute |
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| Summary of Analytical Procedure: |
The sample is collected on a 0.8-µm AA cellulose filter. The
filters are ashed with concentrated HNO3, 1000 ppm nickel, and HCl to destroy the organic matrix and
dissolve the metal. The samples are diluted using deionized water and the samples and standards are injected
into the graphite furnace to determine the sample concentration. |
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| Detection Limit: |
0.02 µg/mL |
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1. Introduction:
1.1 Scope
This method describes the collection and analysis of airborne selenium. It is applicable for both ceiling and
time-weighted average (TWA) exposure evaluations. The analysis is based on the utilization of a graphite
furnace.
1.2 Previous analysis of selenium was by an atomic absorption spectro-photometer (AAS). This method did not take
into account the possibility of interfering complexing species such as Ni, Cu, Hg, etc. in order to dissociate
these complexing species, it was necessary to develop a method in which a higher temperature, such as with the
graphite furnace, was used. This proved to be a very effective and accurate method.
1.3 Uses
Selenium exhibits both photovoltaic action, where light is converted directly into electricity, and photo-conductive
action, where the electrical resistance decreases with increased illumination. These properties make
selenium useful in the production of photo cells and exposure meters for photographic use, as well as
solar cells. Selenium is also able to convert ac electricity to dc and is extensively, used in rectifiers. Below its
melting point, selenium is a p-type semiconductor, and is finding many uses in electronic and solid state
applications. It is used in zerography for reproducing and copying documents, letters, etc. It is used in the
manufacture of pigments, in insecticides, in rubber compounding, to remove the green (iron) tint of glass, to
produce pink, ruby, and black glass glaze, to improve the machinability of copper alloys and stainless steel,
to improve the grain, structure, and ductility of cast steel, to increase the depth of chill in cast iron, as a
flameproofing agent for textiles and wire-cable coverings, and in chemical and ceramic manufacture. Exposures to
selenium may result during the smelting and refining of ores containing selenium, in the refining of copper,
silver, and gold to remove the selenium, or from the use of selenium compounds.
1.4 Physical and Chemical Properties
Selenium is a non-metallic element of the sulfur group. Selenium exists in several allotropic forms. Three are
generally recognized, but as many as six have been claimed. Selenium can be found as either red in powder form,
or black in vitreous form. Crystalline monoclinic selenium is a deep red; crystalline hexagonal
selenium, the most stable variety, is a metallic gray. Being a member of the sulfur family, it resembles sulfur
both in its various forms and in its compounds.
The physical and chemical properties of selenium are listed in Table 1.4.
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Table 1.4
Physical and Chemical Properties of Selenium
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|
Form I |
Form II |
Form III |
|
| Molecular weight |
78.96 g/mole |
78.96 |
78.96 |
| Molecular formula |
Se |
Se |
Se |
| color/ |
bluish-gray |
red |
red amorphous |
| crystalline form |
met hexagonal |
monoclinic prism |
black vitreous |
| specific gravity |
4.81 |
4.50 |
red 4.26 |
| melting point (°C) |
217 |
170-180 |
60-80 |
| boiling point (°C) |
634.9 |
634.8 |
634.8 |
| Solubility (g/100 mL) |
|
|
| cold water |
insoluble |
insoluble |
insoluble |
| hot water |
insoluble |
insoluble |
insoluble |
| H2SO4 |
soluble |
soluble |
------ |
| CHCl3 |
soluble |
------- |
------ |
| alcohol |
insoluble |
------- |
------ |
| CS2 |
very slightly soluble |
------- |
soluble |
| KMO3 |
------- |
soluble |
------ |
| Benzene |
------- |
------- |
soluble |
The red amorphous powder turns black upon standing and vitreous upon heating.
2. Range and Detection Limit
A lower analytical limit, 0.02 µg/mL, was selected for routine analysis.
3. Precision and Accuracy
Not determined.
4. Interferences
None known.
5. Sampling Procedure
5.1 The sample is collected on a 0.8-µm AA cellulose membrane filter using a flow rate between 1.5 and 2.0 liters
per minute. Suggested minimum air volume is 100 liters. A sample blank should also be submitted. (If
considerable loose dust is present in the cassette, a clean filter should be placed over the dust before
sealing.)
5.2 The sample cassettes are plugged, sealed with OSHA tape, labeled, and sent to the laboratory for analysis.
5.3 No storage problems are normally anticipated. Vibration or jolting of samples should be kept to a minimum to
avoid dislodging of dust from the filter.
6. Analytical Procedure
6.1 Apparatus
Atomic absorption spectrophotometer equipped with graphite furnace, argon purge system, and deuterium arc background corrector.
Chart recorder.
Glassware.
AA filters (0.8-µm, cellulose membrane filters 37-mm diam)
2-or 3-piece filter cassettes Personal sampling pump (capable of sampling between 1.0 and 2.0 liters per
minute)
6.2 Reagents
HCl, reagent grade
HNO3, reagent grade
A certified aqueous standard such as "SPEX" 1,000 ppm standard. 1,000 ppm Ni solution, prepared as
follows
Dissolve 5.0 g Ni(NO3)2.6H2O in 100 mL H2O, add 5 mL KNO3,
dilute to 1 1.
Diluting solution: Twenty AA filters are ashed with 100 mL concentrate MNO3 and 100 mL of 1,000 ppm
Ni solution to a volume of 20 - 40 mL, diluted to 500 mL with deionized water and 2 mL HCl.
6.3 Standards Preparation
Standards are prepared to match the matrix of the samples (filter content acid and nickel concentration) as closely
as possible according to the dilution scheme of Table 6.3.1.
The 0.2, 1, 2, 5, 10 and 20 ppm "stock solutions" are made by serial dilution of the 1,000 ppm As
stock (with deionized water) as follows in Table 6.3.1.
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Table 6.3.1
Stock Solutions
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| Stock Solution |
Standard Solution Used |
mL Used |
Final Volume |
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| 10 ppm |
1000 ppm |
10 mL |
1000 mL |
| 1.0 ppm |
10 ppm |
100 mL |
1000 mL |
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The diluted stock solutions should be prepared just before using them to prepare the working
standards as outlined in Table 6.3.2.
When preparing the working standards from the stock solutions, all dilutions are made with the diluting
solution.
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Table 6.3.2
Working Standard Solutions
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| STD (PPM) |
mL Stock Used |
Stock Concentration (ppm) |
Final Volume |
|
| 0.02 |
2 |
1 |
100 mL |
| 0.05 |
5 |
1 |
100 mL |
| 0.1 |
10 |
1 |
100 mL |
| 0.2 |
20 |
1 |
100 mL |
| 0.5 |
5 |
1 |
100 mL |
| 1.0 |
10 |
10 |
100 mL |
| 2.0 |
20 |
10 |
100 mL |
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6.4. Sample Preparation
Note: All glassware must be rinsed with 1:1 HN03 and deionized water prior to use. Phillips beakers
used for the digestion are refluxed with 1:1 nitric acid and rinsed with deionized water before use.
Place filter in 125 mL Phillips beaker, add 5 mL of 1000 ppm Ni solution and 5 µL concentrated HNO3
and ash to approximately 1-2 mL volume. After sample has cooled, add 2 drops HCl and swirl contents (no additional
heating is done).
Quantitatively transfer sample to 25 mL volume flask, dilute to volume with deionized water, and mix. Additional
dilutions for samples over 2 ppm Se are made with the diluting solution.
6.5 Sample Analysis
The analysis for selenium is performed using a graphite furnace. Instrumental parameters are as follows:
Selenium Conditions
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Dry |
= 90T, 40H, 150F |
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Char |
= 900T, 502, 30H, 100F |
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Atomize |
= 2650T, 0R, 8H, 15F |
| Wavelength: |
196.0 nm |
Chart |
= Range 10 |
| Slit 4 |
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EDL Power |
= 6 1/2 watts |
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(STDS prepared same as As) |
Injection volume = 10 µL The 2.0 ppm standard should give a near full scale deflection using these conditions. The
entire series of standards should be run at the beginning and the end of the analysis. A standard should be run
after every fourth or fifth sample in the sample range.
6.6 Calculations
A linear regression of standard ppm vs standard peak height is performed using the 0SHA Automatic AA program. The
sample results are calculated based on sample peak heights; a function of sample absorption.
mg
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= |
(ppm Se*)(sample volume, mL)(dilution factor)
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| m3 |
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air volume, liters |
*blank corrected
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