This method is a sorbent tube/thermal desorption/gas chromatographic-based monitoring method for volatile organic compounds (VOCs) in ambient air at 0.5 to 25 parts per billion (ppbv) concentration levels. Performance criteria are provided as part of the method in Section 14.
EPA has previously published Compendium Method TO-1 describing the use of the porous polymer Tenax® GC for sampling nonpolar VOCs and Compendium Method TO-2 describing the use of carbon molecular sieve for highly volatile, nonpolar organics. Since these methods were developed, a new generation of thermal desorption systems as well as new types of solid adsorbents have become available commercially. These sorbents are used singly or in multisorbent packings. Tubes with more than one sorbent, packed in order of increasing sorbent strength are used to facilitate quantitative retention and desorption of VOCs over a wide volatility range. The higher molecular weight compounds are retained on the front, least retentive sorbent; the more volatile compounds are retained farther into the packing on a stronger adsorbent. The higher molecular weight compounds never encounter the stronger adsorbents, thereby improving the efficiency of the thermal desorption process.
The analytical methodology for this method is identical to TO-15.
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Hold Times, Preservatives, Preps, Collection, Analytical & Documentation | |
---|---|
Holding Time: | The method specifies 30 days from collection to analysis. |
Preservatives: | Refrigerate at 4°C. |
Required Preps: | Anasorb 747 tube is commonly used but there are various types of sorbent tubes available for compounds with different volatilities. |
Collection Method: | TO-17 |
Analytical Methodology: | GC/MS (other detectors are acceptable if method criteria are met) |
Documentation: | TO-17 |
Analyte | Formula | CAS Number | Detection Limit | |
---|---|---|---|---|
Ethylbenzene | C8H10 |
100-41-4 |
1 |
ng |
Styrene | C8H8 |
100-42-5 |
1 |
ng |
Benzyl chloride | C7H7Cl |
100-44-7 |
1 |
ng |
p-Xylene | C8H10 |
106-42-3 |
1 |
ng |
1,4-Dichlorobenzene | C6H4Cl2 |
106-46-7 |
1 |
ng |
1,2-Dibromoethane | C2H4Br2 |
106-93-4 |
1 |
ng |
Allyl chloride | C3H5Cl |
107-05-1 |
1 |
ng |
1,2-Dichloroethane | C2H4Cl2 |
107-06-2 |
1 |
ng |
m-Xylene | C8H10 |
108-38-3 |
1 |
ng |
1,3,5-Trimethylbenzene | C9H12 |
108-67-8 |
1 |
ng |
Toluene | C7H8 |
108-88-3 |
1 |
ng |
Chlorobenzene | C6H5Cl |
108-90-7 |
1 |
ng |
1,2,4-Trichlorobenzene | C6H3Cl3 |
120-82-1 |
1 |
ng |
Tetrachloroethene | C2Cl4 |
127-18-4 |
1 |
ng |
cis-1,2-Dichloroethene | C2H2Cl2 |
156-59-2 |
1 |
ng |
1,3-Dichlorobenzene | C6H4Cl2 |
541-73-1 |
1 |
ng |
1,3-Dichloropropene | C3H4Cl2 |
542-75-6 |
1 |
ng |
Carbon tetrachloride | CCl4 |
56-23-5 |
1 |
ng |
4-ethyltoluene | C9H12 |
622-96-8 |
1 |
ng |
Chloroform | CHCl3 |
67-66-3 |
1 |
ng |
Benzene | C6H6 |
71-43-2 |
1 |
ng |
1,1,1-Trichloroethane | C2H3Cl3 |
71-55-6 |
1 |
ng |
Bromomethane | CH3Br |
74-83-9 |
1 |
ng |
Chloromethane (Methyl chloride) | CH3Cl |
74-87-3 |
1 |
ng |
Chloroethane | C2H5Cl |
75-00-3 |
1 |
ng |
Vinyl chloride | C2H3Cl |
75-01-4 |
1 |
ng |
Methylene chloride | CH2Cl2 |
75-09-2 |
1 |
ng |
1,1-Dichloroethane | C2H4Cl2 |
75-34-3 |
1 |
ng |
1,1-Dichloroethene | C2H2Cl2 |
75-35-4 |
1 |
ng |
Trichlorofluoromethane | CCl3F |
75-69-4 |
1 |
ng |
Dichlorodifluoromethane | CCl2F2 |
75-71-8 |
1 |
ng |
Trichlorotrifluoroethane | C2Cl3F3 |
76-13-1 |
1 |
ng |
1,2-Dichlorotetrafluoroethane | C2Cl2F4 |
76-14-2 |
1 |
ng |
1,2-Dichloropropane | C3H6Cl2 |
78-87-5 |
1 |
ng |
1,1,2-Trichloroethane | C2H3Cl3 |
79-00-5 |
1 |
ng |
Trichloroethene | C2HCl3 |
79-01-6 |
1 |
ng |
1,1,2,2-Tetrachloroethane | C2H2Cl4 |
79-34-5 |
1 |
ng |
Hexachlorobutadiene | C4Cl6 |
87-68-3 |
1 |
ng |
o-Xylene | C8H10 |
95-47-6 |
1 |
ng |
1,2-Dichlorobenzene | C6H4Cl2 |
95-50-1 |
1 |
ng |
1,2,4-Trimethylbenzene | C9H12 |
95-63-6 |
1 |
ng |
* The analytes and detection limits listed for each method represent the typical detection limits and analytes reported for that particular method. Keep in mind that analyte lists may vary from laboratory to laboratory. Detection limits may also vary from lab to lab and are dependent upon the sample size, matrix, and any interferences that may be present in the sample.