NOTE: This method does not include all of the specifications (e.g., equipment and supplies) and procedures (e.g., sampling and analytical) essential to its performance. Some material is incorporated by reference from other methods in this part. Therefore, to obtain reliable results, persons using this method should have a thorough knowledge of at least the following additional test methods: Method 1, Method 2, Method 3, Method 5, Method 6, and Method 19.
This method is applicable for the determination of sulfur dioxide (SO2) emissions from fossil fuel combustion sources in terms of concentration (mg/dscm or lb/dscf) and in terms of emission rate (ng/J or lb/106 Btu) and for the determination of carbon dioxide (CO2) concentration (percent). Moisture content (percent), if desired, may also be determined by this method.
Adherence to the requirements of this method will enhance the quality of the data obtained from air pollutant sampling methods.
2.1 A gas sample is extracted from a sampling point in the stack. The SO2 and the sulfur trioxide, including those fractions in any sulfur acid mist, are separated. The SO2 fraction is measured by the barium-thorin titration method. Moisture and CO2 fractions are collected in the same sampling train, and are determined gravimetrically.
Same as Method 6, Section 4.0.
This method may involve hazardous materials, operations, and equipment. This test method may not address all of the safety problems associated with its use. It is the responsibility of the user to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to performing this test method.
Same as Method 6, Section 5.2.
Same as Method 6, Section 6.1, with the exception of the following:
Two 30-ml midget impingers with a 1-mm restricted tip and two 30-ml midget bubblers with unrestricted tips. Other types of impingers and bubblers (e.g., Mae West for SO2 collection and rigid cylinders containing Drierite for moisture absorbers), may be used with proper attention to reagent volumes and levels, subject to the approval of the Administrator.
A sealable rigid cylinder or bottle with an inside diameter between 30 and 90 mm , a length between 125 and 250 mm, and appropriate connections at both ends. The filter may be a separate heated unit or may be within the heated portion of the Probe. If the filter is within the sampling Probe, the filter should not be within 15 cm of the Probe inlet or any unheated section of the Probe, such as the connection to the first bubbler. The Probe and filter should be heated to at least 20 C (68 F) above the source temperature, but not greater than 120 C (248 F). The filter temperature (i.e., the sample gas temperature) should be monitored to assure the desired temperature is maintained. A heated Teflon connector may be used to connect the filter holder or Probe to the first impinger.
NOTE: For applications downstream of wet scrubbers, a heated out-of-stack filter (either borosilicate glass wool or glass fiber mat) is necessary.
Same as Method 6, Section 6.2.
Same as Method 6, Section 6.3, with the addition of a balance to measure within 0.05 g.
NOTE: Unless otherwise indicated, all reagents must conform to the specifications established by the Committee on Analytical Reagents of the American Chemical Society. Where such specifications are not available, use the best available grade.
Same as Method 6, Section 7.1, with the addition of the following:
Anhydrous calcium sulfate (CaSO4) desiccant, 8 mesh, indicating type is recommended.
NOTE: Do not use silica gel or similar desiccant in this application.
Ascarite II. Sodium hydroxide-coated silica, 8- to 20-mesh.
8.1.1 Measure 15 ml of 80 percent isopropanol into the first midget bubbler and 15 ml of 3 percent hydrogen peroxide into each of the two midget impingers (the second and third vessels in the train) as described in Method 6, Section 8.1. Insert the glass wool into the top of the isopropanol bubbler as shown in Figure 6A-1. Place about 25 g of Drierite into the second midget bubbler (the fourth vessel in the train). Clean the outside of the bubblers and impingers and allow the vessels to reach room temperature. Weigh the four vessels simultaneously to the nearest 0.1 g, and record this initial weight (mwi).
8.1.2 With one end of the CO2 absorber sealed, place glass wool into the cylinder to a depth of about 1 cm (0.5 in.). Place about 150 g of CO2 absorbing material in the cylinder on top of the glass wool, and fill the remaining space in the cylinder with glass wool. Assemble the cylinder as shown in Figure 6A-2. With the cylinder in a horizontal position, rotate it around the horizontal axis. The CO2 absorbing material should remain in position during the rotation, and no open spaces or channels should be formed. If necessary, pack more glass wool into the cylinder to make the CO2 absorbing material stable. Clean the outside of the cylinder of loose dirt and moisture and allow the cylinder to reach room temperature. Weigh the cylinder to the nearest 0.1 g, and record this initial weight (mai).
8.1.3 Assemble the train as shown in Figure 6A-1. Adjust the Probe heater to a temperature sufficient to prevent condensation (see NOTE in Section 6.1). Place crushed ice and water around the impingers and bubblers. Mount the CO2 absorber outside the water bath in a vertical flow position with the sample gas inlet at the bottom. Flexible tubing (e.g., Tygon) may be used to connect the last SO2 absorbing impinger to the moisture absorber and to connect the moisture absorber to the CO2 absorber. A second, smaller CO2 absorber containing Ascarite II may be added in-line downstream of the primary CO2 absorber as a breakthrough indicator. Ascarite II turns white when CO2 is absorbed.
Disconnect the isopropanol bubbler, the SO2 impingers, and the moisture absorber from the sample train. Allow about 10 minutes for them to reach room temperature, clean the outside of loose dirt and moisture, and weigh them simultaneously in the same manner as in Section 8.1. Record this final weight (mwf).
Discard the contents of the isopropanol bubbler and pour the contents of the midget impingers into a leak-free polyethylene bottle for shipping. Rinse the two midget impingers and connecting tubes with water, and add the washing to the same storage container.
Allow the CO2 absorber to warm to room temperature (about 10 minutes), clean the outside of loose dirt and moisture, and weigh to the nearest 0.1 g in the same manner as in Section 8.1. Record this final weight (maf). Discard used Ascarite II material.
Same as Method 6, Section 9.0.
Same as Method 6, Section 10.0.
The sample analysis procedure for SO2 is the same as that specified in Method 6, Section 11.0.
Analysis of QA audit samples is required only when this method is used for compliance determinations. Obtain an audit sample set as directed in Section 7.3.6 of Method 6. Analyze the audit samples, and report the results as directed in Section 11.3 of Method 6. Acceptance criteria for the audit results are the same as those in Method 6.
Same as Method 6, Section 12.0, with the addition of the following:
|Cw||=||Concentration of moisture, percent.|
|CCO2||=||Concentration of CO2, dry basis, percent.|
|ESO2||=||Emission rate of SO2, ng/J (lb/106 Btu).|
|FC||=||Carbon F-factor from Method 19 for the fuel burned, dscm/J (dscf/106 Btu).|
|mwi||=||Initial weight of impingers, bubblers, and moisture absorber, g.|
|mwf||=||Final weight of impingers, bubblers, and moisture absorber, g.|
|mai||=||Initial weight of CO2 absorber, g.|
|maf||=||Final weight of CO2 absorber, g.|
|mSO2||=||Mass of SO2 collected, mg.|
|VCO2(std)||=||Equivalent volume of CO2 collected at standard conditions, dscm (dscf).|
|Vw(std)||=||Equivalent volume of moisture collected at standard conditions, scm (scf).|
|K3||=||Equivalent volume of gaseous CO2 at standard conditions, 5.467 x 10-4 dscm/g (1.930 x 10-2dscf/g).|
|K4||=||Equivalent volume of water vapor at standard conditions, 1.336 x 10-3 scm/g (4.717 x 10-2 scf/g).|
|K2||=||32.03 mg SO2/meq. SO2 (7.061 x 10-5 lb SO2/meq. SO2)|
The minimum detectable limit and the upper limit for the measurement of SO2 are the same as for Method 6. For a 20-liter sample, this method has a precision of ±0.5 percent CO2 for concentrations between 2.5 and 25 percent CO2 and ± 1.0 percent moisture for moisture concentrations greater than 5 percent.
If the only emission measurement desired is in terms of emission rate of SO2 (ng/J or lb/106 Btu), an abbreviated procedure may be used. The differences between the above procedure and the abbreviated procedure are described below.
Analysis of the peroxide solution and QA audit samples is the same as that described in Sections 11.1 and 11.2, respectively.
16.6.1 SO2 Collected.
|K2||=||32.03 mg SO2/meq. SO2|
|=||7.061 x 10-5 lb SO2/meq. SO2|
16.6.2 Sulfur Dioxide Emission Rate.
|K5||=||1.829 x109 mg/dscm|
Same as Method 6, Section 17.0, References 1 through 8, with the addition of the following:
1. Stanley, Jon and P.R. Westlin. An Alternate Method for Stack Gas Moisture Determination. Source Evaluation Society Newsletter. 3(4). November 1978.
2. Whittle, Richard N. and P.R. Westlin. Air Pollution Test Report: Development and Evaluation of an Intermittent Integrated SO2/CO2 Emission Sampling Procedure. Environmental Protection Agency, Emission Standard and Engineering Division, Emission Measurement Branch. Research Triangle Park, NC. December 1979. 14 pp.
Figure 6A-1. Sampling train.