Code of Federal Regulations (Last Updated: November 8, 2024) |
Title 40 - Protection of Environment |
Chapter I - Environmental Protection Agency |
SubChapter C - Air Programs |
Part 61 - National Emission Standards for Hazardous Air Pollutants |
Appendix C to Part 61 - Quality Assurance Procedures
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Appendix C to Part 61 - Quality Assurance Procedures
Procedure 1 - Determination of Adequate Chromatographic Peak Resolution
In this method of dealing with resolution, the extent to which one chromatographic peak overlaps another is determined.
For convenience, consider the range of the elution curve of each compound as running from −2σ to + 2σ. This range is used in other resolution criteria, and it contains 95.45 percent of the area of a normal curve. If two peaks are separated by a known distance, b, one can determine the fraction of the area of one curve that lies within the range of the other. The extent to which the elution curve of a contaminant compound overlaps the curve of a compound that is under analysis is found by integrating the contaminant curve over the limits b−2σs to b + 2σs, where σs is the standard deviation of the sample curve.
This calculation can be simplified in several ways. Overlap can be determined for curves of unit area; then actual areas can be introduced. Desired integration can be resolved into two integrals of the normal distribution function for which there are convenient calculation programs and tables. An example would be Program 15 in Texas Instruments Program Manual ST1, 1975, Texas Instruments, Inc., Dallas, Texas 75222.
In judging the suitability of alternate GC columns or the effects of altering chromatographic conditions, one can employ the area overlap as the resolution parameter with a specific maximum permissible value.
The use of Gaussian functions to describe chromatographic elution curves is widespread. However, some elution curves are highly asymmetric. In cases where the sample peak is followed by a contaminant that has a leading edge that rises sharply but the curve then tails off, it may be possible to define an effective width for tc as “twice the distance from the leading edge to a perpendicular line through the maxim of the contaminant curve, measured along a perpendicular bisection of that line.”
Procedure 2 - Procedure for Field Auditing GC Analysis
Responsibilities of audit supervisor and analyst at the source sampling site include the following:
A. The audit supervisor verifies that audit cylinders are stored in a safe location both before and after the audit to prevent vandalism.
B. At the beginning and conclusion of the audit, the analyst records each cylinder number and pressure. An audit cylinder is never analyzed when the pressure drops below 200 psi.
C. During the audit, the analyst performs a minimum of two consecutive analyses of each audit cylinder gas. The audit must be conducted to coincide with the analysis of source test samples, normally immediately after GC calibration and prior to sample analyses.
D. At the end of audit analyses, the audit supervisor requests the calculated concentrations from the analyst and compares the results with the actual audit concentrations. If each measured concentration agrees with the respective actual concentration within ±10 percent, he directs the analyst to begin analyzing source samples. Audit supervisor judgment and/or supervisory policy determine action when agreement is not within ±10 percent. When a consistent bias in excess of 10 percent is found, it may be possible to proceed with the sample analysis, with a corrective factor to be applied to the results at a later time. However, every attempt should be made to locate the cause of the discrepancy, as it may be misleading. The audit supervisor records each cylinder number, cylinder pressure (at the end of the audit), and all calculated concentrations. The individual being audited must not under any circumstance be told actual audit concentrations until calculated concentrations have been submitted to the audit supervisor.
Field Audit Report
Part A - To be filled out by organization supplying audit cylinders.
1. Organization supplying audit sample(s) and shipping address
2. Audit supervisor, organization, and phone number
3. Shipping instructions: Name, Address, Attention
4. Guaranteed arrival date for cylinders
5. Planned shipping date for cylinders
6. Details on audit cylinders from last analysis
Low conc. High conc. a. Date of last analysis b. Cylinder number c. Cylinder pressure, psi d. Audit gas(es)/balance gas e. Audit gas(es), ppm f. Cylinder construction Part B - To be filled out by audit supervisor.
1. Process sampled
2. Audit location
3. Name of individual audit
4. Audit date
5. Audit results:
Low conc. cylinder High conc. cylinder a. Cylinder number b. Cylinder pressure before audit, psi c. Cylinder pressure after audit, psi d. Measured concentration, ppm Injection #1* Injection #2* Average e. Actual audit concentration, ppm (Part A, 6e) f. Audit accuracy:1 Low Conc. Cylinder High Conc. Cylinder Percent1 accuracy= Measured Conc. − Actual Conc. ________________ × 100 Actual Conc. g. Problems detected (if any) [47 FR 39178, Sept. 7, 1982]