EPA Method 18
ALS - Columbia offers EPA Method 18 testing at these laboratories:
|Rochester, New York Laboratory|
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View Actual EPA Method 18 (PDF File)
EPA Method 18:
MEASUREMENT OF GASEOUS ORGANIC COMPOUND EMISSIONS BY GAS CHROMATOGRAPHY
The major organic components of a gas mixture are separated by gas chromatography (GC) and individually quantified by flame ionization, photoionization, electron capture, or other appropriate detection principles. The retention times of each separated component are compared with those of known compounds under identical conditions. Therefore, the analyst confirms the identity and approximate concentrations of the organic emission components beforehand. With this information, the analyst then prepares or purchases commercially available standard mixtures to calibrate the GC under conditions identical to those of the samples. The analyst also determines the need for sample dilution to avoid detector saturation, gas stream filtration to eliminate particulate matter, and prevention of moisture condensation.
This method is designed to measure gaseous organics emitted from an industrial source. While designed for ppm level sources, some detectors are quite capable of detecting compounds at ambient levels, e.g., ECD, ELCD, and helium ionization detectors. Some other types of detectors are evolving such that the sensitivity and applicability may well be in the ppb range in only a few years.
The official copy of this method is available at 40 Code of Federal Regulations (CFR) 60, Appendix A. The CFR can be accessed on-line at http://www.gpoaccess.gov/cfr/index.html
(A) Co-elution. Resolution interferences that may occur can be eliminated by appropriate GC column and detector choice or by shifting the retention times through changes in the column flow rate and the use of temperature programming.(B) Contamination. The analytical system is demonstrated to be essentially free from contaminants by periodically analyzing blanks that consist of hydrocarbon-free air or nitrogen.(C) Cross-Contamination. Sample cross-contamination that occurs when high-level and low-level samples or standards are analyzed alternately is best dealt with by thorough purging of the GC sample loop between samples.(D) Water vapor. To assure consistent detector response, calibration gases are contained in dry air. To adjust gaseous organic concentrations when water vapor is present in the sample, water vapor concentrations are determined for those samples, and a correction factor is applied.(E) Run-time. The gas chromatograph run time must be sufficient to clear all eluting peaks from the column before proceeding to the next run (in order to prevent sample carryover).
(A) Recovery study for direct interface or dilution interface sampling -- This is done to ensure that there are no significant leaks in the sampling system.(B) Recovery study for bag sampling -- This is done to demonstrate that proper sampling/analysis procedures were selected.(C) Recovery study for adsorption tube sampling -- This is done to demonstrate that proper sampling/analysis procedures were selected.
Maximum Holding Time:
< 1ppm to upper range of instrument
The sensitivity limit for a compound is defined as the minimum detectable concentration of that compound, or the concentration that produces a signal-to-noise ratio of three to one. The minimum detectable concentration is determined during the presurvey calibration for each compound.Adsorbents may be used to concentrate the sample, thus lowering the limit of detection below the 1 part per million (ppm) typically achievable with direct interface or bag sampling.
At least 16 analytes can be tested by ALS - Columbia using EPA Method 18. Please contact us for all available analytes which can be tested by EPA Method 18.
|Dimethyl Sulfoxide (DMSO)||67-68-5|
|Ethyl 3-Ethoxypropionate (EEP)||763-69-9|
|TPH as Stoddard Solvent||8052-41-3|
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