EPA-RCA: 8111:  Haloethers in Water, Soil, and Waste Samples by Chromatography and Electron Capture Detection

  • Summary
  • Analytes
  • Revision
  • Data and Sites
Official Method Name
Haloethers by Gas Chromatography
Current Revision
Revision 0, December 1996
Media
VARIOUS
Instrumentation
Gas Chromatography with Electron Capture Detection
Method Subcategory
Organic
Method Source
  EPA-RCA
Citation
  SW-846 Online: Test Methods for Evaluating Solid Waste, Physical/Chemical Methods
Brief Method Summary
Samples are extracted and cleaned up (according to sample matrix) and the solvent appropriately exchanged. The samples are directly injected into a gas chromatograph where they are analyzed using a wide-bore capillary column and an electron capture detector.
Scope and Application
This method determines the concentration of haloethers in water, soil, and waste samples by using wide-bore open-tubular, capillary-column gas chromatography procedures while utilizing either single-column/single detector or dual column/dual-detector approaches.
Applicable Concentration Range
Not Available.
Interferences
(A) Memory Interferences: Carryover may occur whenever high and low concentration samples are analyzed in sequence. For prevention, rinse the sample syringe between samples with solvent. Also, unusually concentrated samples should be followed by the analysis of a solvent blank. Additional solvent blanks interspersed with the sample extracts should be analyzed whenever a solvent blank indicates cross-contamination.
(B) Coeluting Compounds: Some compounds coelute using this procedure, in which case, they must be reported as coeluting. The samples may be reanalyzed by GC/MS. Dichlorobenzenes are known to coelute with haloethers under certain conditions, in which case, it may be necessary to analyze the extract with two different column packings to resolve all of the compounds.
(C) Electronegative Compound Interferences: Interferences may be caused by halogenated compounds, phthalates, and other oxygenated compounds, in which case, second column or GC/MS confirmation is necessary to ensure proper analyte identification.
(D) Method interferences: Contaminants in solvents, reagents, glassware, and other sample processing hardware may lead to elevated baselines and/or other interferences in the gas chromatograms. Routine analysis of reagent blanks should be performed as a check for method interferences.
(E) Refer to Methods 3500, 3600, and 8000.
Quality Control Requirements
Refer to Chapter One and Methods 8000, 3500, and 5000 for specific QC procedures. Procedures include: validation of sample preparation, introduction, and analysis, initial demonstration of proficiency, calibration verification, evaluation of retention times, analysis of method blanks, matrix spikes, duplicates, surrogates, and laboratory control samples. In addition, refer to Method 8000, Section 8.0 for QC procedures on preparation and analysis.
Sample Handling
See SW-846 Chapter Four for information. See the introductory material to this chapter, "Organic Analytes", Section 4.1. Extracts must be stored in the dark at or below 4oC.
Maximum Holding Time
Aqueous samples - 7 days (sample), 40 days (extract). Solid samples - 14 days (sample), 40 (extract). Also, see SW-846 Chapter Four for information.
Relative Cost
$201 to $400
Sample Preparation Methods
3500, 3510, 3520, 3600, 3620, 3640, 3660