EPA-OGWDW/TSC: 515.4:  Chlorinated Acids by GCECD

  • Summary
  • Analytes
  • Revision
  • Data and Sites
Official Method Name
Determination of Chlorinated Acids in Drinking Water by Liquid-Liquid Microextraction, Derivitization, and Fast Gas Chromatography with Electron Capture Detection
Current Revision
Revision 1.0, April 2000
Media
WATER
Instrumentation
Gas Chromatography with Electron Capture Detection
Method Subcategory
Organic
Method Source
  EPA-OGWDW/TSC
Citation
  Methods for the Determination of Organic and Inorganic Compounds in Drinking Water, Volume 1 (EPA/815-R-00-014)
Brief Method Summary
A 40-mL sample is adjusted to alkaline pH and is allowed to sit for one hour to hydrolyze derivatives. The sample is then washed with hexane:MTBE to clean the sample. The aqueous phase is acidified and extracted with MTBE. Chlorinated acids in the MTBE are converted to methyl esters using diazomethane. The concentrations of the derivatized chlorinated acids (now esters) in the extract are measured using a fast capillary column gas chromatography (GC) system equipped with an electron capture detector (ECD).

Note: Method 515.4 calls for a solvent wash step after hydrolysis and prior to acidification and derivatization. Dacthal, the parent di-ester, does not hydrolyze, and is extracted in the wash step, leaving the mono- and di-acid metabolites to be measured.
Scope and Application
This method determines chlorinated acids in drinking waters.
Applicable Concentration Range
0.5-20 ug/L for a 40 mL sample was tested.
Interferences

(A) Glassware contamination: Solvent rinse and bake glassware to minimize contamination.

(B) Sodium sulfate: Sodium sulfate often contains contaminants. Analyze blanks with sodium sulfate to determine if the sodium sulfate is contaminated.

(C) Co-extracted interferences: Compounds that are co-extracted with analytes may interfere. Some matrices tested contained an interference with Dalapon which was resolved by using as low initial temperature program.

(D) Phthalate ester interference: Avoid the use of plastics and use pure reagents to avoid contamination by these ubiquitous compounds.

Quality Control Requirements
Initial Demonstration of Capability (IDC), determination of MDL, subsequent analysis in each analysis batch of a Laboratory Reagent Blank (LRB), Continuing Calibration Check Standards (CCC), a Laboratory Fortified Sample Matrix (LFM), and either a Laboratory Fortified Sample Matrix Duplicate (LFMD) or a Field Duplicate Sample.
Sample Handling
Grab samples must be collected in accordance with conventional sampling practices using amber glass containers with PTFE-lined screw caps and capacities of at least 40 mL. Dechlorinate sample with sodium sulfite (approximately 2 mg/40 mL of sample) prior to collection. After collection, seal the bottle and agitate by hand for 15 seconds. All samples should be iced during shipment and must not exceed 10oC during the first 48 hours after collection. Samples stored in lab must be held at or below 6oC, but not frozen, and protected from light until extraction. Extracts must be stored at or below 0oC and protected form light in glass vials with PTFE-lined caps.
Maximum Holding Time
Extract samples with 14 days of collection.
Analyze samples within 21 days of extraction.
Relative Cost
$201 to $400
Sample Preparation Methods