NEMI Method Summary

Method Summary Information

Method Number: 548.1 (by FID) Media: WATER
Revision: Revision 1.0, August 1992
Method Source: U.S. EPA National Exposure Research Laboratory (NERL) [formerly EMSL]
Analytes in this method
Subcategory: ORGANIC
Official Name: Determination of Endothall in Drinking Water by Ion-Exchange Extraction, Acidic Methanol Methylation, and Gas Chromatography/Mass Spectrometry
Descriptive Name Endothall in Water Using GCMS
Source Info: U.S.EPA National Exposure Research Laboratory (NERL)
Microbiological and Chemical Exposure Assessment Research Division (MCEARD)
[formerly the Environmental Monitoring Systems Laboratory (EMSL), Cincinnati, OH]
26 West Martin Luther King Drive
Cincinnati, Ohio 45268-0001
Fax: 513-569-7757
email: DWmethods.help@epa.gov
Citation: Methods for the Determination of Organic Compounds in Drinking Water - Supplement II (EPA/600/R-92-129)
209008 Byte file
Brief Method
Summary:
 A 100-mL sample is passed through a liquid/solid extraction (LSE) cartridge containing an intermediate strength, primarily tertiary amine anion exchanger mounted on a vacuum manifold and conditioned with appropriate solvents. Extracted endothall is eluted from the LSE cartridge with 8-mL of acidic methanol. After adding a small volume of methylene chloride as a co-solvent, the dimethyl ester of endothall is formed within 30 minutes with modest heating. After addition of salted reagent water, the ester is partitioned into 8-10 mL of methylene chloride. The extract volume is reduced with a nitrogen purge. The concentration of endothall in the extract is measured using a megabore capillary column gas chromatography (GC) system equipped with a mass spectrometer detector (MS) or a flame ionization detector (FID). A FID may be utilized for the determination of endothall, but must be supported by an additional analysis using a confirmatory gas chromatographic column.
Scope And
Application:
 This method determines endothall in drinking water sources and finished drinking water.
Applicable
Conc Range:
 Not specified in method. Range differs depending on matrix and instrumentation.
Interferences:

(A) Glassware contamination: Thoroughly clean glassware, including baking or solvent rinse.

(B) Reagent contamination: Use high purity reagents.

(C) Ion interferences: Ca+2 and Mg+2 and sulfate lower recovery by interfering with the ion exchange process.

(D) Extracted interferences: Interference from extracted non-target compounds, with retention times similar to target compounds, can be reduced by cleaning the extract.
QC Requirements:

Initial demonstration of laboratory capability, followed by analysis of laboratory reagent blanks (LRBs), laboratory fortified matrix samples, laboratory fortified blanks (LFBs), and QC check standards. A MDL also must be determined.
Sample Handling:

Grab samples must be collected in glass containers following conventional sampling practices without prerinsing the bottle before collection. Composite samples should be collected in refrigerated glass containers. Automatic sampling equipment must be as free as possible of plastic tubing and other potential sources of contamination. Dechlorinate with the addition of 80 mg of sodium thiosulfate per L of sample prior to sample collection. Store samples at 4oC away from light and heat until analysis. Biologically active samples should be acidified to pH 1.5 to 2 with the addition of 1:1 HCl:H20.
Max Holding Time:

7 days; 14 days for extracts.
 
Relative Cost: $201 to $400
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