USGS-NWQL: O-3106-93:  Triazines in Water by Gas Chromatography

  • Summary
  • Analytes
  • Revision
  • Data and Sites
Official Method Name
Methods of Analysis by the U.S. Geological Survey National Water Quality Laboratory - Determination of Triazine and Other Nitrogen-Containing Compounds by Gas Chromatography with Nitr.-Phos. Detectors
Current Revision
1994
Media
WATER
Instrumentation
Gas Chromatography with Nitrogen - Phosphorus Detection
Method Subcategory
Organic
Method Source
  USGS-NWQL
Citation
Markovchick, D.J., Lewis, J.A., Brenton, R.W., Iverson, J.L.,and Wharry, H.L., 1994, Methods of analysis by the U.S. Geological Survey National Water Quality Laboratory--Determination of triazine and other nitrogen-containing compounds by gas chromatography with nitrogen phosphorous detectors: U.S. Geological Survey Open-File Report 94-037.
Brief Method Summary
The pH of a measured volume (about 1 L) of sample is adjusted to range from 7.0 to 9.0. Then 50 g of NaCl is added and dissolved. The sample is extracted with methylene chloride. The methylene chloride extract is isolated, dried, and concentrated to a volume of 1 mL during a solvent exchange to methyl-t-butyl ether (MTBE). Chromatographic conditions are described that permit the separation and determination of the compounds in the extract by capillary column GC with a nitrogen phosphorus detector (NPD).
Scope and Application
This method is suitable for the determination of triazine herbicides and other selected nitrogen-containing compounds in water and mixtures of water-suspended sediment.
Applicable Concentration Range
0.1 - 5.0 (undiluted)
Interferences
Method interferences might be caused by contaminants in solvents, reagents, glassware, and other sample processing apparatus that lead to discrete artifacts or elevated baselines in gas chromatograms. All reagents and apparatus need to be routinely demonstrated to be free from interferences under the conditions of the analysis by running laboratory reagent blanks. The use of ultrapure solvents and reagents will help to minimize interference problems. System contamination might interfere when a sample containing small concentrations of compounds is analyzed immediately following a sample containing large concentrations of compounds. After a sample is injected, the syringe is rinsed 10 times with solvent to reduce the chance of cross-contamination. Matrix interferences might be caused by contaminants that are coextracted from the sample. The extent of matrix interferences will vary from source to source, depending on the water sampled. This potential problem is addressed using a dual column confirmation procedure. If there are further questions about compound identification, the sample is submitted for confirmation using gas chromatography/mass spectrometry (GC/MS). It is important that samples and calibration standards be contained in the same solvent. If this is not the case, chromatographic comparability of standards to sample might be affected.
Quality Control Requirements
Quality-control samples area analyzed at a minimum of one in every ten samples. These QC samples include at least one of each of the following: blanks, quality control samples, third party check solutions, replicates, and spikes. Correlation coefficients for calibration curves must be at least 0.99. QC samples must fall within 1.5 standard deviations of the mean value. If all of the data-acceptance criteria in the SOPs are met, then the analytical data are acceptable.
Sample Handling
This schedule consumes the entire sample. Description: 1 L Glass bottle, amber bottle baked at 450oC by laboratory. Chill sample and maintain at 4oC, ship immediately.
Maximum Holding Time
7 days from arrival at the lab
Relative Cost
$201 to $400
Sample Preparation Methods