USGS-NWQL: O-1121-91:  Organonitrogen Herbicides in Water by Solid Phase Extraction, GC/MS

  • Summary
  • Analytes
  • Revision
  • Data and Sites
Official Method Name
Methods of analysis by the U.S. Geological Survey National Water Quality Laboratory -Determination of organonitrogen herbicides in water by C-18 SPE and capillary-column GC-MS with selected-ion monito
Current Revision
1994
Media
WATER
Instrumentation
Gas Chromatography with Mass Spectrometry Detection
Method Subcategory
Organic
Method Source
  USGS-NWQL
Citation
M.W. Sandstrom, D.S. Wydoski, M.P. Schroeder, J.L. Zamboni and W.T. Foreman, 1992, Methods of analysis by the U.S. Geological Survey National Water Quality Laboratory--Determination of organonitrogen herbicides in water by solid-phase extraction and capillary-column gas chromatography/mass spectrometry with selected-ion monitoring: U.S. Geological Survey Open-File Report 91-519
Brief Method Summary
Water samples (100 mL) are filtered to remove suspended particulate matter. Glass-fiber filters with a nominal 0.7-um pore diameter or disposable, in-line filter units, containing a nylon membrane with a nominal 0.45-um pore diameter depending on the concentration of the suspended particulate matter in the water samples, are used. Filtered water samples are pumped through disposable, polypropylene SPE cartridges containing 0.5 g of porous silica coated with a C-18 organic phase that is chemically bonded to the surface of the silica. The SPE cartridges are dried using a gentle stream of carbon dioxide to remove interstitial water. The adsorbed herbicides and metabolites are removed from the SPE cartridges by elution with 1.8 mL of hexane-isopropanol (3:1). The eluant is further evaporated using a gentle stream of nitrogen to a final volume of 100 uL. Extracts of the eluant are analyzed by a capillary-column GC/MS operated in the SIM mode.
Scope and Application
This method is suitable for the determination of selected organonitrogen herbicides and metabolites in natural-water samples containing at least 0.05 ug/L of each herbicide or metabolite. The method is applicable to herbicides and metabolites that are: (1) efficiently partitioned from the water phase onto an octadecyl (C-18) organic phase that is chemically bonded to a solid inorganic matrix; and (2) sufficiently volatile and thermally stable for gas chromatogrphy. Suspended particulate matter is removed from the samples by filtration, so this method is suitable only for dissolved-phase herbicides and metabolites. The method was used to determine the concentrations of the 23 herbicides and the 2 metabolites of atrazine-desethylatrazine and desisopropylatrazone.
Previously completed development of the method (Sandstrom, 1989), as well as other comparable methods (Thurman and others, 1990) served as background for this report. Testing of the method included adjustment of sample volume and final extract volume to optimize recovery of the herbicides, especially the metabolites of atrazine-destylatrazine and desisopropylatrazine.
Applicable Concentration Range
>0.05
Interferences
Organic compounds having gas-chromatographic retention times and characteristic ions with a mass identical to those of the herbicides and metabolites of interest may interfere.
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, 125-mL, or 60-mL (see schedule for size) glass amber bottle baked at 450oC by laboratory. Some GCC's should be filtered. CHECK METHOD REFERENCE OR E-MAIL LABHELP@USGS.GOV FOR FILTERING REQUIREMENTS. DO NOT RINSE BOTTLE. Do not fill bottle beyond shoulder. Reagents must be added to the sample at the NWQL before analyses. Chill sample and maintain at 4oC and ship immediately.
Maximum Holding Time
Relative Cost
$201 to $400
Sample Preparation Methods
USGS-WRIR 95-4105