USGS-NWQL: O-1131-95:  Pesticides in Water by Solid Phase Extraction and High Performance Liquid Chromatography (HPLC)

  • Summary
  • Analytes
  • Revision
  • Data and Sites
Official Method Name
Methods of Analysis by the U.S. Geological Survey National Water Quality Laboratory - Determination of Pesticides in Water by CarboPak-B Solid-Phase Extraction and HPLC
Current Revision
1996
Media
WATER
Instrumentation
High Performance Liquid Chromatography with Ultraviolet Detection
Method Subcategory
Organic
Method Source
  USGS-NWQL
Citation
Werner, S.L., Burkhardt, M.R., and DeRusseau, S.N., 1996, Methods of analysis by the U.S. Geological Survey National Water Quality Laboratory -- Determination of pesticides in water by Carbopak-B solid-phase extraction and high-performance liquid chromatography: U.S. Geological Survey Open-File Report 96-216.
Brief Method Summary
One liter of prefiltered water is pumped through the SPE cartridge at 25 mL/min. After extraction the adsorbed base and neutral compounds are eluted from the SPE cartridge using 6 mL of an 80:20 (v:v) mixture of methylene chloride and methanol. The acidic compounds are eluted from the same cartridge into a second collection container using 8 mL of the 80:20 solution that has been acidified with trifluoroacetic acid (TFAA) at 0.2 percent. The methylene chloride is removed from both fractions and is replaced with a water-methanol mixture; the final volume is 800 uL. The water-methanol solutions minimizes methylene chloride interference on the HPLC. Compounds are determined in each fraction by HPLC using ultraviolet spectrometry for detection, indentification and quantification.
Scope and Application
This method is designed for the determination of 41 pesticides and pesticide metabolites in filtered natural-water samples. The method is applicable to pesticides that are efficiently partitioned into a graphitized carbon-based solid-phase extraction (SPE) material and are chromatographically resolved and identified using an HPLC equipped with a diode array detector.
Applicable Concentration Range
0.006 - 1.6 (undiluted)
Interferences
Interferences may be caused by compounds recovered from a sample matrix that have similar chemical and physical properties and are not chromatographically resolved from the compounds of interest.
Quality Control Requirements
Laboratory extraction samples are formed into sets of 10 environmental samples plus a blank and a spike for a total set number of 12 samples. In addition, the following QA/QC samples are analyzed with each set of environmental samples: laboratory control spike (LCS), laboratory reagent blank (LRB), continuous calibration verification (CCV), continuing calibration blank (CCB), surrogate, field equipment blank (FEB) and field matrix spike (FMS). See USGS OFR 96-216 for definitions for each QA/QC sample.
Sample Handling
This schedule consumes the entire sample. Description: 1 L Glass bottle, amber bottle baked at 450 deg C by laboratory. Filter sample through a burned glass fiber filter. Treatment and Preservation: 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 4 deg C, ship immediately.
Maximum Holding Time
7 days from arrival at the NWQL
Relative Cost
$201 to $400
Sample Preparation Methods