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
Contact Information:
USGS National Water Quality Laboratory
P.O. Box 25046, MS 407, Buildling 95
Denver Federal Center
Denver, CO 80225-0046
Phone 303.236.2000
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
This method has 43 analytes associated with it.
Analyte
Detection Level
Bias
Precision
Pct False Positive
Pct False Negative
Spiking Level
1-Napthol(90-15-3)
1-Hydroxynaphthalene
1-Naphthalenol
1-Napthol
Alpha-naphthol
0.007 ug/L
N/A
3.00 % RSD (SL)
2,4,5-T(93-76-5)
2,4,5-T
2,4,5-T Acid
2,4,5-Trichlorophenoxyacetic acid
2,4,5-trichloro-Acetic acid
Acetic acid, (2,4,5-trichlorophenoxy)-
Dacamine 4D
Weedone
0.010 ug/L
77% Rec (SL)
8.00 % RSD (SL)
0.50 ug/L
2,4-D(94-75-7)
2,4-D
2,4-D Acid
2,4-D [acetic acid, (2,4-dichlorophenoxy)-1]
2,4-Dichlorophenoxyacetic acid, salts and este
2,4-Dichlorophenoxyacetic acid, salts and esters
Acetic acid, (2,4-dichlorophenoxy)-
Hedonal
Trinoxol
Weed-b-gone
0.013 ug/L
71% Rec (SL)
9.00 % RSD (SL)
0.50 ug/L
2,4-DB(94-82-6)
2,4-DB
2,4-Dichlorophenoxybutyric acid
4-(2,4-Dichlorophenoxy)butyric acid
Butanoic acid, 4-(2,4-dichlorophenoxy)-
Butoxone
Butyrac
Butyric acid, 4-(2,4-dichlorophenoxy)-
Embutone
Legumex
Venceweed
0.013 ug/L
44% Rec (SL)
8.00 % RSD (SL)
0.50 ug/L
2-Methyl-4,6-dinitrophenol(534-52-1)
2,4-Dinitro-6-methyl-phenol
2,4-Dinitro-o-cresol
2-Methyl-4,6-dinitrophenol
4,6-Dinitro-o-cresol
DNOC
Dinitrocresol
Methyl-4,6-dinitrophenol,2-
Phenol, 2-methyl-4,6-dinitro-
0.006 ug/L
N/A
5.00 % RSD (SL)
3-Hydroxycarbofuran(16655-82-6)
3,7-Benzofurandiol, 2,3-dihydro-2,2-dimethyl-,
3-Hydroxycarbofuran
0.014 ug/L
64% Rec (SL)
7.00 % RSD (SL)
0.50 ug/L
Acifluorfen sodium(62476-59-9)
Acifluorfen sodium
Benzoic acid, 5-[2-chloro-4-(trifluoromethyl)phenoxy]-2-nitro-, sodium salt (9CI)
Single-operator method detection limits in organic-free water samples ranged from 0.006 - 0.032 ug/L. Recoveries in organic-free water samples ranged from 37 to 88 percent. Recoveries in ground- and surface-water samples ranged from 29 to 94 percent. The single-operator average standard deviation at a spike level of 0.1 ug/L in organic-free water is 8 percent. The multiple operator (5) and multiple instrument (7) average relative standard deviation for a 0.05 ug/L spike in organic-free water for the two year period April 1993 to April 1995 is 25 percent. Recoveries in organic-free water spiked at the 0.05 ug/L ranged from 22 to 100 percent.
Detection Level Note:
Method detection limits (MDLs) were determined for this method using the procedures of the U.S. Environmental Protection Agency (1997).
Revision
PDF/Link
1996
The Water Quality Portal contains
sample results from
sites that use this method.