USGS-NWQL: O-1126-95: Pesticides in Water by C-18 Solid-Phase Extraction and 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 Pesticides in Water by C-18 SPE and Capillary-Column GC-MS with Select-Ion Monitoring | ||||
---|---|---|---|---|---|
Current Revision
| 1995 | ||||
Media
|
WATER | ||||
Instrumentation
|
Gas Chromatography with Mass Spectrometry Detection | ||||
Method Subcategory
|
Organic | ||||
Method Source
|
USGS-NWQL
|
||||
Citation
|
Zaugg, S.D., Sandstrom, M.W., Smith, S.G., and Fehlberg, K.M., 1995, Methods of analysis by the U.S. Geological Survey National Water Quality Laboratory--Determination of pesticides in water by C-18 solid-phase extraction and capillary-column gas chromatography/mass spectrometry with selected-ion monitoring: U.S. Geological Survey Open-File Report 95-181.
|
||||
Brief Method Summary
|
The samples are filtered at the collection site using glass-fibre filters with 0.7 um pore diameter to remove suspended particulate matter. Filtered water samples are pumped through disposable polypropylene SPE columns containing porous silica coated with an octadecyl (C-18) phase that is chemically bonded to the surface of the silica. The SPE columns are dried using a gentle stream of carbon dioxide or nitrogen gas to remove residual water. The absorbed pesticides and metabolites are then removed from the SPE columns by elution with a hexane-isopropanol (3:1) solution. The eluant is further evaporated by a gentle stream of nitrogen. Extracts of the eluant are analyzed by capillary-column GC-MS operated in the SIM (Selected Ion Monitoring) mode. Acetochlor was added to the suite of analytes for this method in 1996. The methodology remains the same; however, this addition is documented in Lindley, C.E. and others, 1996, Journal of AOAC International, v.79, no.4. |
||||
Scope and Application
|
This method is suitable for the determination of low-level concentrations (in ug/L and ng/L) of pesticides and pesticide metabolites in natural-water samples. The method is applicable to pesticides and metabolites that are efficiently partitioned from the water phase onto an octadecyl (C-18) organic phase that is chemically bonded to an inorganic matrix and that are sufficiently volatile and thermally stable for gas chromatography. Suspended particulate matter is removed by filtration. This method is suitable only for dissolved-phase pesticides and metabolites. | ||||
Applicable Concentration Range
|
0.001 - 4.0 (undiluted) | ||||
Interferences
|
Organic compunds having gas-chromatographic retention times and characteristic ions with a mass identical to those of the pesticides 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 Glass bottle, amber bottle baked at 450oC by laboratory - SOME GCCs should be filtered CHECK METHOD REFERENCE OR EMAIL LABHELP@USGS.GOV FOR FILTERING REQUIREMENTS. 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 4oC, ship immediately. | ||||
Maximum Holding Time
|
7 days from arrival at the NWQL | ||||
Relative Cost
|
$201 to $400 | ||||
Sample Preparation Methods
|
USGS-WRIR 95-4105 |
This method has 51 analytes associated with it.
Analyte | Detection Level |
Bias | Precision | Pct False Positive |
Pct False Negative |
Spiking Level |
---|---|---|---|---|---|---|
( )-cis-Permethrin(54774-45-7)
|
0.016 ug/L | 37% Rec (SL) | 13.00 % RSD (SL) | 0.10 ug/L | ||
2,6-Diethylanaline(579-66-8)
|
0.006 ug/L | 73% Rec (SL) | 3.00 % RSD (SL) | 0.10 ug/L | ||
4,4'-DDE(72-55-9)
|
0.010 ug/L | 48% Rec (SL) | 6.00 % RSD (SL) | 0.10 ug/L | ||
Acetochlor(34256-82-1)
|
0.002 ug/L | 111% Rec (SL) | 4.60 % RSD (SL) | 0.01 ug/L | ||
Alachlor(15972-60-8)
|
0.009 ug/L | 86% Rec (SL) | 3.00 % RSD (SL) | 0.10 ug/L | ||
Atrazine(1912-24-9)
|
0.017 ug/L | 89% Rec (SL) | 6.00 % RSD (SL) | 0.10 ug/L | ||
Azinphos-methyl(86-50-0)
|
0.038 ug/L | 78% Rec (SL) | 15.00 % RSD (SL) | 0.10 ug/L | ||
Benefin(1861-40-1)
|
0.013 ug/L | 46% Rec (SL) | 9.00 % RSD (SL) | 0.10 ug/L | ||
Butylate(2008-41-5)
|
0.008 ug/L | 80% Rec (SL) | 3.00 % RSD (SL) | 0.10 ug/L | ||
Carbamate pesticides(E-12895)
|
N/A | N/A | N/A | |||
Carbaryl(63-25-2)
|
0.046 ug/L | 151% Rec (SL) | 10.00 % RSD (SL) | 0.10 ug/L | ||
Carbofuran(1563-66-2)
|
0.013 ug/L | 108% Rec (SL) | 4.00 % RSD (SL) | 0.10 ug/L | ||
Chlorpyrifos(2921-88-2)
|
0.005 ug/L | 83% Rec (SL) | 2.00 % RSD (SL) | 0.10 ug/L | ||
Cyanazine(21725-46-2)
|
0.013 ug/L | 96% Rec (SL) | 4.00 % RSD (SL) | 0.10 ug/L | ||
DCPA(1861-32-1)
|
0.004 ug/L | 82% Rec (SL) | 2.00 % RSD (SL) | 0.10 ug/L | ||
Desethylatrazine(6190-65-4)
|
0.003 ug/L | 12% Rec (SL) | 8.00 % RSD (SL) | 0.10 ug/L | ||
Diazinon(333-41-5)
|
0.008 ug/L | 77% Rec (SL) | 3.00 % RSD (SL) | 0.10 ug/L | ||
Dieldrin(60-57-1)
|
0.008 ug/L | 67% Rec (SL) | 4.00 % RSD (SL) | 0.10 ug/L | ||
Dimethoate(60-51-5)
|
0.024 ug/L | 11% Rec (SL) | 68.00 % RSD (SL) | 0.10 ug/L | ||
Disulfoton(298-04-4)
|
0.008 ug/L | 72% Rec (SL) | 4.00 % RSD (SL) | 0.10 ug/L | ||
EPTC(759-94-4)
|
0.005 ug/L | 80% Rec (SL) | 2.00 % RSD (SL) | 0.10 ug/L | ||
Ethalfluralin(55283-68-6)
|
0.013 ug/L | 54% Rec (SL) | 8.00 % RSD (SL) | 0.10 ug/L | ||
Ethoprophos(13194-48-4)
|
0.012 ug/L | 80% Rec (SL) | 5.00 % RSD (SL) | 0.10 ug/L | ||
Ethyl parathion(56-38-2)
|
0.022 ug/L | 83% Rec (SL) | 9.00 % RSD (SL) | 0.10 ug/L | ||
Fonofos(944-22-9)
|
0.008 ug/L | 75% Rec (SL) | 3.00 % RSD (SL) | 0.10 ug/L | ||
Lindane(58-89-9)
|
0.011 ug/L | 77% Rec (SL) | 4.00 % RSD (SL) | 0.10 ug/L | ||
Linuron(330-55-2)
|
0.039 ug/L | 126% Rec (SL) | 10.00 % RSD (SL) | 0.10 ug/L | ||
Malathion(121-75-5)
|
0.014 ug/L | 90% Rec (SL) | 5.00 % RSD (SL) | 0.10 ug/L | ||
Methyl parathion(298-00-0)
|
0.035 ug/L | 73% Rec (SL) | 15.00 % RSD (SL) | 0.10 ug/L | ||
Metolachlor(51218-45-2)
|
0.009 ug/L | 92% Rec (SL) | 3.00 % RSD (SL) | 0.10 ug/L | ||
Metribuzin(21087-64-9)
|
0.012 ug/L | 42% Rec (SL) | 9.00 % RSD (SL) | 0.10 ug/L | ||
Molinate(2212-67-1)
|
0.007 ug/L | 82% Rec (SL) | 3.00 % RSD (SL) | 0.10 ug/L | ||
Napropamide(15299-99-7)
|
0.010 ug/L | 83% Rec (SL) | 4.00 % RSD (SL) | 0.10 ug/L | ||
Organochlorine pesticides(E-12851)
|
N/A | N/A | N/A | |||
Organophosphate pesticides(E-12873)
|
N/A | N/A | N/A | |||
Pebulate(1114-71-2)
|
0.009 ug/L | 79% Rec (SL) | 4.00 % RSD (SL) | 0.10 ug/L | ||
Penoxalin(40487-42-1)
|
0.018 ug/L | 46% Rec (SL) | 13.00 % RSD (SL) | 0.10 ug/L | ||
Phorate(298-02-2)
|
0.011 ug/L | 77% Rec (SL) | 4.00 % RSD (SL) | 0.10 ug/L | ||
Prometon(1610-18-0)
|
0.008 ug/L | 77% Rec (SL) | 3.00 % RSD (SL) | 0.10 ug/L | ||
Pronamide(23950-58-5)
|
0.009 ug/L | 76% Rec (SL) | 4.00 % RSD (SL) | 0.10 ug/L | ||
Propachlor(1918-16-7)
|
0.015 ug/L | 79% Rec (SL) | 6.00 % RSD (SL) | 0.10 ug/L | ||
Propanil(709-98-8)
|
0.016 ug/L | 96% Rec (SL) | 5.00 % RSD (SL) | 0.10 ug/L | ||
Propargite(2312-35-8)
|
0.006 ug/L | 59% Rec (SL) | 3.00 % RSD (SL) | 0.10 ug/L | ||
Simazine(122-34-9)
|
0.008 ug/L | 76% Rec (SL) | 3.00 % RSD (SL) | 0.10 ug/L | ||
Tebuthiuron(34014-18-1)
|
0.015 ug/L | 88% Rec (SL) | 6.00 % RSD (SL) | 0.10 ug/L | ||
Terbacil(5902-51-2)
|
0.030 ug/L | 75% Rec (SL) | 13.00 % RSD (SL) | 0.10 ug/L | ||
Terbufos(13071-79-9)
|
0.012 ug/L | 74% Rec (SL) | 5.00 % RSD (SL) | 0.10 ug/L | ||
Thiobencarb(28249-77-6)
|
0.008 ug/L | 85% Rec (SL) | 3.00 % RSD (SL) | 0.10 ug/L | ||
Triallate(2303-17-5)
|
0.008 ug/L | 75% Rec (SL) | 4.00 % RSD (SL) | 0.10 ug/L | ||
Trifluralin(1582-09-8)
|
0.012 ug/L | 47% Rec (SL) | 8.00 % RSD (SL) | 0.10 ug/L | ||
alpha-BHC(319-84-6)
|
0.007 ug/L | 77% Rec (SL) | 3.00 % RSD (SL) | 0.10 ug/L |
Precision Descriptor Notes: | The average short-term, single-operator precision in reagent water at the 0.1 and 1.0 ug/L level is seven percent and the average recovery is seventy-three percent. The average precision of all compounds in reagent water at 0.01 ug/L is eight percent and the average recovery is eighty-three percent. Other precision information is available in USGS OFR 95-181. |
---|---|
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 |
---|---|
1995 |
The Water Quality Portal contains
sample results from
sites that use this method.
Download WQP data
Select data:
File format:
Sites where this method was used
Loading Sites ...