EPA-OGWDW/TSC: 508.1: Chlorinated Pesticides, Herbicides, and Organohalides in Water by GCECD
- Summary
- Analytes
- Revision
- Data and Sites
Official Method Name
|
Determination of Chlorinated Pesticides, Herbicides, and Organohalides by Liquid-Solid Extraction and Electron Capture Gas Chromatography | ||||
---|---|---|---|---|---|
Current Revision
| Revision 2.0, 1995 | ||||
Media
|
WATER | ||||
Instrumentation
|
Gas Chromatography with Electron Capture Detection | ||||
Method Subcategory
|
Organic | ||||
Method Source
|
EPA-OGWDW/TSC
|
||||
Citation
|
Methods for the Determination of Organic Compounds in Drinking Water - Supplement III (EPA/600/R-95-131)
|
||||
Brief Method Summary
|
A 1-L sample is passed through a liquid/solid extraction (LSE) disk or cartridge containing a solid inorganic matrix coated with a chemically bonded C-18 organic phase. The analytes (pesticides, herbicides, and organohalides) are eluted from the LSE disk or cartridge with small volumes of ethyl acetate and methylene chloride, and this eluate is concentrated by evaporation of some of the solvent. The concentrations of analytes are determined using a fused silica capillary column gas chromatography (GC) system equipped with an electron capture detector (ECD). NOTE: CAS Numbers in NEMI for cis- and trans- permethrin differ from those in the method. The CAS Numbers in NEMI are the correct ones. |
||||
Scope and Application
|
This method determines 29 chlorinated pesticides, three herbicides, and four organohalides in drinking water, ground water, and drinking water in any treatment stage. | ||||
Applicable Concentration Range
|
Ranges differ for each analyte depending on matrix and instrumentation. | ||||
Interferences
|
(A) Reagent contamination: Use high purity reagents. (B) Contamination from sample carryover: Rinsing apparatus replacing syringes and injection port liners as needed can minimize contamination. (C) Variable solvents: Use the same solvent for each analysis. |
||||
Quality Control Requirements
|
Initial demonstration of laboratory capability, followed by laboratory reagent blanks (LRBs), laboratory fortified blanks (LFBs), and laboratory fortified matrix samples. Additional quality control practices are recommended. Initial demonstration of capability is demonstrated by analysis of a minimum of four replicate LFBs containing each analyte of concern at a suggested concentration in the range of 0.01 - 0.5 ug/L. The mean accuracy should be 70% to 130% and the RSD should be less than 30%. A method detection limit (MDL) must also be determined for each analyte. |
||||
Sample Handling
|
Dechlorinate samples by adding 50 mg/L of sodium sulfite. Adjust the sample to a pH less than 2 by adding up to 4 mL of 6N HCl. Sample should be kept sealed from collection until analysis. Sampling equipment must not use plastic tubing, plastic gaskets, or any parts that may leach interfering analytes into the sample. Store samples at 4oC until analysis. NOTE: Samples collected for cyanazine determination MUST NOT be dechlorinated or acidified when collected. Acidification and dechlorination must occur immediately prior to fortification with surrogate standard and extraction. |
||||
Maximum Holding Time
|
14 days. |
||||
Relative Cost
|
$201 to $400 | ||||
Sample Preparation Methods
|
Analyte | Detection Level |
Bias | Precision | Pct False Positive |
Pct False Negative |
Spiking Level |
---|---|---|---|---|---|---|
4,4'-DDD(72-54-8)
|
0.003 ug/L | 90% Rec (SL) | 8.89 % RSD (SL) | 0.01 ug/L | ||
4,4'-DDE(72-55-9)
|
0.003 ug/L | 80% Rec (SL) | 11.20 % RSD (SL) | 0.01 ug/L | ||
Alachlor(15972-60-8)
|
0.009 ug/L | 80% Rec (SL) | 37.50 % RSD (SL) | 0.01 ug/L | ||
Aldrin(309-00-2)
|
0.009 ug/L | 80% Rec (SL) | 37.50 % RSD (SL) | 0.01 ug/L | ||
Atrazine(1912-24-9)
|
0.003 ug/L | 140% Rec (SL) | 7.14 % RSD (SL) | 0.01 ug/L | ||
Biopermethrin(51877-74-8)
|
0.007 ug/L | 110% Rec (SL) | 20.00 % RSD (SL) | 0.01 ug/L | ||
Butachlor(23184-66-9)
|
0.070 ug/L | 86% Rec (SL) | 5.50 % RSD (SL) | 0.50 ug/L | ||
Chlordane(57-74-9)
|
N/A | N/A | N/A | |||
Chlorobenzilate(510-15-6)
|
0.002 ug/L | 80% Rec (SL) | 8.75 % RSD (SL) | 0.01 ug/L | ||
Chloroneb(2675-77-6)
|
0.006 ug/L | 120% Rec (SL) | 15.80 % RSD (SL) | 0.01 ug/L | ||
Chlorothalonil(1897-45-6)
|
0.002 ug/L | 70% Rec (SL) | 10.00 % RSD (SL) | 0.01 ug/L | ||
Cyanazine(21725-46-2)
|
0.007 ug/L | 100% Rec (SL) | 22.00 % RSD (SL) | 0.01 ug/L | ||
DCPA(1861-32-1)
|
0.009 ug/L | 100% Rec (SL) | 28.00 % RSD (SL) | 0.01 ug/L | ||
Dieldrin(60-57-1)
|
0.003 ug/L | 70% Rec (SL) | 12.90 % RSD (SL) | 0.01 ug/L | ||
Endosulfan sulfate(1031-07-8)
|
0.003 ug/L | 70% Rec (SL) | 14.30 % RSD (SL) | 0.01 ug/L | ||
Endosulfan-I(959-98-8)
|
0.006 ug/L | 70% Rec (SL) | 27.10 % RSD (SL) | 0.01 ug/L | ||
Endosulfan-II(33213-65-9)
|
0.001 ug/L | 70% Rec (SL) | 42.90 % RSD (SL) | 0.01 ug/L | ||
Endrin(72-20-8)
|
0.007 ug/L | 150% Rec (SL) | 15.30 % RSD (SL) | 0.01 ug/L | ||
Endrin aldehyde(7421-93-4)
|
0.004 ug/L | 80% Rec (SL) | 15.00 % RSD (SL) | 0.01 ug/L | ||
Etridiazole(2593-15-9)
|
0.010 ug/L | 110% Rec (SL) | 40.90 % RSD (SL) | 0.01 ug/L | ||
Heptachlor(76-44-8)
|
0.005 ug/L | 90% Rec (SL) | 17.80 % RSD (SL) | 0.01 ug/L | ||
Heptachlor epoxide(1024-57-3)
|
0.001 ug/L | 60% Rec (SL) | 5.00 % RSD (SL) | 0.01 ug/L | ||
Herbicides(E-12839)
|
N/A | N/A | N/A | |||
Hexachlorobenzene(118-74-1)
|
0.001 ug/L | 100% Rec (SL) | 4.00 % RSD (SL) | 0.01 ug/L | ||
Hexachlorocyclopentadiene(77-47-4)
|
0.004 ug/L | 40% Rec (SL) | 32.50 % RSD (SL) | 0.01 ug/L | ||
Lindane(58-89-9)
|
0.006 ug/L | 70% Rec (SL) | 28.60 % RSD (SL) | 0.01 ug/L | ||
Methoxychlor(72-43-5)
|
0.003 ug/L | 60% Rec (SL) | 15.00 % RSD (SL) | 0.01 ug/L | ||
Metolachlor(51218-45-2)
|
0.015 ug/L | 113% Rec (SL) | 18.20 % RSD (SL) | 0.03 ug/L | ||
Metribuzin(21087-64-9)
|
0.009 ug/L | 90% Rec (SL) | 31.10 % RSD (SL) | 0.01 ug/L | ||
Organics, semivolatile(E-12884)
|
N/A | N/A | N/A | |||
Organochlorine pesticides(E-12851)
|
N/A | N/A | N/A | |||
PCB-1016(12674-11-2)
|
0.029 ug/L | 82% Rec (SL) | 5.70 % RSD (SL) | 0.20 ug/L | ||
PCB-1221(11104-28-2)
|
0.037 ug/L | 85% Rec (SL) | 6.80 % RSD (SL) | 0.20 ug/L | ||
PCB-1232(11141-16-5)
|
0.033 ug/L | 90% Rec (SL) | 5.80 % RSD (SL) | 0.20 ug/L | ||
PCB-1242(53469-21-9)
|
0.043 ug/L | 100% Rec (SL) | 6.90 % RSD (SL) | 0.20 ug/L | ||
PCB-1248(12672-29-6)
|
0.044 ug/L | 88% Rec (SL) | 8.00 % RSD (SL) | 0.20 ug/L | ||
PCB-1254(11097-69-1)
|
0.036 ug/L | 82% Rec (SL) | 7.00 % RSD (SL) | 0.20 ug/L | ||
PCB-1260(11096-82-5)
|
0.012 ug/L | 82% Rec (SL) | 2.40 % RSD (SL) | 0.20 ug/L | ||
PCBs(1336-36-3)
|
N/A | N/A | N/A | |||
Propachlor(1918-16-7)
|
0.008 ug/L | 80% Rec (SL) | 33.80 % RSD (SL) | 0.01 ug/L | ||
Simazine(122-34-9)
|
0.008 ug/L | 90% Rec (SL) | 27.80 % RSD (SL) | 0.01 ug/L | ||
Toxaphene(8001-35-2)
|
0.130 ug/L | 81% Rec (SL) | 5.10 % RSD (SL) | 1.00 ug/L | ||
Trifluralin(1582-09-8)
|
0.001 ug/L | 60% Rec (SL) | 5.00 % RSD (SL) | 0.01 ug/L | ||
alpha-BHC(319-84-6)
|
0.001 ug/L | 70% Rec (SL) | 42.80 % RSD (SL) | 0.01 ug/L | ||
alpha-Chlordane(5103-71-9)
|
0.004 ug/L | 70% Rec (SL) | 17.10 % RSD (SL) | 0.01 ug/L | ||
beta-BHC(319-85-7)
|
0.009 ug/L | 90% Rec (SL) | 32.20 % RSD (SL) | 0.01 ug/L | ||
cis-Permethrin(61949-76-6)
|
0.009 ug/L | 70% Rec (SL) | 42.90 % RSD (SL) | 0.01 ug/L | ||
delta-BHC(319-86-8)
|
0.004 ug/L | 80% Rec (SL) | 17.50 % RSD (SL) | 0.01 ug/L | ||
p,p'-DDT(50-29-3)
|
0.004 ug/L | 120% Rec (SL) | 9.20 % RSD (SL) | 0.01 ug/L | ||
trans-Chlordane(5103-74-2)
|
0.001 ug/L | 60% Rec (SL) | 50.00 % RSD (SL) | 0.01 ug/L | ||
trans-Permethrin(61949-77-7)
|
0.007 ug/L | 110% Rec (SL) | 20.00 % RSD (SL) | 0.01 ug/L |
Precision Descriptor Notes: | Precision and accuracy values determined using single laboratory data from seven replicate measurements of reagent water sample fortified with the analytes of interest. NOTE: "PCBs" is a regulatory parameter in drinking water regulations, and encompasses the sum of multiple Aroclors. See performance data for specific Aroclors. NOTE: CAS Numbers in NEMI for cis- and trans- permethrin differ from those in the method. The CAS Numbers in NEMI are the correct ones. |
---|---|
Detection Level Note: | MDLs were determined using the standard deviation of 7 replicate analyses of an analyte-fortified reagent water sample multiplied by the t-value for 6 degrees of freedom at the 99% confidence level. Detailed instructions for how MDLs are determined are found at 40 CFR part 136, Appendix B. |
Revision | PDF/Link |
---|---|
Revision 2.0, 1995 |