EPA-RCA: 8081B: Organochlorine Pesticides by GC-ECD
- Summary
- Analytes
- Revision
- Data and Sites
Official Method Name
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Organochlorine Pesticides by Gas Chromatography | ||||
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Current Revision
| Revision 2, November 2000 | ||||
Media
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VARIOUS | ||||
Instrumentation
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Gas Chromatography with Electron Capture Detection | ||||
Method Subcategory
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Organic | ||||
Method Source
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EPA-RCA
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Citation
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SW-846 Update IVB
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Brief Method Summary
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A measured volume or weight of sample (approximately 1 L for liquids, 2 to 30 g for solids) is extracted using the appropriate matrix-specific sample extraction technique. A variety of cleanup steps may be applied to the extract, depending on the nature of the matrix interferences and the target analytes. Suggested cleanups include alumina (Method 3610), Florisil (Method 3620), silica gel (Method 3630), gel permeation chromatography (Method 3640), and sulfur (Method 3660). After cleanup, the extract is analyzed by injecting a measured aliquot into a gas chromatograph with either a narrow-bore or wide-bore fused-silica capillary column, and either an electron capture detector (GC/ECD) or an electrolytic conductivity detector (GC/ELCD). | ||||
Scope and Application
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Method 8081 may be used to determine the concentrations of various organochlorine pesticides in extracts from solid and liquid matrices, using fused-silica, open-tubular, capillary columns with electron capture detectors (ECD) or electrolytic conductivity detectors (ELCD). | ||||
Applicable Concentration Range
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None given. | ||||
Interferences
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(1) Contamination of samples, solvent, and carrier gases with target analytes (especially compounds common to environmental laboratories, like methylene chloride). (2) Contamination of samples with sulfur (primarily present in base-neutral fractions). (3) Septum bleed (compounds from the injection septum are analyzed with the sample). (4) Column bleed (compounds from column coating break down, decreasing column efficiency). (5) Ghost peaks (compounds adsorb strongly to the column and carry over to later runs). (6) Coelution of species. (7) Coextracted contaminants. (8) Phthalate esters interfere with detection of pesticides via electron capture detector. |
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Quality Control Requirements
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(see ch.1, SW-846 Methods 3500, 8000), CV, calibration standard, initial demonstration of proficiency, MB, MS, MSD, LD, LCS, and the addition of surrogates to each field sample and QC sample, CS (after 20 samples) | ||||
Sample Handling
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Store the extract in the refrigerator and analyze it within 40 days of extraction. See SW-846, Chapter 4, Organic Analytes, Section 4. See SW-846 Chapter Four for information. | ||||
Maximum Holding Time
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Aqueous samples - 7 days (sample), 40 days (extract). Solid samples - 14 days (sample), 40 (extract). Also, see SW-846 Chapter Four for information. | ||||
Relative Cost
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$201 to $400 | ||||
Sample Preparation Methods
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This method has 53 analytes associated with it.
Analyte | Detection Level |
Bias | Precision | Pct False Positive |
Pct False Negative |
Spiking Level |
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4,4'-DDD(72-54-8)
|
0.850 ug/L | 57% Rec (SL) | 11.00 % RSD (SL) | 500.00 ug/L | ||
4,4'-DDE(72-55-9)
|
0.590 ug/L | 52% Rec (SL) | 11.00 % RSD (SL) | 500.00 ug/L | ||
Alachlor(15972-60-8)
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N/A | N/A | N/A | |||
Aldrin(309-00-2)
|
0.830 ug/L | 92% Rec (SL) | 33.00 % RSD (SL) | 500.00 ug/L | ||
Biopermethrin(51877-74-8)
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N/A | N/A | N/A | |||
Chlordane(57-74-9)
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N/A | N/A | N/A | |||
Chlorobenzilate(510-15-6)
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N/A | N/A | N/A | |||
Chloroneb(2675-77-6)
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N/A | N/A | N/A | |||
Chlorothalonil(1897-45-6)
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N/A | N/A | N/A | |||
DBCP(96-12-8)
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N/A | N/A | N/A | |||
DCPA(1861-32-1)
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N/A | N/A | N/A | |||
Diallate(2303-16-4)
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N/A | N/A | N/A | |||
Dichlone(117-80-6)
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N/A | N/A | N/A | |||
Dicofol(115-32-2)
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N/A | N/A | N/A | |||
Dieldrin(60-57-1)
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N/A | 89% Rec (SL) | 19.00 % RSD (SL) | 500.00 ug/L | ||
Endosulfan sulfate(1031-07-8)
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N/A | N/A | N/A | |||
Endosulfan-I(959-98-8)
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0.510 ug/L | 52% Rec (SL) | 11.00 % RSD (SL) | 500.00 ug/L | ||
Endosulfan-II(33213-65-9)
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0.540 ug/L | 52% Rec (SL) | 10.00 % RSD (SL) | 500.00 ug/L | ||
Endrin(72-20-8)
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0.820 ug/L | 56% Rec (SL) | 10.00 % RSD (SL) | 500.00 ug/L | ||
Endrin aldehyde(7421-93-4)
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0.360 ug/L | 45% Rec (SL) | 6.00 % RSD (SL) | 500.00 ug/L | ||
Endrin ketone(53494-70-5)
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N/A | N/A | N/A | |||
Etridiazole(2593-15-9)
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N/A | N/A | N/A | |||
Halowax 1000(58718-66-4)
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N/A | N/A | N/A | |||
Halowax 1001(58718-67-5)
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N/A | N/A | N/A | |||
Halowax 1013(12616-35-2)
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N/A | N/A | N/A | |||
Halowax 1014(12616-36-3)
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N/A | N/A | N/A | |||
Halowax 1099(39450-05-0)
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N/A | N/A | N/A | |||
Heptachlor(76-44-8)
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0.560 ug/L | 60% Rec (SL) | 13.00 % RSD (SL) | 500.00 ug/L | ||
Heptachlor epoxide(1024-57-3)
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0.340 ug/L | 54% Rec (SL) | 11.00 % RSD (SL) | 500.00 ug/L | ||
Herbicides(E-12839)
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N/A | N/A | N/A | |||
Hexachlorobenzene(118-74-1)
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N/A | N/A | N/A | |||
Hexachlorocyclopentadiene(77-47-4)
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N/A | N/A | N/A | |||
Isodrin(465-73-6)
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N/A | N/A | N/A | |||
Lindane(58-89-9)
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0.320 ug/L | 55% Rec (SL) | 9.00 % RSD (SL) | 500.00 ug/L | ||
Methoxychlor(72-43-5)
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N/A | N/A | N/A | |||
Mirex(2385-85-5)
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N/A | N/A | N/A | |||
Nitrofen(1836-75-5)
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N/A | N/A | N/A | |||
Octachloronaphthalene(2234-13-1)
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N/A | N/A | N/A | |||
Organics, semivolatile(E-12884)
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N/A | N/A | N/A | |||
Organochlorine pesticides(E-12851)
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N/A | N/A | N/A | |||
Pentachloronitrobenzene(82-68-8)
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N/A | N/A | N/A | |||
Perthane(72-56-0)
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N/A | N/A | N/A | |||
Propachlor(1918-16-7)
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N/A | N/A | N/A | |||
Strobane(8001-50-1)
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N/A | N/A | N/A | |||
Toxaphene(8001-35-2)
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N/A | N/A | N/A | |||
Trifluralin(1582-09-8)
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N/A | N/A | N/A | |||
alpha-BHC(319-84-6)
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N/A | 88% Rec (SL) | 25.00 % RSD (SL) | 500.00 ug/L | ||
alpha-Chlordane(5103-71-9)
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0.580 ug/L | 49% Rec (SL) | 8.00 % RSD (SL) | 500.00 ug/L | ||
beta-BHC(319-85-7)
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0.200 ug/L | 351% Rec (SL) | 71.00 % RSD (SL) | 500.00 ug/L | ||
delta-BHC(319-86-8)
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0.350 ug/L | 51% Rec (SL) | 11.00 % RSD (SL) | 500.00 ug/L | ||
p,p'-DDT(50-29-3)
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0.710 ug/L | 57% Rec (SL) | 10.00 % RSD (SL) | 500.00 ug/L | ||
trans-Chlordane(5103-74-2)
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0.580 ug/L | 50% Rec (SL) | 9.00 % RSD (SL) | 500.00 ug/L | ||
trans-Nonachlor(39765-80-5)
|
N/A | N/A | N/A |
Precision Descriptor Notes: | NOTE: SPIKING CONCENTRATION FOR PRECISION AND ACCURACY IS IN UNITS OF NANOGRAMS per GRAM (ng/g). Precision and accuracy data was obtained using three replicate analyses of a sewage sludge spiked with 500 to 1000 ng/g of analyte. Sample clean-up was performed using ultrasonic extraction (see SW-846 Method 3550). The method contains additional performance information obtained with Soxhlet Extraction and Solid Phase Extraction. |
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Detection Level Note: | MDLs were determined using a solid phase extraction preparation (SW-846 Method 3535) through the analysis of 7 spiked wastewater replicates. |
Revision | PDF/Link |
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Revision 2, November 2000 |
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