METHOD 8270D

SEMIVOLATILE ORGANIC COMPOUNDS BY GAS CHROMATOGRAPHY/MASS SPECTROMETRY (GC/MS)

1.0 SCOPE AND APPLICATION

1.1 Method 8270 is used to determine the concentration of semivolatile organic compounds in extracts prepared from many types of solid waste matrices, soils, air sampling media and water samples. Direct injection of a sample may be used in limited applications. The following compounds can be determined by this method:

Appropriate Preparation Techniques b

3540/ Compounds CAS No a 3510 352 3541 355 3580 0 0 Acenaphthene 83-32-9 X X X X X

1-Acetyl-2-thiourea 591-08-2 LR ND ND ND LR

Barban 101-27-9 LR ND ND ND LR Benzidine 92-87-5 CP CP CP CP CP Acenaphthylene 208-96-8 X X X X X Acetophenone 98-86-2 X ND ND ND X 2-Acetylaminofluorene 53-96-3 X ND ND ND X

Aldrin 309-00-2 X X X X X 117-79-3 X ND ND ND X 2-Aminoanthraquinone Aminoazobenzene 60-09-3 X ND ND ND X 92-67-1 X ND ND ND X 4-Aminobiphenyl 3-Amino-9-ethylcarbazole 132-32-1 X X ND ND ND Anilazine 101-05-3 X ND ND ND X Aniline 62-53-3 X X ND X X o-Anisidine 90-04-0 X ND ND ND X Anthracene 120-12-7 X X X X X Aramite 140-57-8 HS(43) ND ND ND X Aroclor 1016 12674-11-2 X X X X X Aroclor 1221 11104-28-2 X X X X X Aroclor 1232 11141-16-5 X X X X X Aroclor 1242 53469-21-9 X X X X X Aroclor 1248 12672-29-6 X X X X X Aroclor 1254 11097-69-1 X X X X X Aroclor 1260 11096-82-5 X X X X X Azinphos-methyl 86-50-0 HS(62) ND ND ND X

Benzoic acid 65-85-0 X X ND X X

CD-ROM 8270D - 1 Revision 4 January 1998Appropriate Preparation Techniques b

Compounds CAS No a 3510 352 3541 355 3540/ 3580 0 0 Benz(a)anthracene 56-55-3 X X X X X Benzo(b)fluoranthene 205-99-2 X X X X X Benzo(k)fluoranthene 207-08-9 X X X X X Benzo(g,h,i)perylene 191-24-2 X X X X X Benzo(a)pyrene 50-32-8 X X X X X p-Benzoquinone 106-51-4 OE ND ND ND X Benzyl alcohol 100-51-6 X X ND X X

α -BHC 319-84-6 X X X X X β -BHC 319-85-7 X X X X X δ -BHC 319-86-8 X X X X X γ -BHC (Lindane) 58-89-9 X X X X X 111-91-1 X X X X X Bis(2-chloroethoxy)methane 111-44-4 X X X X X Bis(2-chloroethyl) ether 108-60-1 X X X X X Bis(2-chloroisopropyl) ether 117-81-7 X X X X X Bis(2-ethylhexyl) phthalate ether 101-55-3 X X X X X 4-Bromophenyl phenyl Bromoxynil 1689-84-5 X ND ND ND X Butyl benzyl phthalate 85-68-7 X X X X X Captafol 2425-06-1 HS(55) ND ND ND X Captan 133-06-2 HS(40) ND ND ND X Carbaryl 63-25-2 X ND ND ND X Carbofuran 1563-66-2 X ND ND ND X Carbophenothion 786-19-6 X ND ND ND X Chlordane (NOS) 57-74-9 X X X X X Chlorfenvinphos 470-90-6 X ND ND ND X 4-Chloroaniline 106-47-8 X ND ND ND X Chlorobenzilate 510-15-6 X ND ND ND X 95-79-4 X ND ND ND X 5-Chloro-2-methylaniline 59-50-7 X X X X X 4-Chloro-3-methylphenol 3-(Chloromethyl)pyridine 6959-48-4 X ND ND ND X hydrochloride 90-13-1 X X X X X 1-Chloronaphthalene 91-58-7 X X X X X 2-Chloronaphthalene 95-57-8 X X X X X 2-Chlorophenol 95-83-0 X X ND ND ND 4-Chloro-1,2-phenylenediamine 4-Chloro-1,3-phenylenediamine 5131-60-2 X X ND ND ND 4-Chlorophenyl phenyl ether 7005-72-3 X X X X X

CD-ROM 8270D - 2 Revision 4 January 1998Appropriate Preparation Techniques b

Compounds CAS No a 3510 352 3541 355 3540/ 3580 0 0 Chrysene 218-01-9 X X X X X Coumaphos 56-72-4 X ND ND ND X p-Cresidine 120-71-8 X ND ND ND X Crotoxyphos 7700-17-6 X ND ND ND X 2-Cyclohexyl-4,6-dinitro-phenol 131-89-5 X ND ND ND LR 4,4'-DDD 72-54-8 X X X X X 4,4'-DDE 72-55-9 X X X X X 4,4'-DDT 50-29-3 X X X X X Demeton-O 298-03-3 HS(68) ND ND ND X Demeton-S 126-75-0 X ND ND ND X Diallate (cis or trans) 2303-16-4 X ND ND ND X 2,4-Diaminotoluene 95-80-7 DC,0E(42) ND ND ND X Dibenz(a,j)acridine 224-42-0 X ND ND ND X Dibenz(a,h)anthracene 53-70-3 X X X X X Dibenzofuran 132-64-9 X X ND X X Dibenzo(a,e)pyrene 192-65-4 ND ND ND ND X 1,2-Dibromo-3-chloropropane 96-12-8 X X ND ND ND Di-n-butyl phthalate 84-74-2 X X X X X Dichlone 117-80-6 OE ND ND ND X 1,2-Dichlorobenzene 95-50-1 X X X X X 1,3-Dichlorobenzene 541-73-1 X X X X X 1,4-Dichlorobenzene 106-46-7 X X X X X 3,3'-Dichlorobenzidine 91-94-1 X X X X X 120-83-2 X X X X X 2,4-Dichlorophenol 87-65-0 X ND ND ND X 2,6-Dichlorophenol Dichlorovos 62-73-7 X ND ND ND X Dicrotophos 141-66-2 X ND ND ND X Dieldrin 60-57-1 X X X X X Diethyl phthalate 84-66-2 X X X X X Diethylstilbestrol 56-53-1 AW,0S(67 ND ND ND X ) Diethyl sulfate 64-67-5 LR ND ND ND LR Dimethoate 60-51-5 HE,HS(31 ND ND ND X ) 3,3'-Dimethoxybenzidine 119-90-4 X ND ND ND LR Dimethylaminoazobenzene 60-11-7 X ND ND ND X 7,12-Dimethylbenz(a)-anthracene 57-97-6 CP(45) ND ND ND CP

CD-ROM 8270D - 3 Revision 4 January 1998Appropriate Preparation Techniques b

Compounds CAS No a 3510 352 3541 355 3540/ 3580 0 0 119-93-7 X ND ND ND X 3,3'-Dimethylbenzidine

α , α -Dimethylphenethylamine 122-09-8 ND ND ND ND X 105-67-9 X X X X X 2,4-Dimethylphenol Dimethyl phthalate 131-11-3 X X X X X 1,2-Dinitrobenzene 528-29-0 X ND ND ND X 1,3-Dinitrobenzene 99-65-0 X ND ND ND X 1,4-Dinitrobenzene 100-25-4 HE(14) ND ND ND X 534-52-1 X X X X X 4,6-Dinitro-2-methylphenol 51-28-5 X X X X X 2,4-Dinitrophenol 2,4-Dinitrotoluene 121-14-2 X X X X X 2,6-Dinitrotoluene 606-20-2 X X X X X Dinocap 39300-45-3 CP,HS(28 ND ND ND CP ) Dinoseb 88-85-7 X ND ND ND X Diphenylamine 122-39-4 X X X X X 57-41-0 X ND ND ND X 5,5-Diphenylhydantoin 122-66-7 X X X X X 1,2-Diphenylhydrazine Di-n-octyl phthalate 117-84-0 X X X X X Disulfoton 298-04-4 X ND ND ND X Endosulfan I 959-98-8 X X X X X Endosulfan II 33213-65-9 X X X X X Endosulfan sulfate 1031-07-8 X X X X X Endrin 72-20-8 X X X X X Endrin aldehyde 7421-93-4 X X X X X Endrin ketone 53494-70-5 X X ND X X EPN 2104-64-5 X ND ND ND X Ethion 563-12-2 X ND ND ND X Ethyl carbamate 51-79-6 DC(28) ND ND ND X Ethyl methanesulfonate 62-50-0 X ND ND ND X Famphur 52-85-7 X ND ND ND X Fensulfothion 115-90-2 X ND ND ND X Fenthion 55-38-9 X ND ND ND X Fluchloralin 33245-39-5 X ND ND ND X Fluoranthene 206-44-0 X X X X X Fluorene 86-73-7 X X X X X 321-60-8 X X X X X 2-Fluorobiphenyl (surr) 2-Fluorophenol (surr) 367-12-4 X X X X X

CD-ROM 8270D - 4 Revision 4 January 1998Appropriate Preparation Techniques b

Compounds CAS No a 3510 352 3541 355 3540/ 3580 0 0 Heptachlor 76-44-8 X X X X X Heptachlor epoxide 1024-57-3 X X X X X Hexachlorobenzene 118-74-1 X X X X X Hexachlorobutadiene 87-68-3 X X X X X Hexachlorocyclopentadiene 77-47-4 X X X X X Hexachloroethane 67-72-1 X X X X X Hexachlorophene 70-30-4 AW,CP(62 ND ND ND CP ) Hexachloropropene 1888-71-7 X ND ND ND X

4,4'-Methylenebis 101-14-4 OE,OS(0) ND ND ND LR (2-chloroaniline) Hexamethylphosphoramide 680-31-9 X ND ND ND X Hydroquinone 123-31-9 ND ND ND ND X 193-39-5 X X X X X Indeno(1,2,3-cd)pyrene Isodrin 465-73-6 X ND ND ND X Isophorone 78-59-1 X X X X X Isosafrole 120-58-1 DC(46) ND ND ND X Kepone 143-50-0 X ND ND ND X Leptophos 21609-90-5 X ND ND ND X Malathion 121-75-5 HS(5) ND ND ND X Maleic anhydride 108-31-6 HE ND ND ND X Mestranol 72-33-3 X ND ND ND X Methapyrilene 91-80-5 X ND ND ND X Methoxychlor 72-43-5 X ND ND ND X 3-Methylcholanthrene 56-49-5 X ND ND ND X

4,4'-Methylenebis(N,N-dimethyl- 101-61-1 X X ND ND ND aniline) Methyl methanesulfonate 66-27-3 X ND ND ND X 91-57-6 X X ND X X 2-Methylnaphthalene Methyl parathion 298-00-0 X ND ND ND X 95-48-7 X ND ND ND X 2-Methylphenol 108-39-4 X ND ND ND X 3-Methylphenol 106-44-5 X ND ND ND X 4-Methylphenol Mevinphos 7786-34-7 X ND ND ND X Mexacarbate 315-18-4 HE,HS(68 ND ND ND X ) Mirex 2385-85-5 X ND ND ND X Monocrotophos 6923-22-4 HE ND ND ND X

CD-ROM 8270D - 5 Revision 4 January 1998Appropriate Preparation Techniques b

Compounds CAS No a 3510 352 3541 355 3540/ 3580 0 0 Naled 300-76-5 X ND ND ND X Naphthalene 91-20-3 X X X X X 130-15-4 X ND ND ND X 1,4-Naphthoquinone 1-Naphthylamine 134-32-7 OS(44) ND ND ND X 91-59-8 X ND ND ND X 2-Naphthylamine Nicotine 54-11-5 DE(67) ND ND ND X 602-87-9 X ND ND ND X 5-Nitroacenaphthene 2-Nitroaniline 88-74-4 X X ND X X 3-Nitroaniline 99-09-2 X X ND X X 4-Nitroaniline 100-01-6 X X ND X X 5-Nitro-o-anisidine 99-59-2 X ND ND ND X Nitrobenzene 98-95-3 X X X X X 92-93-3 X ND ND ND X 4-Nitrobiphenyl Nitrofen 1836-75-5 X ND ND ND X 88-75-5 X X X X X 2-Nitrophenol 100-02-7 X X X X X 4-Nitrophenol 5-Nitro-o-toluidine 99-55-8 X X ND ND X 56-57-5 X ND ND ND X Nitroquinoline-1-oxide N-Nitrosodi-n-butylamine 924-16-3 X ND ND ND X N-Nitrosodiethylamine 55-18-5 X ND ND ND X N-Nitrosodimethylamine 62-75-9 X X X X X N-Nitrosomethylethylamine 10595-95-6 X ND ND ND X N-Nitrosodiphenylamine 86-30-6 X X X X X N-Nitrosodi-n-propylamine 621-64-7 X X X X X N-Nitrosomorpholine 59-89-2 ND ND ND ND X N-Nitrosopiperidine 100-75-4 X ND ND ND X N-Nitrosopyrrolidine 930-55-2 X ND ND ND X Octamethyl pyrophosphoramide 152-16-9 LR ND ND ND LR 101-80-4 X ND ND ND X 4,4'-Oxydianiline Parathion 56-38-2 X X ND ND X Pentachlorobenzene 608-93-5 X ND ND ND X Pentachloronitrobenzene 82-68-8 X ND ND ND X Pentachlorophenol 87-86-5 X X X X X Phenacetin 62-44-2 X ND ND ND X Phenanthrene 85-01-8 X X X X X Phenobarbital 50-06-6 X ND ND ND X Phenol 108-95-2 DC(28) X X X X

CD-ROM 8270D - 6 Revision 4 January 1998Appropriate Preparation Techniques b

Compounds CAS No a 3510 352 3541 355 3540/ 3580 0 0 106-50-3 X ND ND ND X

Phthalic anhydride 85-44-9 CP,HE(1) ND ND ND CP

Propylthiouracil 51-52-5 LR ND ND ND LR 1,4-Phenylenediamine Phorate 298-02-2 X ND ND ND X Phosalone 2310-17-0 HS(65) ND ND ND X Phosmet 732-11-6 HS(15) ND ND ND X Phosphamidon 13171-21-6 HE(63) ND ND ND X

2-Picoline (2-Methylpyridine) 109-06-8 X X ND ND ND Piperonyl sulfoxide 120-62-7 X ND ND ND X Pronamide 23950-58-5 X ND ND ND X

Pyrene 129-00-0 X X X X X Resorcinol 108-46-3 DC,OE(10 ND ND ND X ) Safrole 94-59-7 X ND ND ND X Strychnine 57-24-9 AW,0S(55 ND ND ND X ) Sulfallate 95-06-7 X ND ND ND X Terbufos 13071-79-9 X ND ND ND

Tetraethyl dithiopyrophosphate 3689-24-5 X X ND ND ND X 1,2,4,5-Tetrachlorobenzene 95-94-3 X ND ND ND X 58-90-2 X ND ND ND X 2,3,4,6-Tetrachlorophenol Tetrachlorvinphos 961-11-5 X ND ND ND X

Tetraethyl pyrophosphate 107-49-3 X ND ND ND X Thionazine 297-97-2 X ND ND ND X Thiophenol (Benzenethiol) 108-98-5 X ND ND ND X Toluene diisocyanate 584-84-9 HE(6) ND ND ND X o-Toluidine 95-53-4 X ND ND ND X Toxaphene 8001-35-2 X X X X X 1,2,4-Trichlorobenzene 120-82-1 X X X X X 95-95-4 X X ND X X 2,4,5-Trichlorophenol 88-06-2 X X X X X 2,4,6-Trichlorophenol Trifluralin 1582-09-8 X ND ND ND X 137-17-7 X ND ND ND X 2,4,5-Trimethylaniline Trimethyl phosphate 512-56-1 HE(60) ND ND ND X 1,3,5-Trinitrobenzene 99-35-4 X ND ND ND X Tris(2,3-dibromopropyl) 126-72-7 X ND ND ND LR phosphate

CD-ROM 8270D - 7 Revision 4 January 1998Appropriate Preparation Techniques b

Compounds CAS No a 3510 352 0 3540/ 3541 355 0 3580

Tri-p-tolyl phosphate O,O,O-Triethyl phosphorothioate 78-32-0 126-68-1 X X ND ND ND ND ND ND X X

a Chemical Abstract Service Registry Number
b See Sec. 1.2 for other acceptable preparation methods.

KEY TO ANALYTE LIST

AW = Adsorption to walls of glassware during extraction and storage. CP = Nonreproducible chromatographic performance. DC = Unfavorable distribution coefficient (number in parenthesis is percent recovery). HE = Hydrolysis during extraction accelerated by acidic or basic conditions (number in parenthesis is percent recovery). HS = Hydrolysis during storage (number in parenthesis is percent stability). LR = Low response. ND = Not determined. OE = Oxidation during extraction accelerated by basic conditions (number in parenthesis is percent recovery). OS = Oxidation during storage (number in parenthesis is percent stability).

X = Greater than 70 percent recovery by this technique.

1.2 In addition to the sample preparation methods listed in the above analyte list, Method 3535 describes a solid-phase extraction procedure that may be applied to the extraction of semivolatiles from TCLP leachates (Tables 16 and 17 contain performance data). Method 3542 describes sample preparation for semivolatile organic compounds in air sampled by Method 0010 (Table 11 contains surrogate performance data), Method 3545 describes an automated solvent extraction device for semivolatiles in solids (Table 12 contains performance data), and Method 3561 describes a supercritical fluid device for the extraction of PAHs from solids (see Tables 13, 14, and 15 for performance data).

1.3 Method 8270 can be used to quantitate most neutral, acidic, and basic organic compounds that are soluble in methylene chloride and capable of being eluted, without derivatization, as sharp peaks from a gas chromatographic fused-silica capillary column coated with a slightly polar silicone. Such compounds incl ude polynuclear aromatic hydrocarbons, chlorinated hydrocarbons and pesticides, phthalate esters, organophosphate esters, nitrosamines, haloethers, aldehydes, ethers, ketones, anili nes, pyridines, quinolines, arom atic nitro compounds, and phenols, including nitrophenols. See Table 1 for a list of compounds and their characteristic ions that have been evaluated.
In most cases, Method 8270 is not appropriate for the quantitation of multicomponent analytes, e.g., Aroclors, Toxaphene, Chlordane, etc., because of limited sensitivity for those analytes. When these analytes have been identified by another technique, Method 8270 may be appropriate for confirmation of the identification of these analytes when concentration in the extract

CD-ROM 8270D - 8 Revision 4 January 1998permits. Refer to Sec. 7.0 of Methods 8081 and 8082 for guidance on calibration and quantitation of multicomponent analytes such as the Aroclors, Toxaphene, and Chlordane.

1.4 The following compounds may require special treatment when being determined by this method:

1.4.1 Benzidine may be subject to oxidative losses during solvent concentration and its chromatographic behavior is poor.

1.4.2 Under the alkaline conditions of the extraction step from aqueous matrices,
α -BHC, γ -BHC, Endosulfan I and II, and Endrin are subject to decomposition. Neutral extraction should be performed if these compounds are expected.

1.4.3 Hexachlorocyclopentadiene is subject to thermal decomposition in the inlet of the gas chromatograph, chemical reaction in acetone solution, and photochemical decomposition.

1.4.4 N-nitrosodimethylamine is difficult to separate from the solvent under the chromatographic conditions described.

1.4.5 N-nitrosodiphenylamine decomposes in the gas chromatographic inlet and cannot be separated from diphenylamine.

1.4.6 Pentachlorophenol, 2,4-dinitrophenol, 4-nitrophenol, benzoic acid, 4,6-dinitro-2-methylphenol, 4-chloro-3-m ethylphenol, 2-nitroaniline, 3-nitroaniline, 4-chloroaniline, and benzyl alcohol are subject to erratic chro matographic behavior, especially if the GC system is contaminated with high boiling material.

1.4.7 Pyridine may perform poorly at the GC injection port temperatures listed in the method. Lowering the injection port temperature may reduce the amount of degradation. However, the analyst must use caution in modifying the injection port temperature, as the performance of other analytes may be adversely affected. Therefore, if pyridine is to be determined in addition to other target analytes, it may be necessary to perform separate analyses. In addition, pyridine may be lost during the evaporative concentration of the sample extract. As a result, many of the extraction methods listed above may yield low recoveries unless great care is exercised during the concentration steps. For this reason, analysts may wish to consider the use of extraction techniques such as pressurized fluid extraction (Method 3545) or supercritical fluid extraction, which in volve smaller extract volumes, thereby reducing or eliminating the need for evaporative conc entration techniques for many applications.

1.4.8 Toluene diisocyanate rapidly hydrolyses in water (half-life of less then 30 min.). Therefore, recoveries of this compound from aqueous matrices should not be expected. In addition, in solid matrices, toluene diisocyanate often reacts with alcohols and amines to produce urethane and ureas and consequently cannot usually coexist in a solution containing these materials.

1.4.9 In addition, analytes in the list provided above are flagged when there are limitations caused by sample preparation and/or chromatographic problems.

1.5 The estimated quantitation limit (EQL) of Method 8270 for determining an individual compound is approxim ately 660 μg/kg (wet weight) for soil/sediment samples, 1-200 mg/kg for

CD-ROM 8270D - 9 Revision 4 January 1998wastes (dependent on matrix and method of preparation), and 10 μg/L for ground water samples (see Table 2). EQLs will be proportionately higher for sample extracts that require dilution to avoid saturation of the detector.

1.6 This method is restricted to use by or under the supervision of analysts experienced in the use of gas chromatograph/mass spectrometers and skilled in the interpretation of mass spectra. Each analyst must demonstrate the ability to generate acceptable results with this method.

2.0 SUMMARY OF METHOD

2.1 The samples are prepared for analysis by gas chromatography/mass spectrometry (GC/MS) using the appropriate sample preparation (refer to Method 3500) and, if necessary, sample cleanup procedures (refer to Method 3600).

2.2 The semivolatile compounds are introduced into the GC/MS by injecting the sample extract into a gas chromatograph (GC) with a narrow-bore fused-silica capillary column. The GC column is temperature-programmed to separate the analytes, which are then detected with a mass spectrometer (MS) connected to the gas chromatograph.

2.3 Analytes eluted from the capillary column are introduced into the mass spectrometer via a jet separator or a direct connection. Identification of target analytes is accomplished by comparing their mass spectra with the electron impact (or electron impact-like) spectra of authentic standards. Quantitation is accomplished by comparing the response of a major (quantitation) ion relative to an internal standard using a five-point calibration curve.

2.4 The method includes specific calibration and quality control steps that supersede the general requirements provided in Method 8000.

3.0 INTERFERENCES

3.1 Raw GC/MS data from all blanks, samples, and spikes must be evaluated for interferences. Determine if the source of inte rference is in the preparation and/or cleanup of the samples and take corrective action to eliminate the problem.

3.2 Contamination by carryover can occur whenever high-concentration and low-concentration samples are sequentially analyzed. To reduce carryover, the sample syringe must be rinsed with solvent between sample injections. Whenever an unusually concentratedsample is encountered, it should be followed by the analysis of solvent to check for crosscontamination.

4.0 APPARATUS AND MATERIALS

4.1 Gas chromatograph/mass spectrometer system

4.1.1 Gas chromatograph - An analytical system complete with a temperature-programmable gas chromatograph su itable for splitless injection and all required accessories, including syringes, analytical columns, and gases. The capillary column should be directly coupled to the source.

CD-ROM 8270D - 10 Revision 4 January 19984.1.2 Column - 30-m x 0.25-mm ID (or 0.32-mm ID) 1-μm film thickness silicone-coated fused-silica capillary column (J&W Scientific DB-5 or equivalent).

4.1.3 Mass spectrometer

4.1.3.1 Capable of scanning from 35 to 500 amu every 1 sec or less, using 70 volts (nominal) electron energy in the electron impact ionization mode. The mass spectrometer must be capable of producing a mass spectrum for decafluorotriphenylphosphine (DFTPP) which meets the criteria in Table 3 when 1 μL of the GC/MS tuning standard is injected through the GC (50 ng of DFTPP).

4.1.3.2 An ion trap mass spectrometer may be used if it is capable of axial modulation to reduce ion-molecule reactions and can produce electron impact-like spectra that match those in t he EPA/NIST Library. The mass spectrometer must be capable of producing a mass spectrum for DFTPP which meets the criteria in Table 3 when 5 or 50 ng are introduced.

4.1.4 GC/MS interface - Any GC-to-MS interface may be used that gives acceptable calibration points at 50 ng per injection for each compound of interest and achieves acceptable tuning performance criteria. For a narrow-bore capillary column, the interface is usually capillary-direct into the mass spectrometer source.

4.1.5 Data system - A computer system should be interfaced to the mass spectrometer. The system must allow the continuous acquisition and storage on machine-readable media of all mass spectra obtained throughout the duration of the chromatographic program. The computer should have software that can search any GC/MS data file for ions of a specific mass and that can plot such ion abundances versus time or scan number. This type of plot is defined as an Extracted Ion Current Profile (EICP). Software should also be available that allows integrating the abundances in any EICP between specified time or scan-number limits. The most recent version of the EPA/NIST Mass Spectral Library should also be available.

4.1.6 Guard column (optional) - (J&W deactivated fused-silica, 0.25-mm ID x 6-m, or equivalent) between the injection port and the analytical column joined with column joiners (Hewlett-Packard Catalog No. 5062-3556, or equivalent).

4.2 Syringe - 10-μL.

4.3 Volumetric flasks, Class A - Appropriate sizes with ground-glass stoppers.

4.4 Balance - Analytical, capable of weighing 0.0001 g.

4.5 Bottles - glass with polytetrafluoroethylene (PTFE)-lined screw caps or crimp tops.

5.0 REAGENTS

5.1 Reagent grade inorganic chemicals shall be used in all tests. Unless otherwise indicated, it is intended that all reagents shall conform to the specifications of the Committee on Analytical Reagents of the American Chemical Soci ety, where such specifications are available.

CD-ROM 8270D - 11 Revision 4 January 1998Other grades may be used, provided it is first ascertained that the reagent is of sufficiently high purity to permit its use without lessening the accuracy of the determination.

5.2 Organic-free reagent water - All references to water in this method refer to organic-free reagent water, as defined in Chapter One.

5.3 Stock standard solutions (1000 mg/L) - Standard solutions can be prepared from pure standard materials or purchased as certified solutions.

5.3.1 Prepare stock standard solutions by accurately weighing about 0.0100 g of pure material. Dissolve the material in pesticide quality acetone or other suitable solvent and dilute to volume in a 10-mL volumetric flask. Larger volumes can be used at the convenience of the analyst. When compound purity is assayed to be 96% or greater, the weight may beused without correction to calculate the concentration of the stock standard. Commerciallyprepared stock standards may be used at any concentration if they are certified by the manufacturer or by an independent source.

5.3.2 Transfer the stock standard solutions into bottles with PTFE-lined screw-caps. Store, protected from light, at -10 E C or less or as recommended by the standard manufacturer. Stock standard solutions should be checked frequently for signs of degradation or evaporation, especially just prio r to preparing calibration standards from them.

5.3.3 Stock standard solutions must be replaced after 1 year or sooner if comparison with quality control check samples indicates a problem.

5.3.4 It is recommended that nitrosamine compounds be placed together in a separate calibration mix and not combined with other calibration mixes. When using a premixed certified standard, consult the manufacturer's instructions for additional guidance.

5.3.5 Mixes with hydrochloride salts may contain hydrochloric acid, which can cause analytical difficulties. When using a premixed certified standard, consult the manufacturer's instructions for additional guidance.

5.4 Internal standard solutions - The internal standards recommended are 1,4-dichlorobenzene-d 4 , naphthalene-d 8 , acenaphthene-d 10 , phenanthrene-d 10 , chrysene-d 12 , and perylene-d 12 (see Table 5). Other compounds may be used as internal standards as long as the specifications in Sec. 7.3.2 are met.

5.4.1 Dissolve 0.200 g of each compound with a small volume of carbon disulfide. Transfer to a 50 mL volumetric flask and dilute to volume with methylene chloride so that the final solvent is approximately 20% carbon disulfide. Most of the compounds are also soluble in small volumes of methanol, acetone, or toluene, except for perylene-d 12 . The resulting solution will contain each standard at a concentration of 4,000 ng/μL. Each 1-mL sample extract undergoing analysis should be spiked with 10 μL of the internal standard solution, resulting in a concentration of 40 ng/μL of each internal standard. Store at -10 E C or less when not in use. When using premixed certified solutions, store according to the manufacturer's documented holding time and storage temperature recommendations.

5.4.2 If a more sensitive mass spectrometer is employed to achieve lower detection levels, a more dilute internal standard solution may be required. Area counts of the

CD-ROM 8270D - 12 Revision 4 January 1998internal standard peaks should be between 50-200% of the area of the target analytes in the mid-point calibration analysis.

5.5 GC/MS tuning standard - A methylene chloride solution containing 50 ng/μL of decafluorotriphenylphosphine (DFTPP) should be prepared. The standard should also contain 50 ng/μL each of 4,4'-DDT, pentachlorophenol, and benzidine to verify injection port inertness and GC column performance. Store at -10 E C or less when not in use. If a more sensitive mass spectrometer is employed to achieve lower detection levels, a more dilute tuning solution may be necessary. When using premixed certified solutions, store according to the manufacturer's documented holding time and storage temperature recommendations.

5.6 Calibration standards - A minimum of five calibration standards should be prepared at five different concentrations. At least one of the calibration standards should correspond to a sample concentration at or below that necessary to meet the data quality objectives of the project. The remaining standards should correspond to the range of concentrations found in actual samples but should not exceed the working range of the GC/MS system. Each standard should contain each analyte for detection by this method.

5.6.1 It is the intent of EPA that all target analytes for a particular analysis be included in the calibration standard(s). These target analytes may not include the entire list of analytes (Sec. 1.1) for which the method has been demonstrated. However, the laboratory shall not report a quantitative result for a target analyte that was not included in the calibration standard(s).

5.6.2 Each 1-mL aliquot of calibration standard should be spiked with 10 μL of the internal standard solution prior to analysis. All standards should be stored at -10 E C or less, and should be freshly prepared once a year, or sooner if check standards indicate a problem. The calibration verification standard should be prepared weekly and stored at 4 E C. When using premixed certified solutions, store according to the manufacturer's documented holding time and storage temperature recommendations.

5.7 Surrogate standards - The recommended surrogates are phenol-d 6 , 2-fluorophenol, 2,4,6-tribromophenol, nitrobenzene-d 5 , 2-fluorobiphenyl, and p-terphenyl-d 14 . See Method 3500 for instructions on preparing the surrogate solutions.

5.7.1 Surrogate standard check - Determine what the appropriate concentration should be for the blank extracts after all extraction, cleanup, and concentration steps. Inject this concentration into the GC/MS to determine recovery of surrogate standards. It is recommended that this c heck be done whenever a new surrogate spiking solution is prepared.

NOTE : Method 3561 (SFE Extraction of PAHs) recommends the use of bromobenzene and p-quaterphenyl to better cover the range of PAHs listed in the method.

5.7.2 If a more sensitive mass spectrometer is employed to achieve lower detection levels, a more dilute surrogate solution may be necessary.

5.8 Matrix spike and laboratory control standards - See Method 3500 for instructions on preparing the matrix spike standard. The same standard may be used as the laboratory control standard (LCS).

CD-ROM 8270D - 13 Revision 4 January 19985.8.1 Matrix spike check - Determine what concentration should be in the blank extracts after all extraction, cleanup, and concentration steps. Inject this concentration into the GC/MS to determine recovery. It is recommended that this check be done whenever a new matrix spiking solution is prepared.

5.8.2 If a more sensitive mass spectrometer is employed to achieve lower detection levels, a more dilute matrix and LCS spiking solution may be necessary.

5.8.3 Some projects may require the spiking of the specific compounds of interest, since the spiking compounds listed in Method 3500 would not be representative of the compounds of interest required for the project. When this occurs, the matrix and LCS spiking standards should be prepared in methanol, with each compound present at a concentration appropriate for the project.

5.9 Solvents - Acetone, hexane, methylene chloride, isooctane, carbon disulfide, toluene, and other appropriate solvents. All solvents should be pesticide quality or equivalent.

6.0 SAMPLE COLLECTION, PRESERVATION, AND HANDLING

6.1 See the introductory material to this chapter, Organic Analytes, Sec. 4.1.

6.2 Store the sample extracts at -10 E C, protected from light, in sealed vials (e.g., screwcap vials or crimp-capped vials) equipped with unpierced PTFE-lined septa.

7.0 PROCEDURE

7.1 Sample preparation

7.1.1 Samples are normally prepared by one of the following methods prior to GC/MS analysis.

Matrix Methods
Air (particulates and sorbent resin) 3542 Water (including TCLP leachates) 3510, 3520, 3535 Soil/sediment 3540, 3541, 3545, 3550, 3560, 3561 Waste 3540, 3541, 3545, 3550, 3560, 3561, 3580

7.1.2 In very limited applications, direct injection of the sample into the GC/MS system with a 10-μL syringe may be appropriate. The detection limit is very high (approximately 10,000 μg/L). Therefore, it is only permitted where concentrations in excess of 10,000 μg/L are expected.

CD-ROM 8270D - 14 Revision 4 January 19987.2 Extract cleanup - Extracts may be cleaned up by any of the following methods prior to GC/MS analysis.
Analytes of interest Methods

Aniline & aniline derivatives 3620 Phenols 3630, 3640, 8041 a Phthalate esters 3610, 3620, 3640 Nitrosamines 3610, 3620, 3640 Organochlorine pesticides & PCBs 3610, 3620, 3630, 3660, 3665 Nitroaromatics and cyclic ketones 3620, 3640 Polynuclear aromatic hydrocarbons 3611, 3630, 3640 Haloethers 3620, 3640 Chlorinated hydrocarbons 3620, 3640 Organophosphorus pesticides 3620 Petroleum waste 3611, 3650 All base, neutral, and acid

priority pollutants 3640

a Method 8041 includes a derivatization technique and a GC/ECD analysis, if interferences

are encountered on GC/FID.

7.3 Initial calibration
Establish the GC/MS operating conditions, us ing the following recommendations as guidance.
Mass range: 35-500 amu Scan time: 1 sec/scan Initial temperature: 40 E C, hold for 4 minutes Temperature program: 40-270 E C at 10 E C/min Final temperature: 270 E C, hold until benzo[g,h,i]perylene elutes Injector temperature: 250-300 E C Transfer line temperature: 250-300 E C Source temperature: According to manufacturer's specifications Injector: Grob-type, splitless Injection volume: 1-2 μL Carrier gas: Hydrogen at 50 cm/sec or helium at 30 cm/sec Ion trap only: Set axial modulation, manifold temperature, and emission current to manufacturer's recommendations
Split injection is allowed if the sensitivity of the mass spectrometer is sufficient.

7.3.1 The GC/MS system must be hardware-tuned using a 50-ng injection of DFTPP. Analyses must not begin until the tuning criteria are met.

7.3.1.1 In the absence of specific recommendations on how to acquire the mass spectrum of DFTPP from the instrument manufacturer, the following approach has been shown to be useful: Three scans (the peak apex scan and the scans immediately preceding and followi ng the apex) are acquired and averaged. Background subtraction is required, and must be accomplished using a single scan acquired no more than 20 scans prior to the elution of DFTPP. The background

CD-ROM 8270D - 15 Revision 4 January 1998subtraction should be designed only to eliminate column bleed or instrument background ions. Do not subtract part of the DFTPP peak.

7.3.1.2 Use the DFTPP mass intensity criteria in Table 3 as tuning acceptance criteria. Alternatively, other documented tuning criteria may be used (e.g. CLP, Method 525, or manufacturer's instructions), provided that method performance is not adversely affected.

NOTE: All subsequent standards, samples, MS/MSDs, and blanks associated with a DFTPP analysis must use the identical mass spectrometer instrument conditions.

7.3.1.3 The GC/MS tuning standard solution should also be used to assess GC column performance and injection port inertness. Degradation of DDT to DDE and DDD should not exceed 20%. (See Sec. 8.0 of Method 8081 for the percent breakdown calculation). Benzidine and pentachlorophenol should be present at their normal responses, and no peak tailing should be visible.

7.3.1.4 If degradation is excessive and/or poor chromatography is noted, the injection port may require cleaning. It may also be necessary to break off the first 6-12 in. of the capillary column. The use of a guard column (Sec. 4.1.6) between the injection port and the analytical column may help prolong analytical column performance.

7.3.2 The internal standards selected in Sec. 5.4 should permit most of the components of interest in a chromatogram to have retention times of 0.80-1.20 relative to one of the internal standards. Use the base peak ion from the specific internal standard as the primary ion for quantitation (see Table 1). If interferences are noted, use the next most intense ion as the quantitation ion (i.e. for 1,4-dichlorobenzene-d 4 , use 152 m/z for quantitation).

7.3.3 Analyze 1-2 μL of each calibration standard (containing internal standards) and tabulate the area of the primary characteristic ion against concentration for each target analyte (as indicated in Table 1). A set of at least five calibration standards is necessary (see Sec. 5.6 and Method 8000). The injection volume must be the same for all standards and sample extracts. Figure 1 shows a chromatogram of a calibration standard containing base/neutral and acid analytes.
Calculate response factors (RFs) for each target analyte relative to one of the internal standards as follows:

RF ' A s × C is A is × C s

where:

A s = Peak area (or height) of the analyte or surrogate.

CD-ROM 8270D - 16 Revision 4 January 1998A is = Peak area (or height) of the internal standard. C s = Concentration of the analyte or surrogate, in μg/L. C is = Concentration of the internal standard, in μg/L.

7.3.4 System performance check compounds (SPCCs)

7.3.4.1 A system performance check must be performed to ensure that minimum average RFs are met before the calibration curve is used. For semivolatiles, the System performance check compounds (SP CCs) are: N-nitroso-di-n-propylamine; hexachlorocyclopentadiene; 2,4-dinitrophenol; and 4-nitrophenol.

7.3.4.2 The minimum acceptable average RF for these compounds is 0.050. These SPCCs typically have very low RFs (0.1-0.2) and tend to decrease in response as the chromatographic system begins to deteriorate or the standard material begins to deteriorate. They are usually the first to show poor performance. Therefore, they must meet the minimum requirement when the system is calibrated.

7.3.4.3 If the minimum response factors are not met, the system must be evaluated, and corrective action must be taken before sample analysis begins. Possible problems include standard mixt ure degradation, injection port inlet contamination, contamination at the front end of the analytical column, and active sites in the column or chromatographic system. This check must be met before sample analysis begins.

7.3.5 Calibration check compounds (CCCs)

7.3.5.1 The purpose of the CCCs are to evaluate the calibration from the standpoint of the integrity of the system. High variability for these compounds may be indicative of system leaks or reactive sites on the column. Meeting the CCC criteria is not a substitute for successful calibration of the target analytes using one of the approaches described in Sec. 7.0 of Method 8000.

7.3.5.2 Calculate the mean respons e factor and the relative standard deviation (RSD) of the response factors for each target analyte. The RSD should be less than or equal to 15% for each target analyte. However, the RSD for each individual CCC (see Table 4) must be less than or equal to 30%.

n n j RF i j (RF i & RF ) 2

i ' 1 mean RF ' RF ' i ' 1 SD ' n n

& 1

SD RSD ' × 100 RF

CD-ROM 8270D - 17 Revision 4 January 19987.3.5.3 If the RSD of any CCC is greater than 30%, then the chromatographic system is too reactive for analysis to begin. Clean or replace the injector liner and/or capillary column, then repeat the calibration procedure beginning with Sec. 7.3.

7.3.5.4 If the CCCs are not included in the list of analytes for a project, and therefore not included in the calibration standards, then refer to Sec. 7.0 of Method 8000.

7.3.6 Evaluation of retention times - The relative retention time (RRT) of each target analyte in each calibration standard should agree within 0.06 RRT units. Late-eluting target analytes usually have much better agreement.

Retention time of the analyte RRT ' Retention time of the internal standard

7.3.7 Linearity of target analytes - If the RSD of any target analytes is 15% or less, then the relative response factor is assumed to be constant over the calibration range, and the average relative response factor may be used for quantitation (Sec. 7.6.2).

7.3.7.1 If the RSD of any target analyte is greater than 15%, refer to Sec. 7.0 in Method 8000 for additional calibration options. One of the options must be applied to GC/MS calibration in this situation, or a new initial calibration must be performed.

NOTE : Method 8000 designates a linearity criterion of 20% RSD. That criterion pertains to GC and HPLC methods other than GC/MS. Method 8270 requires 15% RSD as evidence of sufficient linearity to employ an average response factor.

7.3.7.2 When the RSD exceeds 15%, the plotting and visual inspection of a calibration curve can be a useful diagnostic tool. The inspection may indicate analytical problems, including errors in standard preparation, the presence of active sites in the chromatographic system, analytes that exhibit poor chromatographic behavior, etc.

7.4 GC/MS calibration verification - Calibration verification consists of three steps that are performed at the beginning of each 12-hour analytical shift.

7.4.1 Prior to the analysis of samples or calibration standards, inject 50 ng of the DFTPP standard into the GC/MS system. The resultant mass spectrum for DFTPP must meet the criteria given in Table 3 before sample analysis begins. These criteria must be demonstrated each 12-hour shift during which samples are analyzed.

7.4.2 The initial calibration (Sec. 7.3) for each compound of interest should be verified once every 12 hours prior to sample analysis, using the introduction technique and conditions used for samples. This is accomplished by analyzing a calibration standard at a concentration near the midpoint concentration for the calibrating range of the GC/MS. The

CD-ROM 8270D - 18 Revision 4 January 1998results from the calibration standard analysis should meet the verification acceptance criteria provided in Secs. 7.4.4 through 7.4.7.

NOTE : The DFTPP and calibration verification standard may be combined into a single standard as long as both tuning and calibration verification acceptance criteria for the project can be met without interferences.

7.4.3 A method blank should be analyzed either after the calibration standard, or at any other time during the analytical shift, to ensure that the total system (introduction device, transfer lines and GC/MS syst em) is free of contaminants. If the method blank indicates contamination, then it may be appropriate to analyze a solvent blank to demonstrate that the contamination is not a re sult of carryover from standards or samples. See Sec. 8.0 of Method 8000B for method blank performance criteria.

7.4.4 System performance check compounds (SPCCs)

7.4.4.1 A system performance che ck must be made during every 12-hour analytical shift. Each SPCC in the calibration verification standard must meet a minimum response factor of 0.050. This is the same check that is applied during the initial calibration.

7.4.4.2 If the minimum response factors are not met, the system must be evaluated, and corrective action must be taken before sample analysis begins. Possible problems include standard mixture degradation, injection port inlet contamination, contamination at the front end of the analytical column, and active sites in the column or chromatographic system. This check must be met before sample analysis begins.

7.4.5 Calibration check compounds (CCCs)

7.4.5.1 After the system performance check is met, the CCCs listed in Table 4 are used to check the validity of the initial calibration. Use percent difference when performing the average response factor model calibration. Use percent drift when calibrating using a regression fit model. Refer to Sec. 7.0 of Method 8000 for guidance on calculating percent difference and drift.

7.4.5.2 If the percent difference for each CCC is less than or equal to 20%, then the initial calibration is assumed to be valid. If the criterion is not met (i.e., greater than 20% difference or drift) for any one CCC, then corrective action must be taken prior to the analysis of samples. If the CCCs are not included in the list of analytes for a project, and therefore not included in the calibration standards, then all analytes must meet the 20% difference or drift criterion.

7.4.5.3 Problems similar to those listed under SPCCs could affect the CCCs. If the problem cannot be corrected by other measures, a new initial calibration must be generated. The CCC criteria must be met before sample analysis begins.

7.4.6 Internal standar d retention time - The retention times of the internal standards in the calibration verification standard must be evaluated immediately after or during data acquisition. If the retention time for any internal standard changes by more than 30 seconds from that in the mid-point standard level of the most recent initial calibration

CD-ROM 8270D - 19 Revision 4 January 1998sequence, then the chromatographic system must be inspected for malfunctions and corrections must be made, as required. When corrections are made, reanalysis of samples analyzed while the system was malfunctioning is required.

7.4.7 Internal standard response - If the EICP area for any of the internal standards in the calibration verification standard changes by a factor of two (-50% to +100%) from that in the mid-point standard level of the most recent initial calibration sequence, the mass spectrometer must be inspected for malfunctions and corrections must be made, as appropriate. When corrections are made, reanalysis of samples analyzed while the system was malfunctioning is required.

7.5 GC/MS analysis of samples

7.5.1 It is highly recommended that sample extracts be screened on a GC/FID or GC/PID using the same type of capillary column used in the GC/MS system. This will minimize contamination of the GC/MS system from unexpectedly high concentrations of organic compounds.

7.5.2 Allow the sample extract to warm to room temperature. Just prior to analysis, add 10 μL of the internal standard solution to the 1-mL concentrated sample extract obtained from sample preparation.

7.5.3 Inject a 1-2 μL aliquot of the sample extract into the GC/MS system, using the same operating conditions that were used for the calibration (Sec. 7.3). The volume to be injected should contain 100 ng of base/neutral and 200 ng of acid surrogates (assuming 100% recovery), unless a more sensitive GC/MS system is being used and the surrogate solution is less concentrated then that listed in Sec. 5.7. The injection volume must be the same volume used for the calibration standards.

7.5.4 If the response for any quantitation ion exceeds the initial calibration range of the GC/MS system, the sample extract must be diluted and reanalyzed. Additional internal standard solution must be added to the diluted extract to maintain the same concentration as in the calibration standards (40 ng/μL, unless a more sensitive GC/MS system is being used). Secondary ion quantitation should be used only when there are sample interferences with the primary ion.

NOTE: It may be a useful diagnostic tool to monitor internal standard retention times and responses (area counts) in all samples, spikes, blanks, and standards to effectively check drifting method performance, poor injection execution, and anticipate the need for system inspection and/or maintenance.

7.5.4.1 When ions from a compound in the sample saturate the detector, this analysis must be followed by the analysis of an instrument blank consisting of clean solvent. If the blank analysis is not free of interferences, then the system must be decontaminated. Sample analysis may not resume until the blank analysis is demonstrated to be free of interferences.

7.5.4.2 All dilutions should keep the response of the major constituents (previously saturated peaks) in the upper half of the linear range of the curve.

CD-ROM 8270D - 20 Revision 4 January 19987.5.5 The use of selected ion monitoring (SIM) is acceptable for applications requiring detection limits below the normal range of electron impact mass spectrometry. However, SIM may provide a lesser degree of confidence in the compound identification unless multiple ions are monitored for each compound.

7.6 Qualitative analysis

7.6.1 The qualitative identification of compounds determined by this method is based on retention time and on comparison of the sample mass spectrum, after background correction, with characteristic ions in a reference mass spectrum. The reference mass spectrum must be generated by the laboratory using the conditions of this method. The characteristic ions from the reference mass spectrum are defined as the three ions of greatest relative intensity, or any ions over 30% relative intensity, if less than three such ions occur in the reference spectrum. Compounds are identified when the following criteria are met.

7.6.1.1 The intensities of the characteristic ions of a compound must maximize in the same scan or within one scan of each other. Selection of a peak by a data system target compound search routine where the search is based on the presence of a target chromatographic peak containing ions specific for the target compound at a compound-specific retention time will be accepted as meeting this criterion.

7.6.1.2 The RRT of the sample component is within ± 0.06 RRT units of the RRT of the standard component.

7.6.1.3 The relative intensities of the characteristic ions agree within 30% of the relative intensities of these ions in the reference spectrum. (Example: For an ion with an abundance of 50% in the reference spectrum, the corresponding abundance in a sample spectrum can range between 20% and 80%.)

7.6.1.4 Structural isomers that produce very similar mass spectra should be identified as individual isomers if they hav e sufficiently different GC retention times. Sufficient GC resolution is achieved if the height of the valley between two isomer peaks is less than 25% of the sum of the two peak heights. Otherwise, structural isomers are identified as isomeric pairs. Diastereomeric pairs (e.g., Aramite and Isosafrol) that may be separable by the GC should be identified, quantitated and reported as the sum of both compounds by the GC.

7.6.1.5 Identification is hampered when sample components are not resolved chromatographically and produce mass spectra containing ions contributed by more than one analyte. When gas chromatographic peaks obviously represent more than one sample component (i.e., a broadened peak with shoulder(s) or a valley between two or more maxima), appropriate selection of analyte spectra and background spectra is important.

7.6.1.6 Examination of extracted ion current profiles of appropriate ions can aid in the selection of spectra and in qualitative identification of compounds. When analytes coelute (i.e., only one chromatographic peak is apparent), the identification criteria may be met, but each analyte spectrum will contain extraneous ions contributed by the coeluting compound.

CD-ROM 8270D - 21 Revision 4 January 19987.6.2 For samples containing components not associated with the calibration standards, a library search may be made for the purpose of tentative identification. The necessity to perform this type of identific ation will be determined by the purpose of the analyses being conducted. Data system library search routines should not use normalization routines that would misrepresent the library or unknown spectra when compared to each other.
For example, the RCRA permit or waste delisting requirements may require the reporting of non-target analytes. Only after visual comparison of sample spectra with the nearest library searches may the analyst assign a tentative identification. Guidelines for tentative identification are:
(1) Relative intensities of major ions in the reference spectrum (ions > 10% of the most abundant ion) should be present in the sample spectrum.
(2) The relative intensities of the major ions should agree within ± 20%. (Example: For an ion with an abundance of 50% in the standard spectrum, the corresponding sample ion abundance must be between 30 and 70%.)
(3) Molecular ions present in the reference spectrum should be present in the sample spectrum.
(4) Ions present in the sample spectrum but not in the reference spectrum should be reviewed for possible background contamination or presence of coeluting compounds.
(5) Ions present in the reference spectrum but not in the sample spectrum should be reviewed for possible subtraction from the sample spectrum because of background contamination or coeluting peaks. Data system library reduction programs can sometimes create these discrepancies.

7.7 Quantitative analysis

7.7.1 Once a compound has been identified, the quantitation of that compound will be based on the integrated abundance of the primary characteristic ion from the EICP.

7.7.2 If the RSD of a co mpound's res ponse factor is 15% or less, then the concentration in the extract may be determined using the average response factor ( & F) from R & initial calibration data (Sec. 7.3.5). See Method 8000, Sec. 7.0, for the equations describing internal standard calibration and either linear or non-linear calibrations.

7.7.3 Where applicable, the concentration of any non-target analytes identified in the sample (Sec. 7.6.2) should be estimated. The same formulae should be used with the following modifications: The areas A x and A is should be from the total ion chromatograms, and the RF for the compound should be assumed to be 1.

7.7.4 The resulting concentration should be reported indicating: (1) that the value is an estimate, and (2) which internal standard was used to determine concentration. Use the nearest internal standard free of interferences.

CD-ROM 8270D - 22 Revision 4 January 19987.7.5 Quantitation of multicomponent compounds (e.g., Toxaphene, Aroclors, etc.) is beyond the scope of Method 8270. Normally, quantitation is performed using a GC/ECD, by Methods 8081 or 8082. However, Method 8270 may be used to confirm the identification of these compounds, when the concentrations are at least 10 ng/μL in the concentrated sample extract.

7.7.6 Structural isomers that produce very similar mass spectra should be quantitated as individual isomers if they have sufficiently different GC retention times. Sufficient GC resolution is achieved if the height of the valley between two isomer peaks is less than 25% of the sum of the two peak hei ghts. Otherwise, structural isomers are quantitated as isomeric pairs. Diastereomeric pairs (e.g., Aramite and Isosafrol) that may be separable by the GC should be summed and reported as the sum of both compounds.

8.0 QUALITY CONTROL

8.1 Refer to Chapter One and Method 8000 for specific quality control (QC) procedures. Quality control procedures to ensure the proper operation of the various sample preparation and/or sample introduction techniques can be found in Method 3500. Each laboratory should maintain a formal quality assurance program. The laboratory should also maintain records to document the quality of the data generated.

8.2 Quality control procedures necessary to evaluate the GC system operation are found in Sec. 7.0 of Method 8000 and include calibration verification and chromatographic analysis of samples. In addition, instrument QC requirements may be found in the following sections of Method 8270:

8.2.1 The GC/MS system must be tuned to meet the DFTPP criteria discussed in Secs. 7.3.1 and 7.4.1.

8.2.2 There must be an initial calibration of the GC/MS system as described in Sec. 7.3.

8.2.3 The GC/MS system must meet the calibration verification acceptance criteria in Sec. 7.4, each 12 hours.

8.2.4 The RRT of the sample component must fall within the RRT window of the standard component provided in Sec. 7.6.1.

8.3 Initial demonstration of proficiency - Each laboratory must demonstrate initial proficiency with each sample preparation and determinative method combination it utilizes, by generating data of acceptable accuracy and precision for target analytes in a clean matrix. The laboratory must also repeat the following operations whenever new staff are trained or significant changes in instrumentation are made. See Method 8000, Sec. 8.0 for information on how to accomplish this demonstration.

8.4 Sample quality control for preparation and analysis - The laboratory must also have procedures for documenting the effect of the matrix on method performance (precision, accuracy, and detection limit). At a minimum, this includes the analysis of QC samples including a method blank, matrix spike, a duplicate, and a laboratory control sample (LCS) in each analytical batch and the addition of surrogates to each field sample and QC sample.

CD-ROM 8270D - 23 Revision 4 January 19988.4.1 Before processing any samples, t he analyst should demonstrate, through the analysis of a method blank, that interferences from the analytical system, glassware, and reagents are under control. Each time a set of samples is analyzed or there is a change in reagents, a method blank should be analyzed as a safeguard against chronic laboratory contamination. The blanks should be carried through all stages of sample preparation and measurement.

8.4.2 Documenting the effect of the matrix should include the analysis of at least one matrix spike and one duplicate unspiked sample or one matrix spike/matrix spike duplicate pair. The decision on whether to prepare and analyze duplicate samples or a matrix spike/matrix spike duplicate must be based on a knowledge of the samples in the sample batch. If samples are expected to contain target analytes, then laboratories may use one matrix spike and a duplicate analysis of an unspiked field sample. If samples are not expected to contain target analytes, laboratories should use a matrix spike and matrix spike duplicate pair.

8.4.3 A laboratory control sample (LCS) should be included with each analytical batch. The LCS consists of an aliquot of a clean (control) matrix similar to the sample matrix and of the same weight or volume. The LCS is spiked with the same analytes at the same concentrations as the matrix spike. When the results of the matrix spike analysis indicate a potential problem due to the sample matrix itself, the LCS results are used to verify that the laboratory can perform the analysis in a clean matrix.

8.4.4 See Method 8000, Sec. 8.0 for the details on carrying out sample quality control procedures for preparation and analysis.

8.5 Surrogate recoveries - The laboratory must evaluate surrogate recovery data from individual samples versus the surrogate control limits developed by the laboratory. See Method 8000, Sec. 8.0 for information on evaluating surrogate data and developing and updating surrogate limits.

8.6 The experience of the analyst performing GC /MS analyses is invaluable to the success of the methods. Each day that analysis is performed, the calibration verification standard should be evaluated to determine if the chromatographic system is operating properly. Questions that should be asked are: Do the peaks look normal? Is the response obtained comparable to the response from previous calibrations? Careful examination of the standard chromatogram can indicate whether the column is still performing acceptably, the injector is leaking, the injector septum needs replacing, etc. If any changes ar e made to the system (e.g., the column changed, a septum is changed), see the guidance in Sec 8.2 of Method 8000 regarding whether recalibration of the system must take place.

8.7 It is recommended that the laboratory adopt additional quality assurance practices for use with this method. The specific practices that are most productive depend upon the needs of the laboratory and the nature of the samples. Whenever possible, the laboratory should analyze standard reference materials and participate in relevant performance evaluation studies.

9.0 METHOD PERFORMANCE

9.1 Method 8250 (the packed column versi on of Method 8270) was tested by 15 laboratories using organic-free reagent water, drinking water, surface water, and industrial

CD-ROM 8270D - 24 Revision 4 January 1998wastewaters spiked at six concentrations ranging from 5 to 1,300 μg/L. Single operator accuracy and precision, and method accuracy were found to be directly related to the concentration of the analyte and essentially independent of the sample matrix. Linear equations to describe these relationships are presented in Table 7. These values are presented as guidance only and are not intended as absolute acceptance criteria. Laboratories should generate their own acceptance criteria for capillary column method performance . (See Method 8000.)

9.2 Chromatograms from calibration standards analyzed with Day 0 and Day 7 samples were compared to detect possible deterioration of GC performance. These recoveries (using Method 3510 extraction) are presented in Table 8.

9.3 Method performance data using Method 3541 (automated Soxhlet extraction) are presented in Table 9. Single laboratory accuracy and precision data were obtained for semivolatile organics in a clay soil by spiking at a concentration of 6 mg/kg for each compound. The spiking solution was mixed into the soil during addition and then allowed to equilibrate for approximately 1 hour prior to extraction. The spiked samples were then extracted by Method 3541 (Automated Soxhlet). Three extractions were performed and each extract was analyzed by gas chromatography/mass spectrometry following Method 8270. The low recovery of the more volatile compounds is probably due to volatilization losses during equilibration. These data are listed in Table 10 and were taken from Reference 7.

9.4 Surrogate precision and accuracy data are presented in Table 11 from a field dynamic spiking study based on air sampling by Method 0010. The trapping media were prepared for analysis by Method 3542 and subsequently analyzed by Method 8270.

9.5 Single laboratory precision and bias data using Method 3545 (pressurized fluid extraction) for semivolatile organic compounds are presented in Table 12. The samples were conditioned spiked samples prepared and certified by a commercial supplier that contained 57 semivolatile organics at three concentrations (250, 2500, and 12,500 μg/kg) on three types of soil (clay, loam and sand). Spiked samples were ex tracted both by the Dionex Accelerated Solvent Extraction system and by the Perstorp Environm ental SoxtecTM (automated Soxhlet). The data in Table 12 represent seven replicate extractions and analyses for each individual sample and were taken from reference 9. The average recoveries from the three matrices for all analytes and all replicates relative to the automated Soxhlet data are as follows: clay 96.8%, loam 98.7% and sand 102.1%. The average recoveries from the three concentrations also relative to the automated Soxhlet data are as follows: low-101.2%, mid-97.2% and high-99.2%.

9.6 Single laboratory precision and bias data using Method 3561 (SFE extraction of PAHs with a variable restrictor and solid trapping material) were obtained for the method analytes by the extraction of two certified reference materials ( EC-1, a lake sediment from Environment Canada and HS-3, a marine sediment from the National Science and Engineering Research Council of Canada, both naturally-contaminated with PAHs). The SFE instrument used for these extractions was a Hewlett-Packard Model 7680. Analysis was by GC/MS. Average recoveries from six replicate extractions range from 85 to 148% (overall average of 100%) based on the certified value (or a Soxhlet value if a certified value was unavailable for a specific analyte) for the lake sediment. Average recoveries from three replicate extr actions range from 73 to 133% (overall average of 92%) based on the certified value for the marine sediment. The data are found in Tables 13 and 14 and were taken from Reference 10.

9.7 Single laboratory precision and accuracy data using Method 3561 (SFE extraction of PAHs with a fixed restrictor and liquid trapping) were obtained for twelve of the method analytes

CD-ROM 8270D - 25 Revision 4 January 1998by the extraction of a certified reference material (a soil naturally contaminated with PAHs). The SFE instrument used for these extractions was a Dionex Model 703-M. Analysis was by GC/MS. Average recoveries from four replicate extracti ons range from 60 to 122% (overall average of 89%) based on the certified value. Following are the instrument conditions that were utilized to extract a 3.4 g sample: Pressure - 300 atm; Time - 60 min.; Extraction fluid - CO 2 ; Modifier - 10% 1:1 (v/v) methanol/methylene chloride; Oven temperature - 80 E C; Restrictor temperature - 120 E C; and, Trapping fluid - chloroform (methylene chloride has also been used). The data are found in Table 15 and were taken from Reference 11.

9.8 Tables 16 and 17 contain single-laboratory precision and accuracy data for solidphase extraction of TCLP buffer solutions spiked at two levels and extracted using Method 3535.

9.9 Table 18 contains multiple-laboratory data for solid-phase extraction of spiked TCLP soil leachates extracted using Method 3535.

10.0 REFERENCES

1. Eichelberger, J.W., Harris, L.E., and Budde, W.L., "Reference Compound to Calibrate Ion Abundance Measurement in Gas Chromatography-M ass Spectrometry Systems", Analytical Chemistry, 47, 995-1000, 1975.

2. "Method Detection Limit for Methods 624 and 625", Olynyk, P., Budde, W.L., and Eichelberger, J.W., unpublished report, October 1980.

3. "Interlaboratory Method Study for EPA Method 625-Base/Neutrals, Acids, and Pesticides", Final Report for EPA Contract 68-03-3102.

4. Burke, J.A., "Gas Chromatography for Pestic ide Residue Analysis: Some Practical Aspects", Journal of the Association of Official Analytical Chemists (AOAC), 48, 1037, 1965.

5. Lucas, S.V., Kornfeld, R.A., "GC-MS Suitability Testing of RCRA Appendix VIII and Michigan List Analytes ", U.S. Environmental Protection Agency, Environmental Monitoring and Support Laboratory, Cincinnati, OH 45268, February 20, 1987, Contract No. 68-03-3224.

6. Engel, T.M., Kornfeld, R.A., Warner, J.S., and Andrews, K.D., "Screening of Semivolatile Organic Compounds for Extractability and Aqueous Stability by SW-846, Method 3510", U.S. Environmental Protection Agency, Environmental Monitoring and Support Laboratory, Cincinnati, OH 45268, June 5, 1987, Contract 68-03-3224.

7. Lopez-Avila, V. (W. Beckert, Project Officer); "Development of a Soxtec Extraction Procedure for Extraction of Organic Compounds from Soils and Sediments"; U.S. Environmental Protection Agency, Environmental Monitoring and Support Laboratory, Las Vegas, NV, October 1991; EPA 600/X-91/140.

8. Bursey, J., Merrill, R., McAllister, R., and McGaughey, J., "Laboratory Validation of VOST and SemiVOST for Halogenated Hydrocarbons from the Clean Air Act Amendments List", Vol. 1 and 2, U.S. Environmental Protection Agency, EPA 600/R-93/123a and b, (NTIS PB 93­ 227163 and 93-27171), Research Triangle Park, NC, July 1993.

CD-ROM 8270D - 26 Revision 4 January 19989. Richter, B., Ezzell, J., and Felix, D., "Single Laboratory Method Validation Report: Extraction of Target Compound List/Priority Pollutant List BNAs and Pesticides using Accelerated Solvent Extraction (ASE) with Analytical Validation by GC/MS and GC/ECD", Document 101124, Dionex Corporation, Salt Lake City, UT, June 16, 1994.

10. Lee, H.B., Peart, T.E., Hong-You, R.L., and Gere, D.R., "Supercritical Carbon Dioxide Extraction of Polycyclic Aromatic Hydrocar bons from Sediments", J. Chromatography, A 653 83-91 (1993).

11. Warner, S., "SFE Extraction of PNAs from Solid Matrices Using the Dionex 703M SFE Extractor and a Liquid Trap," EPA Region III, Central Regional Laboratory, 839 Bestgate Road, Annapolis, MD 21401, December 12, 1994.

12. Markell, C., "3M Data Submission to EPA," letter to B. Lesnik, June 27, 1995.

CD-ROM 8270D - 27 Revision 4 January 1998TABLE 1

CHARACTERISTIC IONS FOR SEMIVOLATILE COMPOUNDS

Retention Primary Secondary Ion(s) Compound Time (min) Ion 2-Picoline 3.75 a 93 66,92 Aniline 5.68 93 66,65 Phenol 5.77 94 65,66 Bis(2-chloroethyl) ether 5.82 93 63,95 2-Chlorophenol 5.97 128 64,130 1,3-Dichlorobenzene 6.27 146 148,111 1,4-Dichlorobenzene-d 4 (IS) 6.35 152 150,115 1,4-Dichlorobenzene 6.40 146 148,111 Benzyl alcohol 6.78 108 79,77 1,2-Dichlorobenzene 6.85 146 148,111 N-Nitrosomethylethylamine 6.97 88 42,43,56 Bis(2-chloroisopropyl) ether 7.22 45 77,121 Ethyl carbamate 7.27 62 44,45,74 Thiophenol (Benzenethiol) 7.42 110 66,109,84 Methyl methanesulfonate 7.48 80 79,65,95 N-Nitrosodi-n-propylamine 7.55 70 42,101,130 Hexachloroethane 7.65 117 201,199 Maleic anhydride 7.65 54 98,53,44 Nitrobenzene 7.87 77 123,65 Isophorone 8.53 82 95,138 N-Nitrosodiethylamine 8.70 102 42,57,44,56 2-Nitrophenol 8.75 139 109,65 2,4-Dimethylphenol 9.03 122 107,121 p-Benzoquinone 9.13 108 54,82,80 Bis(2-chloroethoxy)methane 9.23 93 95,123 Benzoic acid 9.38 122 105,77 2,4-Dichlorophenol 9.48 162 164,98 Trimethyl phosphate 9.53 110 79,95,109,140 Ethyl methanesulfonate 9.62 79 109,97,45,65 1,2,4-Trichlorobenzene 9.67 180 182,145 Naphthalene-d 8 (IS) 9.75 136 68 Naphthalene 9.82 128 129,127 Hexachlorobutadiene 10.43 225 223,227 Tetraethyl pyrophosphate 11.07 99 155,127,81,109 Diethyl sulfate 11.37 139 45,59,99,111,125 4-Chloro-3-methylphenol 11.68 107 144,142 2-Methylnaphthalene 11.87 142 141 2-Methylphenol 12.40 107 108,77,79,90 Hexachloropropene 12.45 213 211,215,117,106,141 Hexachlorocyclopentadiene 12.60 237 235,272 N-Nitrosopyrrolidine 12.65 100 41,42,68,69

CD-ROM 8270D - 28 Revision 4 January 1998TABLE 1 (continued)

Retention Primary Secondary Ion(s) Compound Time (min) Ion Acetophenone 12.67 105 71,51,120 4-Methylphenol 12.82 107 108,77,79,90 2,4,6-Trichlorophenol 12.85 196 198,200 o-Toluidine 12.87 106 107,77,51,79 3-Methylphenol 12.93 107 108,77,79,90 2-Chloronaphthalene 13.30 162 127,164 N-Nitrosopiperidine 13.55 114 42,55,56,41 1,4-Phenylenediamine 13.62 108 80,53,54,52 1-Chloronaphthalene 13.65 a 162 127,164 2-Nitroaniline 13.75 65 92,138 5-Chloro-2-methylaniline 14.28 106 141,140,77,89 Dimethyl phthalate 14.48 163 194,164 Acenaphthylene 14.57 152 151,153 2,6-Dinitrotoluene 14.62 165 63,89 Phthalic anhydride 14.62 104 76,50,148 o-Anisidine 15.00 108 80,123,52 3-Nitroaniline 15.02 138 108,92 Acenaphthene-d 10 (IS) 15.05 164 162,160 Acenaphthene 15.13 154 153,152 2,4-Dinitrophenol 15.35 184 63,154 2,6-Dinitrophenol 15.47 162 164,126,98,63 4-Chloroaniline 15.50 127 129,65,92 Isosafrole 15.60 162 131,104,77,51 Dibenzofuran 15.63 168 139 2,4-Diaminotoluene 15.78 121 122,94,77,104 2,4-Dinitrotoluene 15.80 165 63,89 4-Nitrophenol 15.80 139 109,65 2-Naphthylamine 16.00 a 143 115,116 1,4-Naphthoquinone 16.23 158 104,102,76,50,130 p-Cresidine 16.45 122 94,137,77,93 Dichlorovos 16.48 109 185,79,145 Diethyl phthalate 16.70 149 177,150 Fluorene 16.70 166 165,167 2,4,5-Trimethylaniline 16.70 120 135,134,91,77 N-Nitrosodi-n-butylamine 16.73 84 57,41,116,158 4-Chlorophenyl phenyl ether 16.78 204 206,141 Hydroquinone 16.93 110 81,53,55 4,6-Dinitro-2-methylphenol 17.05 198 51,105 Resorcinol 17.13 110 81,82,53,69 N-Nitrosodiphenylamine 17.17 169 168,167 Safrole 17.23 162 104,77,103,135 Hexamethyl phosphoramide 17.33 135 44,179,92,42

CD-ROM 8270D - 29 Revision 4 January 1998TABLE 1 (continued)

Retention Primary Secondary Ion(s) Compound Time (min) Ion 3-(Chloromethyl)pyridine hydrochloride 17.50 92 127,129,65,39 Diphenylamine 17.54 a 169 168,167 1,2,4,5-Tetrachlorobenzene 17.97 216 214,179,108,143,218 1-Naphthylamine 18.20 143 115,89,63 1-Acetyl-2-thiourea 18.22 118 43,42,76 4-Bromophenyl phenyl ether 18.27 248 250,141 Toluene diisocyanate 18.42 174 145,173,146,132,91 2,4,5-Trichlorophenol 18.47 196 198,97,132,99 Hexachlorobenzene 18.65 284 142,249 Nicotine 18.70 84 133,161,162 Pentachlorophenol 19.25 266 264,268 5-Nitro-o-toluidine 19.27 152 77,79,106,94 Thionazine 19.35 107 96,97,143,79,68 4-Nitroaniline 19.37 138 65,108,92,80,39 Phenanthrene-d 10 (IS) 19.55 188 94,80 Phenanthrene 19.62 178 179,176 Anthracene 19.77 178 176,179 1,4-Dinitrobenzene 19.83 168 75,50,76,92,122 Mevinphos 19.90 127 192,109,67,164 Naled 20.03 109 145,147,301,79,189 1,3-Dinitrobenzene 20.18 168 76,50,75,92,122 Diallate (cis or trans) 20.57 86 234,43,70 1,2-Dinitrobenzene 20.58 168 50,63,74 Diallate (trans or cis) 20.78 86 234,43,70 Pentachlorobenzene 21.35 250 252,108,248,215,254 5-Nitro-o-anisidine 21.50 168 79,52,138,153,77 Pentachloronitrobenzene 21.72 237 142,214,249,295,265 4-Nitroquinoline-1-oxide 21.73 174 101,128,75,116 Di-n-butyl phthalate 21.78 149 150,104 2,3,4,6-Tetrachlorophenol 21.88 232 131,230,166,234,168 Dihydrosaffrole 22.42 135 64,77 Demeton-O 22.72 88 89,60,61,115,171 Fluoranthene 23.33 202 101,203 1,3,5-Trinitrobenzene 23.68 75 74,213,120,91,63 Dicrotophos 23.82 127 67,72,109,193,237 Benzidine 23.87 184 92,185 Trifluralin 23.88 306 43,264,41,290 Bromoxynil 23.90 277 279,88,275,168 Pyrene 24.02 202 200,203 Monocrotophos 24.08 127 192,67,97,109 Phorate 24.10 75 121,97,93,260 Sulfallate 24.23 188 88,72,60,44

CD-ROM 8270D - 30 Revision 4 January 1998TABLE 1 (continued)

Compound Retention Time (min) Primary Ion Secondary Ion(s)

Demeton-S 24.30 88 60,81,89,114,115 Phenacetin 24.33 108 180,179,109,137,80 Dimethoate 24.70 87 93,125,143,229 Phenobarbital 24.70 204 117,232,146,161 Carbofuran 24.90 164 149,131,122 Octamethyl pyrophosphoramide 24.95 135 44,199,286,153,243 4-Aminobiphenyl 25.08 169 168,170,115 Dioxathion 25.25 97 125,270,153 Terbufos 25.35 231 57,97,153,103
α , α -Dimethylphenylamine 25.43 58 91,65,134,42 Pronamide 25.48 173 175,145,109,147 Aminoazobenzene 25.72 197 92,120,65,77 Dichlone 25.77 191 163,226,228,135,193 Dinoseb 25.83 211 163,147,117,240 Disulfoton 25.83 88 97,89,142,186 Fluchloralin 25.88 306 63,326,328,264,65 Mexacarbate 26.02 165 150,134,164,222 4,4'-Oxydianiline 26.08 200 108,171,80,65 Butyl benzyl phthalate 26.43 149 91,206 4-Nitrobiphenyl 26.55 199 152,141,169,151 Phosphamidon 26.85 127 264,72,109,138 2-Cyclohexyl-4,6-Dinitrophenol 26.87 231 185,41,193,266 Methyl parathion 27.03 109 125,263,79,93 Carbaryl 27.17 144 115,116,201 Dimethylaminoazobenzene 27.50 225 120,77,105,148,42 Propylthiouracil 27.68 170 142,114,83 Benz(a)anthracene 27.83 228 229,226 Chrysene-d 12 (IS) 27.88 240 120,236 3,3'-Dichlorobenzidine 27.88 252 254,126 Chrysene 27.97 228 226,229 Malathion 28.08 173 125,127,93,158 Kepone 28.18 272 274,237,178,143,270 Fenthion 28.37 278 125,109,169,153 Parathion 28.40 109 97,291,139,155 Anilazine 28.47 239 241,143,178,89 Bis(2-ethylhexyl) phthalate 28.47 149 167,279 3,3'-Dimethylbenzidine 28.55 212 106,196,180 Carbophenothion 28.58 157 97,121,342,159,199 5-Nitroacenaphthene 28.73 199 152,169,141,115 Methapyrilene 28.77 97 50,191,71 Isodrin 28.95 193 66,195,263,265,147 Captan 29.47 79 149,77,119,117

CD-ROM 8270D - 31 Revision 4 January 1998TABLE 1 (continued)

Retention Primary Secondary Ion(s) Compound Time (min) Ion Chlorfenvinphos 29.53 267 269,323,325,295 Crotoxyphos 29.73 127 105,193,166 Phosmet 30.03 160 77,93,317,76 EPN 30.11 157 169,185,141,323 Tetrachlorvinphos 30.27 329 109,331,79,333 Di-n-octyl phthalate 30.48 149 167,43 2-Aminoanthraquinone 30.63 223 167,195 Barban 30.83 222 51,87,224,257,153 Aramite 30.92 185 191,319,334,197,321 Benzo(b)fluoranthene 31.45 252 253,125 Nitrofen 31.48 283 285,202,139,253 Benzo(k)fluoranthene 31.55 252 253,125 Chlorobenzilate 31.77 251 139,253,111,141 Fensulfothion 31.87 293 97,308,125,292 Ethion 32.08 231 97,153,125,121 Diethylstilbestrol 32.15 268 145,107,239,121,159 Famphur 32.67 218 125,93,109,217 Tri-p-tolyl phosphate b 32.75 368 367,107,165,198 Benzo(a)pyrene 32.80 252 253,125 Perylene-d 12 (IS) 33.05 264 260,265 7,12-Dimethylbenz(a)anthracene 33.25 256 241,239,120 5,5-Diphenylhydantoin 33.40 180 104,252,223,209 Captafol 33.47 79 77,80,107 Dinocap 33.47 69 41,39 Methoxychlor 33.55 227 228,152,114,274,212 2-Acetylaminofluorene 33.58 181 180,223,152 4,4'-Methylenebis(2-chloroaniline) 34.38 231 266,268,140,195 3,3'-Dimethoxybenzidine 34.47 244 201,229 3-Methylcholanthrene 35.07 268 252,253,126,134,113 Phosalone 35.23 182 184,367,121,379 Azinphos-methyl 35.25 160 132,93,104,105 Leptophos 35.28 171 377,375,77,155,379 Mirex 35.43 272 237,274,270,239,235 Tris(2,3-dibromopropyl) phosphate 35.68 201 137,119,217,219,199 Dibenz(a,j)acridine 36.40 279 280,277,250 Mestranol 36.48 277 310,174,147,242 Coumaphos 37.08 362 226,210,364,97,109 Indeno(1,2,3-cd)pyrene 39.52 276 138,227 Dibenz(a,h)anthracene 39.82 278 139,279 Benzo(g,h,i)perylene 41.43 276 138,277 1,2:4,5-Dibenzopyrene 41.60 302 151,150,300 Strychnine 45.15 334 334,335,333

CD-ROM 8270D - 32 Revision 4 January 1998TABLE 1 (continued)

Retention Primary Secondary Ion(s) Compound Time (min) Ion Piperonyl sulfoxide 46.43 162 135,105,77 Hexachlorophene 47.98 196 198,209,211,406,408 Aldrin

-- 66 263,220 Aroclor 1016

-- 222 260,292 Aroclor 1221

-- 190 224,260 Aroclor 1232

-- 190 224,260 Aroclor 1242

-- 222 256,292 Aroclor 1248

-- 292 362,326 Aroclor 1254

-- 292 362,326 Aroclor 1260

-- 360 362,394
α -BHC

-- 183 181,109 β -BHC

-- 181 183,109 δ -BHC

-- 183 181,109 γ -BHC (Lindane)

-- 183 181,109 4,4'-DDD

-- 235 237,165 4,4'-DDE

-- 246 248,176 4,4'-DDT

-- 235 237,165 Dieldrin

-- 79 263,279 1,2-Diphenylhydrazine

-- 77 105,182 Endosulfan I

-- 195 339,341 Endosulfan II

-- 337 339,341 Endosulfan sulfate

-- 272 387,422 Endrin

-- 263 82,81 Endrin aldehyde

-- 67 345,250 Endrin ketone

-- 317 67,319 2-Fluorobiphenyl (surr)

-- 172 171 2-Fluorophenol (surr)

-- 112 64 Heptachlor

-- 100 272,274 Heptachlor epoxide

-- 353 355,351 Nitrobenzene-d 5 (surr)

-- 82 128,54 N-Nitrosodimethylamine

-- 42 74,44 Phenol-d 6 (surr)

-- 99 42,71 Terphenyl-d 14 (surr)

-- 244 122,212 2,4,6-Tribromophenol (surr)

-- 330 332,141 Toxaphene

-- 159 231,233

IS = internal standard surr = surrogate

a Estimated retention times
b Substitute for the non-specific mixture, tricresyl phosphate

CD-ROM 8270D - 33 Revision 4 January 1998TABLE 2
ESTIMATED QUANTITATION LIMITS (EQLs) FOR SEMIVOLATILE ORGANICS

Estimated Quantitation Limits a

Compound Ground water (μg/L) Low Soil/Sediment b (μg/kg) Acenaphthene 10 660 Acenaphthylene 10 660 Acetophenone 10 ND 2-Acetylaminofluorene 20 ND 1-Acetyl-2-thiourea 1000 ND 2-Aminoanthraquinone 20 ND Aminoazobenzene 10 ND 4-Aminobiphenyl 20 ND Anilazine 100 ND o-Anisidine 10 ND Anthracene 10 660 Aramite 20 ND Azinphos-methyl 100 ND Barban 200 ND Benz(a)anthracene 10 660 Benzo(b)fluoranthene 10 660 Benzo(k)fluoranthene 10 660 Benzoic acid 50 3300 Benzo(g,h,i)perylene 10 660 Benzo(a)pyrene 10 660 p-Benzoquinone 10 ND Benzyl alcohol 20 1300 Bis(2-chloroethoxy)methane 10 660 Bis(2-chloroethyl) ether 10 660 Bis(2-chloroisopropyl) ether 10 660 4-Bromophenyl phenyl ether 10 660 Bromoxynil 10 ND Butyl benzyl phthalate 10 660 Captafol 20 ND Captan 50 ND Carbaryl 10 ND Carbofuran 10 ND Carbophenothion 10 ND Chlorfenvinphos 20 ND 4-Chloroaniline 20 1300 Chlorobenzilate 10 ND

CD-ROM 8270D - 34 Revision 4 January 1998TABLE 2 (Continued)

Estimated Quantitation Limits a

Compound Ground water (μg/L) Low Soil/Sediment b (μg/kg) 5-Chloro-2-methylaniline 10 ND 4-Chloro-3-methylphenol 20 1300 3-(Chloromethyl)pyridine hydrochloride 100 ND 2-Chloronaphthalene 10 660 2-Chlorophenol 10 660 4-Chlorophenyl phenyl ether 10 660 Chrysene 10 660 Coumaphos 40 ND p-Cresidine 10 ND Crotoxyphos 20 ND 2-Cyclohexyl-4,6-dinitrophenol 100 ND Demeton-O 10 ND Demeton-S 10 ND Diallate (cis or trans) 10 ND Diallate (trans or cis) 10 ND 2,4-Diaminotoluene 20 ND Dibenz(a,j)acridine 10 ND Dibenz(a,h)anthracene 10 660 Dibenzofuran 10 660 Dibenzo(a,e)pyrene 10 ND Di-n-butyl phthalate 10 ND Dichlone NA ND 1,2-Dichlorobenzene 10 660 1,3-Dichlorobenzene 10 660 1,4-Dichlorobenzene 10 660 3,3'-Dichlorobenzidine 20 1300 2,4-Dichlorophenol 10 660 2,6-Dichlorophenol 10 ND Dichlorovos 10 ND Dicrotophos 10 ND Diethyl phthalate 10 660 Diethylstilbestrol 20 ND Diethyl sulfate 100 ND Dimethoate 20 ND 3,3'-Dimethoxybenzidine 100 ND Dimethylaminoazobenzene 10 ND 7,12-Dimethylbenz(a)anthracene 10 ND

CD-ROM 8270D - 35 Revision 4 January 1998TABLE 2 (Continued)

Estimated Quantitation Limits a

Compound Ground water (μg/L) Low Soil/Sediment b (μg/kg) 3,3'-Dimethylbenzidine 10 ND 2,4-Dimethylphenol 10 660 Dimethyl phthalate 10 660 1,2-Dinitrobenzene 40 ND 1,3-Dinitrobenzene 20 ND 1,4-Dinitrobenzene 40 ND 4,6-Dinitro-2-methylphenol 50 3300 2,4-Dinitrophenol 50 3300 2,4-Dinitrotoluene 10 660 2,6-Dinitrotoluene 10 660 Dinocap 100 ND Dinoseb 20 ND 5,5-Diphenylhydantoin 20 ND Di-n-octyl phthalate 10 660 Disulfoton 10 ND EPN 10 ND Ethion 10 ND Ethyl carbamate 50 ND Bis(2-ethylhexyl) phthalate 10 660 Ethyl methanesulfonate 20 ND Famphur 20 ND Fensulfothion 40 ND Fenthion 10 ND Fluchloralin 20 ND Fluoranthene 10 660 Fluorene 10 660 Hexachlorobenzene 10 660 Hexachlorobutadiene 10 660 Hexachlorocyclopentadiene 10 660 Hexachloroethane 10 660 Hexachlorophene 50 ND Hexachloropropene 10 ND Hexamethylphosphoramide 20 ND Indeno(1,2,3-cd)pyrene 10 660 Isodrin 20 ND Isophorone 10 660 Isosafrole 10 ND

CD-ROM 8270D - 36 Revision 4 January 1998TABLE 2 (Continued)

Estimated Quantitation Limits a

Compound Ground water (μg/L) Low Soil/Sediment b (μg/kg) Kepone 20 ND Leptophos 10 ND Malathion 50 ND Mestranol 20 ND Methapyrilene 100 ND Methoxychlor 10 ND 3-Methylcholanthrene 10 ND Methyl methanesulfonate 10 ND 2-Methylnaphthalene 10 660 Methyl parathion 10 ND 2-Methylphenol 10 660 3-Methylphenol 10 ND 4-Methylphenol 10 660 Mevinphos 10 ND Mexacarbate 20 ND Mirex 10 ND Monocrotophos 40 ND Naled 20 ND Naphthalene 10 660 1,4-Naphthoquinone 10 ND 1-Naphthylamine 10 ND 2-Naphthylamine 10 ND Nicotine 20 ND 5-Nitroacenaphthene 10 ND 2-Nitroaniline 50 3300 3-Nitroaniline 50 3300 4-Nitroaniline 20 ND 5-Nitro-o-anisidine 10 ND Nitrobenzene 10 660 4-Nitrobiphenyl 10 ND Nitrofen 20 ND 2-Nitrophenol 10 660 4-Nitrophenol 50 3300 5-Nitro-o-toluidine 10 ND 4-Nitroquinoline-1-oxide 40 ND N-Nitrosodi-n-butylamine 10 ND N-Nitrosodiethylamine 20 ND

CD-ROM 8270D - 37 Revision 4 January 1998TABLE 2 (Continued)

Estimated Quantitation Limits a

Compound Ground water (μg/L) Low Soil/Sediment b (μg/kg) N-Nitrosodiphenylamine 10 660 N-Nitroso-di-n-propylamine 10 660 N-Nitrosopiperidine 20 ND N-Nitrosopyrrolidine 40 ND Octamethyl pyrophosphoramide 200 ND 4,4'-Oxydianiline 20 ND Parathion 10 ND Pentachlorobenzene 10 ND Pentachloronitrobenzene 20 ND Pentachlorophenol 50 3300 Phenacetin 20 ND Phenanthrene 10 660 Phenobarbital 10 ND Phenol 10 660 1,4-Phenylenediamine 10 ND Phorate 10 ND Phosalone 100 ND Phosmet 40 ND Phosphamidon 100 ND Phthalic anhydride 100 ND 2-Picoline ND ND Piperonyl sulfoxide 100 ND Pronamide 10 ND Propylthiouracil 100 ND Pyrene 10 660 Resorcinol 100 ND Safrole 10 ND Strychnine 40 ND Sulfallate 10 ND Terbufos 20 ND 1,2,4,5-Tetrachlorobenzene 10 ND 2,3,4,6-Tetrachlorophenol 10 ND Tetrachlorvinphos 20 ND Tetraethyl pyrophosphate 40 ND Thionazine 20 ND Thiophenol (Benzenethiol) 20 ND o-Toluidine 10 ND

CD-ROM 8270D - 38 Revision 4 January 1998TABLE 2 (Continued)

Estimated Quantitation Limits a

Compound Ground water (μg/L) Low Soil/Sediment b (μg/kg) 1,2,4-Trichlorobenzene 10 660 2,4,5-Trichlorophenol 10 660 2,4,6-Trichlorophenol 10 660 Trifluralin 10 ND 2,4,5-Trimethylaniline 10 ND Trimethyl phosphate 10 ND 1,3,5-Trinitrobenzene 10 ND Tris(2,3-dibromopropyl) phosphate 200 ND Tri-p-tolyl phosphate(h) 10 ND

a Sample EQLs are highly matrix-dependent. The EQLs listed here are provided for guidance and

may not always be achievable.

b EQLs listed for soil/sediment are based on wet weight. Normally, data are reported on a dry

weight basis, therefore, EQLs will be higher based on the % dry weight of each sample. These EQLs are based on a 30-g sample and gel permeation chromatography cleanup.

ND = Not Determined
NA = Not Applicable

Other Matrices Factor c
High-concentration soil and sludges by ultrasonic extractor 7.5 Non-water miscible waste 75

c EQL = (EQL for Low Soil/Sediment given above in Table 2) x (Factor)

CD-ROM 8270D - 39 Revision 4 January 1998TABLE 3

DFTPP KEY IONS AND ION ABUNDANCE CRITERIA a,b

Mass Ion Abundance Criteria
51 30-60% of mass 198
68 < 2% of mass 69
70 < 2% of mass 69
127 40-60% of mass 198
197 < 1% of mass 198 198 Base peak, 100% relative abundance
199 5-9% of mass 198
275 10-30% of mass 198
365 > 1% of mass 198
441 Present but less than mass 443
442 > 40% of mass 198
443 17-23% of mass 442

a Data taken from Reference 3.
b Alternate tuning criteria may be employed, (e.g., CLP,

Method 525, or manufacturers ' instructions), provided that method performance is not adversely affected.

TABLE 4
CALIBRATION CHECK COMPOUNDS (CCC)

Base/Neutral Fraction Acid Fraction Acenaphthene 1,4-Dichlorobenzene
Hexachlorobutadiene Diphenylamine Di-n-octyl phthalate
Fluoranthene Benzo(a)pyrene 4-Chloro-3-methylphenol 2,4-Dichlorophenol 2-Nitrophenol
Phenol Pentachlorophenol 2,4,6-Trichlorophenol

CD-ROM 8270D - 40 Revision 4 January 1998TABLE 5

SEMIVOLATILE INTERNAL STANDARDS WITH CORRESPONDING ANALYTES ASSIGNED FOR QUANTITATION

1,4-Dichlorobenzene-d 4 Naphthalene-d 8 Acenaphthene-d 10 Aniline Acetophenone Acenaphthene Benzyl alcohol Benzoic acid Acenaphthylene Bis(2-chloroethyl) ether Bis(2-chloroethoxy)methane 1-Chloronaphthalene Bis(2-chloroisopropyl) ether 4-Chloroaniline 2-Chloronaphthalene 2-Chlorophenol 4-Chloro-3-methylphenol 4-Chlorophenyl phenyl ether 1,3-Dichlorobenzene 2,4-Dichlorophenol Dibenzofuran 1,4-Dichlorobenzene 2,6-Dichlorophenol Diethyl phthalate 1,2-Dichlorobenzene α , α -Dimethyl- Dimethyl phthalate Ethyl methanesulfonate phenethylamine 2,4-Dinitrophenol 2-Fluorophenol (surr) 2,4-Dimethylphenol 2,4-Dinitrotoluene
Hexachloroethane Hexachlorobutadiene 2,6-Dinitrotoluene Methyl methanesulfonate Isophorone Fluorene 2-Methylphenol 2-Methylnaphthalene 2-Fluorobiphenyl (surr) 4-Methylphenol Naphthalene Hexachlorocyclopentadiene N-Nitrosodimethylamine Nitrobenzene 1-Naphthylamine N-Nitroso-di-n-propylamine Nitrobenzene-d 8 (surr) 2-Naphthylamine
Phenol 2-Nitrophenol 2-Nitroaniline
Phenol-d 6 (surr) N-Nitrosodi-n-butylamine 3-Nitroaniline
2-Picoline N-Nitrosopiperidine 4-Nitroaniline 1,2,4-Trichlorobenzene 4-Nitrophenol
Pentachlorobenzene 1,2,4,5-Tetrachlorobenzene 2,3,4,6-Tetrachlorophenol 2,4,6-Tribromophenol (surr) 2,4,6-Trichlorophenol 2,4,5-Trichlorophenol

(surr) = surrogate

CD-ROM 8270D - 41 Revision 4 January 1998TABLE 5 (continued)

Phenanthrene-d 10 Chrysene-d 12 Perylene-d 12 4-Aminobiphenyl Benzidine Benzo(b)fluoranthene

Anthracene Benzo(a)anthracene Benzo(k)fluoranthene 4-Bromophenyl phenyl ether Bis(2-ethylhexyl) phthalate Benzo(g,h,i)perylene

Di-n-butyl phthalate Butyl benzyl phthalate Benzo(a)pyrene 4,6-Dinitro-2-methylphenol Chrysene Dibenz(a,j)acridine Diphenylamine 3,3'-Dichlorobenzidine Dibenz(a,h)anthracene

Fluoranthene p-Dimethyl aminoazobenzene

Hexachlorobenzene Pyrene N-Nitrosodiphenylamine Terphenyl-d 14 (surr) Pentachlorophenol 7,12-Dimethylbenz(a) anthracene

Pentachloronitrobenzene Di-n-octyl phthalate

Phenacetin Indeno(1,2,3-cd) pyrene

Phenanthrene 3-Methylcholanthrene

Pronamide

(surr) = surrogate

CD-ROM 8270D - 42 Revision 4 January 1998TABLE 6

MULTILABORATORY PERFORMANCE DATA a

Test conc. Limit for Range for x & Range Compound (μg/L) s (μg/L) (μg/L) p, p s (%) Acenaphthene 100 27.6 60.1-132.3 47-145 Acenaphthylene 100 40.2 53.5-126.0 33-145 Aldrin 100 39.0 7.2-152.2 D-166 Anthracene 100 32.0 43.4-118.0 27-133 Benz(a)anthracene 100 27.6 41.8-133.0 33-143 Benzo(b)fluoranthene 100 38.8 42.0-140.4 24-159 Benzo(k)fluoranthene 100 32.3 25.2-145.7 11-162 Benzo(a)pyrene 100 39.0 31.7-148.0 17-163 Benzo(g,h,i)perylene 100 58.9 D-195.0 D-219 Benzyl butyl phthalate 100 23.4 D-139.9 D-152 β -BHC 100 31.5 41.5-130.6 24-149 δ -BHC 100 21.6 D-100.0 D-110 Bis(2-chloroethyl) ether 100 55.0 42.9-126.0 12-158 Bis(2-chloroethoxy)methane 100 34.5 49.2-164.7 33-184 Bis(2-chloroisopropyl) ether 100 46.3 62.8-138.6 36-166 Bis(2-ethylhexyl) phthalate 100 41.1 28.9-136.8 8-158 4-Bromophenyl phenyl ether 100 23.0 64.9-114.4 53-127 2-Chloronaphthalene 100 13.0 64.5-113.5 60-118 4-Chlorophenyl phenyl ether 100 33.4 38.4-144.7 25-158 Chrysene 100 48.3 44.1-139.9 17-168 4,4'-DDD 100 31.0 D-134.5 D-145 4,4'-DDE 100 32.0 19.2-119.7 4-136 4,4'-DDT 100 61.6 D-170.6 D-203 Dibenzo(a,h)anthracene 100 70.0 D-199.7 D-227 Di-n-butyl phthalate 100 16.7 8.4-111.0 1-118 1,2-Dichlorobenzene 100 30.9 48.6-112.0 32-129 1,3-Dichlorobenzene 100 41.7 16.7-153.9 D-172 1,4-Dichlorobenzene 100 32.1 37.3-105.7 20-124 3,3'-Dichlorobenzidine 100 71.4 8.2-212.5 D-262 Dieldrin 100 30.7 44.3-119.3 29-136 Diethyl phthalate 100 26.5 D-100.0 D-114 Dimethyl phthalate 100 23.2 D-100.0 D-112 2,4-Dinitrotoluene 100 21.8 47.5-126.9 39-139 2,6-Dinitrotoluene 100 29.6 68.1-136.7 50-158 Di-n-octyl phthalate 100 31.4 18.6-131.8 4-146 Endosulfan sulfate 100 16.7 D-103.5 D-107 Endrin aldehyde 100 32.5 D-188.8 D-209 Fluoranthene 100 32.8 42.9-121.3 26-137

CD-ROM 8270D - 43 Revision 4 January 1998TABLE 6 (continued)

Compound Test conc. (μg/L) Limit for s (μg/L) Range for x & (μg/L) Range p, p s (%) Fluorene 100 20.7 71.6-108.4 59-121 Heptachlor 100 37.2 D-172.2 D-192 Heptachlor epoxide 100 54.7 70.9-109.4 26.155 Hexachlorobenzene 100 24.9 7.8-141.5 D-152 Hexachlorobutadiene 100 26.3 37.8-102.2 24-116 Hexachloroethane 100 24.5 55.2-100.0 40-113 Indeno(1,2,3-cd)pyrene 100 44.6 D-150.9 D-171 Isophorone 100 63.3 46.6-180.2 21-196 Naphthalene 100 30.1 35.6-119.6 21-133 Nitrobenzene 100 39.3 54.3-157.6 35-180 N-Nitrosodi-n-propylamine 100 55.4 13.6-197.9 D-230 Aroclor 1260 100 54.2 19.3-121.0 D-164 Phenanthrene 100 20.6 65.2-108.7 54-120 Pyrene 100 25.2 69.6-100.0 52-115 1,2,4-Trichlorobenzene 100 28.1 57.3-129.2 44-142 4-Chloro-3-methylphenol 100 37.2 40.8-127.9 22-147 2-Chlorophenol 100 28.7 36.2-120.4 23-134 2,4-Chlorophenol 100 26.4 52.5-121.7 39-135 2,4-Dimethylphenol 100 26.1 41.8-109.0 32-119 2,4-Dinitrophenol 100 49.8 D-172.9 D-191 2-Methyl-4,6-dinitrophenol 100 93.2 53.0-100.0 D-181 2-Nitrophenol 100 35.2 45.0-166.7 29-182 4-Nitrophenol 100 47.2 13.0-106.5 D-132 Pentachlorophenol 100 48.9 38.1-151.8 14-176 Phenol 100 22.6 16.6-100.0 5-112 2,4,6-Trichlorophenol 100 31.7 52.4-129.2 37-144

s = Standard deviation of four recovery measurements, in μg/L

& x = Average recovery for four recovery measurements, in μg/L

p, p s = Measured percent recovery
D = Detected; result must be greater than zero

a Criteria from 40 CFR Part 136 for Method 625, using a packed GC column. These criteria are

based directly on the method performance data in Table 7. Where necessary, the limits for recovery have been broadened to assure applicability of the limits to concentrations below those used to develop Table 7. These values are for guidance only. Appropriate derivation of acceptance criteria for capillary columns should result in much narrower ranges. See Method 8000 for information on developing and updating acceptance criteria for method performance.

CD-ROM 8270D - 44 Revision 4 January 1998TABLE 7

METHOD ACCURACY AND PRECISION AS FUNCTIONS OF CONCENTRATION a

Accuracy, as Single analyst Overall precision, Compound Acenaphthene Acenaphthylene Aldrin Anthracene Benz(a)anthracene Benzo(b)fluoranthene Benzo(k)fluoranthene Benzo(a)pyrene Benzo(g,h,i)perylene Benzyl butyl phthalate β -BHC δ -BHC Bis(2-chloroethyl) ether Bis(2­ recovery, x’ (μg/L) 0.96C+0.19 0.89C+0.74 0.78C+1.66 0.80C+0.68 0.88C-0.60 0.93C-1.80 0.87C-1.56 0.90C-0.13 0.98C-0.86 0.66C-1.68 0.87C-0.94 0.29C-1.09 0.86C-1.54 1.12C-5.04 precision, s r ’ (μg/L) 0.15 x & -0.12 0.24 x & -1.06 0.27 x & -1.28 0.21 x & -0.32 0.15 x & +0.93 0.22 x & +0.43 0.19 x & +1.03 0.22 x & +0.48 0.29 x & +2.40 0.18 x & +0.94 0.20 x & -0.58 0.34 x & +0.86 0.35 x & -0.99 0.16 x & +1.34 S’ (μg/L) 0.21 x & -0.67 0.26 x & -0.54 0.43 x & +1.13 0.27 x & -0.64 0.26 x & -0.21 0.29 x & +0.96 0.35 x & +0.40 0.32 x & +1.35 0.51 x & -0.44 0.53 x & +0.92 0.30 x & +1.94 0.93 x & -0.17 0.35 x & +0.10 0.26 x & +2.01 chloroethoxy)methane Bis(2-chloroisopropyl) ether Bis(2-ethylhexyl) phthalate 4-Bromophenyl phenyl 1.03C-2.31 0.84C-1.18 0.91C-1.34 0.24 x & +0.28 0.26 x & +0.73 0.13 x & +0.66 0.25 x & +1.04 0.36 x & +0.67 0.16 x & +0.66 ether 2-Chloronaphthalene 4-Chlorophenyl phenyl 0.89C+0.01 0.91C+0.53 0.07 x & +0.52 0.20 x & -0.94 0.13 x & +0.34 0.30 x & -0.46 ether Chrysene 4,4'-DDD 4,4'-DDE 4,4'-DDT Dibenzo(a,h)anthracene Di-n-butyl phthalate 1,2-Dichlorobenzene 1,3-Dichlorobenzene 1,4-Dichlorobenzene 3,3'-Dichlorobenzidine Dieldrin Diethyl phthalate Dimethyl phthalate 2,4-Dinitrotoluene 2,6-Dinitrotoluene Di-n-octyl phthalate Endosulfan sulfate Endrin aldehyde 0.93C-1.00 0.56C-0.40 0.70C-0.54 0.79C-3.28 0.88C+4.72 0.59C+0.71 0.80C+0.28 0.86C-0.70 0.73C-1.47 1.23C-12.65 0.82C-0.16 0.43C+1.00 0.20C+1.03 0.92C-4.81 1.06C-3.60 0.76C-0.79 0.39C+0.41 0.76C-3.86 0.28 x & +0.13 0.29 x & -0.32 0.26 x & -1.17 0.42 x & +0.19 0.30 x & +8.51 0.13 x & +1.16 0.20 x & +0.47 0.25 x & +0.68 0.24 x & +0.23 0.28 x & +7.33 0.20 x & -0.16 0.28 x & +1.44 0.54 x & +0.19 0.12 x & +1.06 0.14 x & +1.26 0.21 x & +1.19 0.12 x & +2.47 0.18 x & +3.91 0.33 x & -0.09 0.66 x & -0.96 0.39 x & -1.04 0.65 x & -0.58 0.59 x & +0.25 0.39 x & +0.60 0.24 x & +0.39 0.41 x & +0.11 0.29 x & +0.36 0.47 x & +3.45 0.26 x & -0.07 0.52 x & +0.22 1.05 x & -0.92 0.21 x & +1.50 0.19 x & +0.35 0.37 x & +1.19 0.63 x & -1.03 0.73 x & -0.62

CD-ROM 8270D - 45 Revision 4 January 1998TABLE 7 (Continued)

Accuracy, as Single analyst Overall precision, Compound Fluoranthene Fluorene Heptachlor Heptachlor epoxide Hexachlorobenzene Hexachlorobutadiene Hexachloroethane Indeno(1,2,3-cd)pyrene Isophorone Naphthalene Nitrobenzene N-Nitrosodi-n-propylamine Aroclor 1260 Phenanthrene Pyrene 1,2,4-Trichlorobenzene 4-Chloro-3-methylphenol 2-Chlorophenol 2,4-Dichlorophenol 2,4-Dimethylphenol 2,4-Dinitrophenol 2-Methyl-4,6-dinitrophenol 2-Nitrophenol 4-Nitrophenol Pentachlorophenol Phenol 2,4,6-Trichlorophenol recovery, x’ (μg/L) 0.81C+1.10 0.90C-0.00 0.87C-2.97 0.92C-1.87 0.74C+0.66 0.71C-1.01 0.73C-0.83 0.78C-3.10 1.12C+1.41 0.76C+1.58 1.09C-3.05 1.12C-6.22 0.81C-10.86 0.87C+0.06 0.84C-0.16 0.94C-0.79 0.84C+0.35 0.78C+0.29 0.87C-0.13 0.71C+4.41 0.81C-18.04 1.04C-28.04 0.07C-1.15 0.61C-1.22 0.93C+1.99 0.43C+1.26 0.91C-0.18 precision, s r ’ (μg/L) 0.22 x & -0.73 0.12 x & +0.26 0.24 x & -0.56 0.33 x & -0.46 0.18 x & -0.10 0.19 x & +0.92 0.17 x & +0.67 0.29 x & +1.46 0.27 x & +0.77 0.21 x & -0.41 0.19 x & +0.92 0.27 x & +0.68 0.35 x & +3.61 0.12 x & +0.57 0.16 x & +0.06 0.15 x & +0.85 0.23 x & +0.75 0.18 x & +1.46 0.15 x & +1.25 0.16 x & +1.21 0.38 x & +2.36 0.10 x & +42.29 0.16 x & +1.94 0.38 x & +2.57 0.24 x & +3.03 0.26 x & +0.73 0.16 x & +2.22 S’ (μg/L) 0.28 x & -0.60 0.13 x & +0.61 0.50 x & -0.23 0.28 x & +0.64 0.43 x & -0.52 0.26 x & +0.49 0.17 x & +0.80 0.50 x & -0.44 0.33 x & +0.26 0.30 x & -0.68 0.27 x & +0.21 0.44 x & +0.47 0.43 x & +1.82 0.15 x & +0.25 0.15 x & +0.31 0.21 x & +0.39 0.29 x & +1.31 0.28 x & +0.97 0.21 x & +1.28 0.22 x & +1.31 0.42 x & +26.29 0.26 x & +23.10 0.27 x & +2.60 0.44 x & +3.24 0.30 x & +4.33 0.35 x & +0.58 0.22 x & +1.81

x' = Expected recovery for one or more measurements of a sample containing a concentration of C, in μg/L.
s r ' = Expected single analyst standard deviation of measurements at an average concentration of x & , in μg/L. S' = Expected interlaboratory standard deviation of measurements at an average concentration found of x & , in μg/L. C = True value for the concentration, in μg/L.

& x = Average recovery found for measurements of samples containing a concentration of C, in μg/L.

a Criteria from 40 CFR Part 136 for Method 625, using a packed GC column. These criteria are based directly on the method performance data in Table 7. These values are for guidance only. Appropriate derivation of acc eptance criteria for capillary columns should result in much narrower ranges. See Method 8000 for information on developing and updating acceptance criteria for method performance.

CD-ROM 8270D - 46 Revision 4 January 1998TABLE 8

EXTRACTION EFFICIENCY AND AQUEOUS STABILITY RESULTS

Percent Recovery, Day 0 Percent Recovery, Day 7 Compound Mean RSD Mean RSD 3-Amino-9-ethylcarbazole 80 8 73 3 4-Chloro-1,2-phenylenediamine 91 1 108 4 4-Chloro-1,3-phenylenediamine 84 3 70 3 1,2-Dibromo-3-chloropropane 97 2 98 5
Dinoseb 99 3 97 6

Parathion 100 2 103 4 4,4'-Methylenebis(N,N- 108 4 90 4 dimethylaniline)

5-Nitro-o-toluidine 99 10 93 4
2-Picoline 80 4 83 4 Tetraethyl dithiopyrophosphate 92 7 70 1

Data taken from Reference 6.

CD-ROM 8270D - 47 Revision 4 January 1998TABLE 9

MEAN PERCENT RECOVERIES AND PERCENT RSD VALUES FOR SEMIVOLATILE ORGANICS FROM SPIKED CLAY SOIL AND TOPSOIL BY AUTOMATED SOXHLET EXTRACTION (METHOD 3541) WITH HEXANE-ACETONE (1:1) a

Clay Soil Topsoil

Mean RSD Mean RSD Compound Recovery Recovery 1,3-Dichlorobenzene 0

-­ 0

-­ 1,2-Dichlorobenzene 0

-­ 0

-­ Nitrobenzene 0

-­ 0

-- Benzal chloride 0

-­ 0

-- Benzotrichloride 0

-­ 0

-­ 4-Chloro-2-nitrotoluene 0

-­ 0

-- Hexachlorocyclopentadiene 4.1 15 7.8 23 2,4-Dichloronitrobenzene 35.2 7.6 21.2 15 3,4-Dichloronitrobenzene 34.9 15 20.4 11 Pentachlorobenzene 13.7 7.3 14.8 13 2,3,4,5-Tetrachloronitrobenzene 55.9 6.7 50.4 6.0 Benefin 62.6 4.8 62.7 2.9 alpha-BHC 58.2 7.3 54.8 4.8 Hexachlorobenzene 26.9 13 25.1 5.7 delta-BHC 95.8 4.6 99.2 1.3 Heptachlor 46.9 9.2 49.1 6.3 Aldrin 97.7 12 102 7.4 Isopropalin 102 4.3 105 2.3 Heptachlor epoxide 90.4 4.4 93.6 2.4 trans-Chlordane 90.1 4.5 95.0 2.3 Endosulfan I 96.3 4.4 101 2.2 Dieldrin 129 4.7 104 1.9 2,5-Dichlorophenyl-4-nitrophenyl ether 110 4.1 112 2.1 Endrin 102 4.5 106 3.7 Endosulfan II 104 4.1 105 0.4 p,p'-DDT 134 2.1 111 2.0 2,3,6-Trichlorophenyl-4'-nitrophenyl ether 110 4.8 110 2.8 2,3,4-Trichlorophenyl-4'-nitrophenyl ether 112 4.4 112 3.3 Mirex 104 5.3 108 2.2

a The operating conditions for the Soxtec apparatus were as follows: immersion time 45 min; extraction time 45 min; the sample size was 10 g; the spiking concentration was 500 ng/g, except for the surrogate compounds at 1000 ng/g, 2, 5-Dichlorophenyl-4-nitrophenyl ether, 2,3,6­ Trichlorophenyl-4-nitrophenyl ether, and 2,3,4-Tr ichlorophenyl-4-nitrophenyl ether at 1500 ng/g, Nitrobenzene at 2000 ng/g, and 1,3-Dichlorobenzene and 1,2-Dichlorobenzene at 5000 ng/g.

CD-ROM 8270D - 48 Revision 4 January 1998TABLE 10

SINGLE LABORATORY ACCURACY AND PRECISION DATA FOR THE EXTRACTION OF SEMIVOLATILE ORGANICS FROM SPIKED CLAY BY AUTOMATED SOXHLET (METHOD 3541) a

Compound Mean Recovery RSD Phenol 47.8 5.6 Bis(2-chloroethyl)ether 2-Chlorophenol Benzyl alcohol 2-Methylphenol Bis(2-chloroisopropyl)ether 4-Methylphenol N-Nitroso-di-n-propylamine Nitrobenzene 25.4 42.7 55.9 17.6 15.0 23.4 41.4 28.2 13 4.3 7.2 6.6 15

6.7 6.2 7.7 Isophorone 2-Nitrophenol 2,4-Dimethylphenol Benzoic acid 56.1 36.0 50.1 40.6 4.2 6.5 5.7 7.7 Bis(2-chloroethoxy)methane 2,4-Dichlorophenol 1,2,4-Trichlorobenzene 44.1 55.6 18.1 3.0 4.6 31 Naphthalene 4-Chloroaniline 26.2 55.7 15 12 4-Chloro-3-methylphenol 2-Methylnaphthalene Hexachlorocyclopentadiene 2,4,6-Trichlorophenol 2,4,5-Trichlorophenol 2-Chloronaphthalene 2-Nitroaniline 65.1 47.0 19.3 70.2 26.8 61.2 73.8 5.1 8.6 19

6.3 2.9 6.0 6.0 Dimethyl phthalate Acenaphthylene 3-Nitroaniline 74.6 71.6 77.6 5.2 5.7 5.3 Acenaphthene 2,4-Dinitrophenol 4-Nitrophenol Dibenzofuran 79.2 91.9 62.9 82.1 4.0 8.9 16

5.9 2,4-Dinitrotoluene 84.2 5.4 2,6-Dinitrotoluene 68.3 5.8 Diethyl phthalate 4-Chlorophenyl-phenyl ether 74.9 67.2 5.4 3.2

CD-ROM 8270D - 49 Revision 4 January 1998TABLE 10 (continued)

Compound Mean Recovery RSD Fluorene 82.1 3.4 4-Nitroaniline 79.0 7.9 4,6-Dinitro-2-methylphenol 63.4 6.8 N-Nitrosodiphenylamine 77.0 3.4 4-Bromophenyl-phenyl ether 62.4 3.0 Hexachlorobenzene 72.6 3.7 Pentachlorophenol 62.7 6.1 Phenanthrene 83.9 5.4 Anthracene 96.3 3.9 Di-n-butyl phthalate 78.3 40 Fluoranthene 87.7 6.9 Pyrene 102 0.8 Butyl benzyl phthalate 66.3 5.2 3,3'-Dichlorobenzidine 25.2 11 Benzo(a)anthracene 73.4 3.8 Bis(2-ethylhexyl) phthalate 77.2 4.8 Chrysene 76.2 4.4 Di-n-octyl phthalate 83.1 4.8 Benzo(b)fluoranthene 82.7 5.0 Benzo(k)fluoranthene 71.7 4.1 Benzo(a)pyrene 71.7 4.1 Indeno(1,2,3-cd)pyrene 72.2 4.3 Dibenzo(a,h)anthracene 66.7 6.3 Benzo(g,h,i)perylene 63.9 8.0 1,2-Dichlorobenzene 0

-­ 1,3-Dichlorobenzene 0

-­ 1,4-Dichlorobenzene 0

-­ Hexachloroethane 0

-- Hexachlorobutadiene 0

-­

a Number of determinations was three. The operating conditions for the Soxtec apparatus were as follows: immersion time 45 min; extraction time 45 min; the sample size was 10 g clay soil; the spike concentration was 6 mg/kg per compound. The sample was allowed to equilibrate 1 hour after spiking.

Data taken from Reference 7.

CD-ROM 8270D - 50 Revision 4 January 1998TABLE 11

PRECISION AND BIAS VALUES FOR METHOD 3542 1

Compound Mean Recovery Standard Deviation % RSD
2-Fluorophenol 74.6 28.6 38.3
Phenol-d 5 77.8 27.7 35.6
Nitrobenzene-d 5 65.6 32.5 49.6 2-Fluorobiphenyl 75.9 30.3 39.9 2,4,6-Tribromophenol 67.0 34.0 50.7 Terphenyl-d 14 78.6 32.4 41.3

1 The surrogate values shown in Table 11 represent mean recoveries for surrogates in all Method 0010 matrices in a field dynamic spiking study.

CD-ROM 8270D - 51 Revision 4 January 1998TABLE 12
ACCELERATED SOLVENT EXTRACTION (METHOD 3545) RECOVERY VALUES AS PERCENT OF SOXTECTM

Clay Loam Sand Mean Compound Low Mid High Low Mid High Low Mid High Rec.

Phenol 93.3 78.7 135.9 73.9 82. 8 124.6 108.8 130.6 89.7 102.0 Bis(2-chloroethyl) et her 102.1 85.1 109.1 96.0 88.0 103.6 122.3 119.9 90.8 101.9 2-Chlorophenol 100.8 82.6 115.0 93.8 88.9 111.1 115.0 115.3 91.9 101.6 1,3-Dichlorobenzene 127.7 129.7 110.0 *364.2 129.9 119. 0 *241.3 *163.7 107.1 120.6 1,4-Dichlorobenzene 127.9 127.0 110.5 *365.9 127.8 116. 4 *309.6 *164.1 105.8 119.2 1,2-Dichlorobenzene 116.8 115.8 101.3 *159.2 113.4 105. 5 *189.3 134.0 100.4 112.5 2-Methylphenol 98.9 82.1 119.7 87.6 89.4 111.0 133.2 128.0 92.1 104.7 Bis(2-chloroisopropyl)ether 109.4 71.5 108.0 81.8 81.0 88.6 118.1 148.3 94.8 100.2
o-Toluidine 100.0 89.7 117.2 100. 0 *152.5 120.3 100.0 *199.5 102.7 110.3 N-Nitroso-di-n-propylamine 103.0 79.1 107.7 83.9 88.1 96.2 109.9 123.3 91.4 98.1
Hexachloroethane 97.1 125.1 111.0 *245. 4 117.1 128.1 *566.7 147.9 103.7 118.6
Nitrobenzene 104.8 82.4 106.6 86.8 84.6 101.7 119.7 122.1 93.3 100.2 Isophorone 100.0 86.4 98.2 87.1 87.5 109.7 135.5 118.4 92.7 101.7 2,4-Dimethylphenol 100.0 104.5 140.0 100.0 114.4 123. 1 100.0 *180.6 96.3 109.8 2-Nitrophenol 80.7 80.5 107.9 91.4 86.7 103.2 122.1 107.1 87.0 96.3 Bis(chloroethoxy)methane 94.4 80.6 94.7 86.5 84.4 99.6 130. 6 110.7 93.2 97.2 2,4-Dichlorophenol 88.9 87. 8 111.4 85.9 87.6 103.5 123.3 107.0 92.1 98.6 1,2,4-Trichlorobenzene 98. 0 97.8 98.8 123.0 93.7 94. 5 137.0 99.4 95.3 104.2 Naphthalene 101.7 97.2 123.6 113.2 102.9 129.5 *174.5 114.0 89.8 106.1 4-Chloroaniline 100.0 *150.2 *162.4 100. 0 125.5 *263.6 100.0 *250.8 114.9 108.1
Hexachlorobutadiene 101.1 98.7 102.2 124.1 90.3 98.0 134. 9 96.1 96.8 104.7 4-Chloro-3-methylphenol 90.4 80.2 114.7 79.0 85.2 109.8 131. 6 116.2 90.1 99.7 2-Methylnaphthalene 93.2 89.9 94.6 104. 1 92.2 105.9 146.2 99.1 93.3 102.1 Hexachlorocyclopentadien 100.0 100.0 0.0 100.0 100.0 6.8 100.0 100.0 *238.3 75.8
e 2,4,6-Trichlorophenol 94.6 90.0 112.0 84.2 91.2 103. 6 101.6 95.9 89.8 95.9 2,4,5-Trichlorophenol 84.4 91.9 109.6 96.1 80.7 103. 6 108.9 83.9 87.9 94.1 2-Chloronaphthalene 100.0 91.3 93.6 97.6 93.4 98. 3 106.8 93.0 92.0 96.2
2-Nitroaniline 90.0 83.4 97.4 71. 3 88.4 89.9 112.1 113.3 87.7 92.6 2,6-Dinitrotoluene 83.1 90.6 91.6 86.4 90.6 90.3 104. 3 84.7 90.9 90.3 Acenaphthylene 104.9 95.9 100.5 99.0 97.9 108.8 118.5 97.8 92.0 101.7
3-Nitroaniline *224.0 115. 6 97.6 100.0 111.8 107. 8 0.0 111.7 99.0 92.9 Acenaphthene 102.1 92.6 97. 6 97.2 96.9 104.4 114. 2 92.0 89.0 98.4 4-Nitrophenol 0.0 93.2 121.5 18.1 87.1 116.6 69.1 90.5 84.5 75.6 2,4-Dinitrotoluene 73.9 91.9 100.2 84.7 93.8 98.9 100. 9 84.3 87.3 90.7

CD-ROM 8270D - 52 Revision 4 January 1998TABLE 12 (continued)

Clay Loam Sand Mean Compound Low Mid High Low Mid High Low Mid High Rec.

Dibenzofuran 89.5 91.7 109.3 98.5 92.2 111.4 113.8 92.7 90.4 98.8 4-Chlorophenyl phenyl ether 83.0 94.5 98.7 95.7 94.3 94.2 111.4 87.7 90.3 94.4

Fluorene 85.2 94.9 89.2 102.0 95. 5 93.8 121.3 85.7 90.9 95.4
4-Nitroaniline 77.8 114.8 94.5 129. 6 103.6 95.4 *154.1 89.3 87.5 99.1 N-Nitrosodiphenylamine 82.6 96.7 93.8 92.9 93.4 116.4 97. 5 110.9 86.7 96.8 4-Bromophenyl phenyl 85.6 92.9 92.8 91.1 107.6 89.4 118.0 97.5 87.1 95.8 ether
Hexachlorobenzene 95.4 91.7 92.3 95. 4 93.6 83.7 106.8 94.3 90.0 93.7 Pentachlorophenol 68.2 85. 9 107.7 53.2 89.8 88.1 96.6 59.8 81.3 81.2
Phenanthrene 92.1 93.7 93.3 100.0 97.8 113.3 124.4 101.0 89.9 100.6
Anthracene 101.6 95.0 93.5 92.5 101.8 118.4 123.0 94.5 90.6 101.2 Carbazole 94.4 99.3 96.6 105.5 96.7 111.4 115.7 83.2 88.9 99.1
Fluoranthene 109.9 101.4 94.3 111.6 96.6 109.6 123.2 85.4 92.7 102.7 Pyrene 106.5 105.8 107.6 116.7 90. 7 127.5 103.4 95.5 93.2 105.2 3,3'-Dichlorobenzidine 100.0 *492.3 131.4 100.0 *217.6 *167.6 100.0 *748.8 100.0 116.5 Benzo(a)anthracene 98.1 107.0 98.4 119.3 98.6 104. 0 105.0 93.4 89.3 101.5 Chrysene 100.0 108.5 100.2 116.8 93.0 117.0 106.7 93.6 90.2 102.9 Benzo(b)fluoranthene 106.6 109.9 75.6 121.7 100.7 93. 9 106.9 81.9 93.6 99.0 Benzo(k)fluoranthene 102.4 105.2 88.4 125.5 99.4 95. 1 144.7 89.2 78.1 103.1 Benzo(a)pyrene 107.9 105.5 80.8 122.3 97.7 104. 6 101.7 86.2 92.0 99.9 Indeno(1,2,3-cd)pyrene 95. 1 105.7 93.8 126.0 105.2 90. 4 133.6 82.6 91.9 102.7 Dibenz(a,h)anthracene 85.0 102.6 82.0 118.8 100.7 91. 9 142.3 71.0 93.1 98.6 Benzo(g,h,i)perylene 98.0 0.0 81.2 0 .0 33.6 78.6 128.7 83.0 94.2 66.4
Mean 95.1 94.3 101.0 95.5 96.5 104.1 113.0 100.9 92.5

* Values greater than 150% were not used to determine the averages, but the 0% values were used.

CD-ROM 8270D - 53 Revision 4 January 1998TABLE 13

SINGLE LABORATORY ACCURACY AND PRECISION FOR THE EXTRACTION OF PAHs FROM A CERTIFIED REFERENCE SEDIMENT EC-1, USING METHOD 3561 (SFE - SOLID TRAP)

Certified Value SFE Value a Percent of SFE

Compound (mg/kg) (mg/kg) Certified Value RSD Naphthalene (27.9) b 41.3 ± 3.6 (148) 8.7 Acenaphthylene (0.8) 0.9 ± 0.1 (112) 11.1 Acenaphthene (0.2) 0.2 ± 0.01 (100) 0.05

Fluorene (15.3) 15.6 ± 1.8 (102) 11.5

Phenanthrene 15.8 ± 1.2 16.1 ± 1.8 102 11.2

Anthracene (1.3) 1.1 ± 0.2 (88) 18.2

Fluoranthene 23.2 ± 2.0 24.1 ± 2.1 104 8.7 Pyrene 16.7 ± 2.0 17.2 ± 1.9 103 11.0 Benz(a)anthracene 8.7 ± 0.8 8.8 ± 1.0 101 11.4 Chrysene (9.2) 7.9 ± 0.9 (86) 11.4 Benzo(b)fluoranthene 7.9 ± 0.9 8.5 ± 1.1 108 12.9 Benzo(k)fluoranthene 4.4 ± 0.5 4.1 ± 0.5 91 12.2 Benzo(a)pyrene 5.3 ± 0.7 5.1 ± 0.6 96 11.8 Indeno(1,2,3-cd)pyrene 5.7 ± 0.6 5.2 ± 0.6 91 11.5 Benzo(g,h,i)perylene 4.9 ± 0.7 4.3 ± 0.5 88 11.6 Dibenz(a,h)anthracene (1.3) 1.1 ± 0.2 (85) 18.2

a Relative standard deviations for the SFE values are based on six replicate extractions.

b Values in parentheses were obtained from, or compared to, Soxhlet extraction results which were not certified.

Data are taken from Reference 10.

CD-ROM 8270D - 54 Revision 4 January 1998TABLE 14

SINGLE LABORATORY ACCURACY AND PRECISION FOR THE EXTRACTION OF PAHs FROM A CERTIFIED REFERENCE SEDIMENT HS-3, USING METHOD 3561 (SFE - SOLID TRAP)

Certified Value SFE Value a Percent of SFE

Compound (mg/kg) (mg/kg) Certified Value RSD Naphthalene 9.0 ± 0.7 7.4 ± 0.6 82 8.1 Acenaphthylene 0.3 ± 0.1 0.4 ± 0.1 133 25.0 Acenaphthene 4.5 ± 1.5 3.3 ± 0.3 73 9.0

Fluorene 13.6 ± 3.1 10.4 ± 1.3 77 12.5

Phenanthrene 85.0 ± 20.0 86.2 ± 9.5 101 11.0

Anthracene 13.4 ± 0.5 12.1 ± 1.5 90 12.4

Fluoranthene 60.0 ± 9.0 54.0 ± 6.1 90 11.3 Pyrene 39.0 ± 9.0 32.7 ± 3.7 84 11.3 Benz(a)anthracene 14.6 ± 2.0 12.1 ± 1.3 83 10.7 Chrysene 14.1 ± 2.0 12.0 ± 1.3 85 10.8 Benzo(b)fluoranthene 7.7 ± 1.2 8.4 ± 0.9 109 10.7 Benzo(k)fluoranthene 2.8 ± 2.0 3.2 ± 0.5 114 15.6 Benzo(a)pyrene 7.4 ± 3.6 6.6 ± 0.8 89 12.1 Indeno(1,2,3-cd)pyrene 5.0 ± 2.0 4.5 ± 0.6 90 13.3 Benzo(g,h,i)perylene 5.4 ± 1.3 4.4 ± 0.6 82 13.6 Dibenz(a,h)anthracene 1.3 ± 0.5 1.1 ± 0.3 85 27.3

a Relative standard deviations for the SFE values are based on three replicate extractions.

Data are taken from Reference 10.

CD-ROM 8270D - 55 Revision 4 January 1998TABLE 15

SINGLE LABORATORY ACCURACY AND PRECISION FOR THE EXTRACTION OF PAHs FROM A CERTIFIED REFERENCE SOIL SRS103-100, USING METHOD 3561 (SFE - LIQUID TRAP)

Compound Naphthalene 2-Methylnaphthalene Acenaphthene
Dibenzofuran Certified Value (mg/kg)

32.4 ± 8.2
62.1 ± 11.5

632 ± 105

307 ± 49 SFE Value a (mg/kg)

29.55
76.13
577.28
302.25 Percent of Certified Value

91

122

91
98 SFE RSD

10.5

2.0
2.9

4.1

Fluorene 492 ± 78 427.15 87 3.0

Phenanthrene 1618 ± 340 1278.03 79 3.4

Anthracene 422 ± 49 400.80 95 2.6

Fluoranthene 1280 ± 220 1019.13 80 4.5 Pyrene Benz(a)anthracene Chrysene Benzo(a)pyrene Benzo(b)fluoranthene + Benzo(k)fluoranthene 1033 ± 285
252 ± 8
297 ± 26
97.2 ± 17.1
153 ± 22 911.82
225.50
283.00

58.28
130.88 88
89
95
60
86 3.1
4.8
3.8
6.5
10.7

a Relative standard deviations for the SFE values are based on four replicate extractions.

Data are taken from Reference 11.

CD-ROM 8270D - 56 Revision 4 January 1998TABLE 16

SINGLE LABORATORY RECOVERY DATA FOR SOLID-PHASE EXTRACTION OF BASE/NEUTRAL/ACID EXTRACTABLES FROM SPIKED TCLP BUFFERS LOW SPIKE LEVEL

Analyte Spike Level (μg/L) Buffer 1 (pH = 2.886)
Recovery (%) RSD Buffer 2 (pH = 4.937)
Recovery (%) RSD
1,4-Dichlorobenzene 3,750 63 10 63 9

Hexachloroethane 1,500 55 6 77 4

Nitrobenzene 1,000 82 10 100 5
Hexachlorobutadiene 250 65 3 56 4
2,4-Dinitrotoluene 65 89 4 101 5
Hexachlorobenzene 65 98 5 95 6
o-Cresol 100,000 83 10 85 5
m-Cresol* 100,000 86 8 85 3 p-Cresol* 100,000 * * * * 2,4,6-Trichlorophenol 1,000 84 12 95 12 2,4,5-Trichlorophenol 200,000 83 11 88 3 Pentachlorophenol 50,000 82 9 78 9

Results from seven replicate spiked buffer samples.

* In this study, m-cresol and p-cresol co-eluted and were quantitated as a mixture of both isomers.

Data from Reference 12.

CD-ROM 8270D - 57 Revision 4 January 1998TABLE 17

SINGLE LABORATORY RECOVERY DATA FOR SOLID-PHASE EXTRACTION OF BASE/NEUTRAL/ACID EXTRACTABLES FROM SPIKED TCLP BUFFERS HIGH SPIKE LEVEL

Analyte Spike Level (μg/L) Buffer 1 (pH = 2.886)
Recovery (%) RSD Buffer 2 (pH = 4.937)
Recovery (%) RSD
1,4-Dichlorobenzene 15,000 63 10 63 9

Hexachloroethane 6,000 54 7 46 7
Nitrobenzene 4,000 81 4 81 13

Hexachlorobutadiene 1,000 81 5 70 11
2,4-Dinitrotoluene 260 99 8 98 3

Hexachlorobenzene 260 89 8 91 9
o-Cresol* 400,000 92 15 90 4
m-Cresol* 400,000 95 8 82 6 p-Cresol* 400,000 82 14 84 7 2,4,6-Trichlorophenol 4,000 93 12 104 12 2,4,5-Trichlorophenol 800,000 93 14 97 23 Pentachlorophenol 200,000 84 9 73 8

Results from seven replicate spiked buffer samples.

* In this study, recoveries of these compounds were determined from triplicate spikes of the individual compounds into separate buffer solutions.

Data from Reference 12.

CD-ROM 8270D - 58 Revision 4 January 1998TABLE 18RECOVERY DATA FROM THREE LABORATORIES FOR SOLID-PHASE EXTRACTIONOF BASE/NEUTRAL/ACID EXTRACTABLES FROM SPIKED TCLP LEACHATES FROM SOIL SAMPLESBuffer 1 pH = 2.886Lab 1Lab 2Lab 3SpikeAnalyteLevel%R RSD n %R RSD n %R RSD n(μg/L)*o-Cresol200,000 86 8 7 35.3 0.7 3 7.6 6 3m-Cresol**-- 77 8 7 -- -- -- -- -- -­p-Cresol**-- -- -- -- -- -- -- 7.7 11 32,4,6-Trichlorophenol 2,000 106 6 7 96.3 3.9 3 44.8 5 32,4,5-Trichlorophenol 400,000 93 3 7 80.5 4.5 3 63.3 11 3Pentachlorophenol 100,000 79 2 7 33.8 12.2 3 29.2 13 31,4-Dichlorobenzene 7,500 51 5 7 81.3 5.3 3 19.2 7 3Hexachloroethane3,000 50 5 7 66.2 2.1 3 12.6 11 3Nitrobenzene2,000 80 8 7 76.3 5.3 3 63.9 12 3Hexachlorobutadiene500 53 8 7 63.3 4.8 3 9.6 9 32,4-Dinitrotoluene130 89 8 7 35.7 2.6 3 58.2 17 3Hexachlorobenzene130 84 21 7 92.3 1.6 3 71.7 9 3(continued)CD-ROM8270D - 59Revision 4January 1998TABLE 18(continued)Buffer 2 pH = 4.937Lab 1Lab 2Lab 3SpikeAnalyteLevel%R RSD n %R RSD n %R RSD n(μg/L)*o-Cresol200,00 97 13 7 37.8 4.5 3 6.1 24 3m-Cresol**-- 83 4 7 -- -- -- 6.0 25 3p-Cresol**-- -- -- -- -- -- -- -- -- -­2,4,6-Trichlorophenol 2,000 104 4 7 91.7 8.0 3 37.7 25 32,4,5-Trichlorophenol 400,000 94 4 7 85.2 0.4 3 64.4 10 3Pentachlorophenol 100,000 109 11 7 41.9 28.2 3 36.6 32 31,4-Dichlorobenzene 7,500 50 5 7 79.7 1.0 3 26.5 68 3Hexachloroethane3,000 51 3 7 64.9 2.0 3 20.3 90 3Nitrobenzene2,000 80 4 7 79.0 2.3 3 59.4 6 3Hexachlorobutadiene500 57 5 7 60 3.3 3 16.6 107 32,4-Dinitrotoluene130 86 6 7 38.5 5.2 3 62.2 6 3Hexachlorobenzene130 86 7 7 91.3 0.9 3 75.5 5 3* 250-mL aliquots of leachate were spiked. Lab 1 spiked at one-half these levels.** m-Cresol and p-Cresol coelute. Lab 1and Lab 3 reported o-Cresol and the sum of m-and p-Cresol. Lab 2 reported the sum ofallthree isomers of Cresol.Data from Reference 12.CD-ROM8270D - 60Revision 4January 1998FIGURE 1 GAS CHROMATOGRAM OF BASE/NEUTRAL AND ACID CALIBRATION STANDARD

CD-ROM 8270D - 61 Revision 4 January 1998METHOD 8270D SEMIVOLATILE ORGANIC COMPOUNDS BY GAS CHROMATOGRAPHY/MASS SPECTROMETRY (GC/MS)

CD-ROM 8270D - 62 Revision 4 January 1998