|
US EPA 8270
The ATAS 8270 Injector System has been developed to automate the injection of the large volumes of the sample
extract directly into the OPTIC injector. It is known that the ability to routinely inject larger volumes
of solvent results in significant savings for the sample preparation laboratory. It is estimated that 65% of all
costs associated with semi-volatile sample analysis result from sample preparation and concentration.
By a significant increase in GC-MS sensitivity, sample volumes can be greatly reduced from 1000 ml down to 50 ml or less. Corresponding decreases in solvent usage are also
realized. Soil samples can be extracted and analyzed without further concentration steps. Volatile
surrogate recoveries show dramatic improvement.
The ATAS 8270 Injector System has been configured to provide all the components necessary for successful
installation and validation of EPA 8270 Method. A single part number is all that is required to order the
complete turn-key package.Our 8270 ATAS Injection System is guaranteed to exceed 8270 method compliance criteria.
KEY FEATURES OF THE ATAS 8270 INJECTOR SYSTEM
Reproducible large volume injection
Reproducible, quantitative results (tested by US EPA)
Rugged, reliable, automated performance
Significant cost savings in sample preparation
Guaranteed Method 8270 performance
Flexible OPTIC injector allows for additional method development
Compatible with all GC-MS systems
|
Reference Method |
Ambient Water |
|
Semi-Volatiles by LVI / GC-MS (BNAs) EPA Method 8270
Modified |
MDLa (ug/L) |
RDLb (ug/L) |
|
Parameter |
|
|
|
1,2,4-Trichlorobenzene |
0.01 |
0.05 |
|
1,2-Dichlorobenzene |
0.05 |
0.25 |
|
1,3-Dichlorobenzene |
0.05 |
0.25 |
|
1,4-Dichlorobenzene |
0.05 |
0.25 |
|
2,4,5-Trichlorophenol |
0.13 |
0.25 |
|
2,4,6-Trichlorophenol |
0.05 |
0.25 |
|
2,4-Dichlorophenol |
0.1 |
0.25 |
|
2,4-Dimethylphenol |
1.5 |
5 |
|
2,4-Dinitrophenol |
1 |
2.5 |
|
2,4-Dinitrotoluene |
0.05 |
0.125 |
|
2,6-Dinitrotoluene |
0.05 |
0.125 |
|
2-Chloronaphthalene |
0.01 |
0.05 |
|
2-Chlorophenol |
0.1 |
0.25 |
|
2-Fluorophenol |
0.025 |
0.05 |
|
2-Methylnaphthalene |
0.1 |
0.5 |
|
2-Methylphenol |
0.25 |
2.5 |
|
2-Nitroaniline |
0.1 |
0.2 |
|
2-Nitrophenol |
0.05 |
0.25 |
|
3,3'-Dichlorobenzidine |
0.75 |
5 |
|
3-Nitroaniline |
0.5 |
1.25 |
|
4,6-Dinitro-O-Cresol |
1 |
2.5 |
|
4-Bromophenyl Phenyl Ether |
0.025 |
0.05 |
|
4-Chloro-3-Methylphenol |
0.25 |
0.5 |
|
4-Chloroaniline |
0.25 |
0.5 |
|
4-Chlorophenyl Phenyl Ether |
0.025 |
0.05 |
|
4-Methylphenol |
0.25 |
1.25 |
|
4-Nitroaniline |
0.5 |
1.25 |
|
4-Nitrophenol |
0.5 |
2.5 |
|
Acenaphthene |
0.01 |
0.05 |
|
Acenaphthylene |
0.01 |
0.05 |
|
Anthracene |
0.01 |
0.05 |
|
Benzo(a)anthracene |
0.025 |
0.05 |
|
Benzo(a)pyrene |
0.01 |
0.025 |
|
Benzo(b)fluoranthene |
0.01 |
0.025 |
|
Benzo(g,h,i)perylene |
0.05 |
0.125 |
|
Benzo(k)fluoranthene |
0.01 |
0.025 |
|
Benzyl Butyl Phthalate |
0.01 |
0.025 |
|
Bis(2-Chloroethoxy)Methane |
0.01 |
0.025 |
|
Bis(2-Chloroethyl)Ether |
0.01 |
0.025 |
|
Bis(2-Chloroisopropyl)Ether |
0.01 |
0.025 |
|
Bis(2-Ethylhexyl)Phthalate |
0.01 |
0.025 |
|
Caffeine |
0.01 |
0.025 |
|
Carbazole |
0.025 |
0.05 |
|
Chrysene |
0.025 |
0.05 |
|
Dibenzo(a,h)anthracene |
0.05 |
0.125 |
|
Dibenzofuran |
0.01 |
0.025 |
|
Diethyl Phthalate |
0.01 |
0.025 |
|
Dimethyl Phthalate |
0.01 |
0.025 |
|
Di-N-Butyl Phthalate |
0.01 |
0.025 |
|
Di-N-Octyl Phthalate |
0.01 |
0.025 |
|
Fluoranthene |
0.01 |
0.025 |
|
Fluorene |
0.01 |
0.025 |
|
Hexachlorobenzene |
0.025 |
0.05 |
|
Hexachlorobutadiene |
0.05 |
0.25 |
|
Hexachloroethane |
0.025 |
0.125 |
|
Indeno(1,2,3-Cd)Pyrene |
0.05 |
0.25 |
|
Isophorone |
0.01 |
0.025 |
|
Naphthalene |
0.025 |
0.05 |
|
Nitrobenzene |
0.01 |
0.025 |
|
N-Nitrosodimethylamine |
0.025 |
0.05 |
|
N-Nitrosodi-N-Propylamine |
0.1 |
0.2 |
|
N-Nitrosodiphenylamine |
0.25 |
1.25 |
|
Pentachlorophenol |
0.13 |
0.25 |
|
Phenanthrene |
0.01 |
0.025 |
|
Phenol |
0.1 |
0.2 |
|
Pyrene |
0.01 |
0.025 |
a Method Detection Limit.
b Reporting Detection Limit.
|
|