This application note will outline appropriate methods for the extraction of organophosphorus pesticides from ground water as outlined in EPA method 8141B using the Atlantic® C18 SPE disk processed using Biotage automated or manual SPE solutions and DryVap® Concentrator System. The first section will highlight the use of the Biotage® Horizon 5000 fully automated extraction system and the method used for this application. Additionally, there will be an Application Modification section that will highlight the use of the Biotage® VacMaster™ Disk vacuum manifold for this application.
EPA Method 8141B describes the performance-based procedure for determination of low ppb levels of organophosphorus (OP) pesticides in ground water. The primary extraction solvent is hexane which in turn eliminates the need to perform a solvent exchange.
Organophosphorus pesticides are the most widely used pesticides in the world. They are readily hydrolyzed and therefore do not persist in the environment for very long nor accumulate in the body fat of humans or other animals. The ubiquitous nature of the OP pesticides results in routine exposure for humans through the consumption of fresh and processed vegetables, contact with pesticide-contaminated surfaces, breathing air near pesticide applications, and drinking pesticide contaminated water. OP pesticides interfere with the nervous system of both insects and humans. In humans, these compounds block the production of cholinesterase. The main target organs in humans are the nervous system, respiratory tract, and cardiovascular system. The EPA classifies most OP compounds as toxicity class I (highly toxic) or toxicity class II (moderately toxic).
The OP pesticides are extracted using solid phase extraction (SPE) using Atlantic® C18 disks, based on the procedure outlined in Method 3535A for OP pesticides by Method 8141. The analysis is performed with capillary GC using an FPD (flame photometric detector) utilizing a splitless injection technique.
*The DryVap™ system has been discontinued, we recommend using a TurboVap®.
|
Step
|
Select Solvent
|
Volume (mL)
|
Purge (s)
|
Vacuum
|
Saturate (s)
|
Soak (s)
|
Drain/ Elute (s) |
Sample Delay (s) |
|
|
Condition SPE Disk |
Acetone |
11 |
60 |
2 |
1 |
60 |
180 |
|
|
|
Condition SPE Disk |
Methanol |
11 |
60 |
2 |
1 |
60 |
5 |
|
|
|
Condition SPE Disk |
Reagent water |
15 |
60 |
2 |
1 |
60 |
5 |
|
|
|
Load Sample |
|
|
|
2 |
|
|
|
45 |
|
|
Air Dry Disk |
|
|
|
6 |
|
|
360 |
|
|
|
Elute Sample Container |
Acetone |
8 |
15 |
2 |
1 |
60 |
120 |
|
|
|
Elute Sample Container |
Hexane |
8 |
15 |
2 |
1 |
60 |
120 |
|
|
|
Elute Sample Container |
Hexane |
8 |
15 |
2 |
1 |
90 |
240 |
|
|
|
Elute Sample Container |
Hexane |
8 |
15 |
6 |
1 |
90 |
240 |
|
|
|
GC Conditions
|
Oven Temperature |
Program |
|||
|
Inlet A Temperature |
225 °C |
Initial Temperature |
80 °C |
||
|
Detector A Temperature |
250 °C |
Initial Time |
0.00 min |
||
|
Detector B Temperature |
250 °C |
Level |
Ramp (C/min) |
Temp (°C) |
Final Time(min) |
|
Constant Pressure |
25.0 psi |
1 |
20 |
170 |
0.00 |
|
Carrier Gas |
He |
2 (A) |
10 |
280 |
5.53 |
|
Detector Gas |
He, H, Air |
3 (B) |
0 |
0 |
0 |
Biotage would like to thank Sheldon Murray at the City of Ft. Worth, TX for his help in producing this method.
|
Solvent |
Vol. (mL) |
Saturate (sec.) |
Soak (sec.) |
Waste Destination |
Drain (sec.) |
|
Acetone |
11 |
1 |
60 |
Organic |
180 |
|
MeOH |
11 |
1 |
60 |
Organic |
5 |
|
Reagent Water |
15 |
1 |
60 |
Organic |
5 |
|
Solvent |
Vol. (mL) |
Saturate (sec.) |
Soak (sec.) |
Waste Destination |
Elute (sec.) |
|
Acetone |
8 |
1 |
60 |
Organic |
120 |
|
Hexane |
8 |
1 |
60 |
Organic |
120 |
|
Hexane |
8 |
1 |
90 |
Organic |
240 |
|
Hexane |
8 |
1 |
90 |
Organic |
240 |
Literature number: AN034