Extracting Organochlorine Pesticides from Water With Atlantic™ HLB-M Disks (EPA Method 8081) Michael Ebitson, Horizon Technology, Inc., Salem, NH Introduction The purpose of this application note is to establish a solid phase extraction (SPE) procedure to streamline the sample preparation process for determining organochlorine pesticides from water. The analysis of organochlorine pesticides in water has proved a challenging matrix to meet the data requirements for quality control acceptance criteria’s. Traditional extraction methods such as liquid-liquid extraction (LLE) or continuous liquid-liquid extraction (CLLE) can use up to 250 mL of dichloromethane (DCM) as the extracting solvent. LLE and CLLE are labor intensive, use large amounts of solvent, have matrix interfering emulsions, and require contaminant free glassware to determine trace amounts of pesticides in water. With the traditional techniques the user still needs to interact by solvent exchanging the extract from DCM to hexane which involves two concentration steps with hundreds of milliliters of solvents. By using SPE we are able to use acetone and hexane as the extraction solvents for the determination of organochlorine pesticides in aqueous samples. Relative to the DCMacetone mixture, the use of hexane-acetone generally reduces the amount of interferences that are extracted and improves the signal-to-noise ratio within the analysis phase of sample processing. This was accomplished by optimizing an SPE method based on the Horizon Technology SPE-DEX 4790 Automated Extractor System using a 47 mm Atlantic HLB-M extraction disk. The pesticides analyzed in this study were part of a standard mix consisting of alpha-BHC, gamma-BHC (Lindane), beta-BHC, delta-BHC, heptachlor, aldrin, heptachlor epoxide, gamma-chlordane, alpha chlordane, 4,4’-DDE, endosulfan I, dieldrin, endrin, 4,4’-DDD, endosulfan II, 4,4’-DDT, endrin aldehyde, methoxychlor, endosulfan sulfate, and endrin ketone. Tetrachloro-mxylene (TCMX) and decachlorobiphenyl (DCB) were used as the extraction surrogates. Five of the pesticides (DDT, aldrin, dieldrin, endrin, and heptachlor) are known as part of the “dirty dozen” of persistent organic pollutants (POPs). POPs are organic compounds that are resistant to environmental degradation. Pesticide pollution is a subject of global concern, and although many countries have now banned the use of organochlorine pesticides, they linger in the environment and can contaminate water sources. Pesticides are toxic to animals and humans, so methods which accurately and easily quantify them are essential to the future. Organochlorine Pesticide exposure can cause illnesses including disruption of the endocrine, reproductive, and immune systems; neurobehavioral disorders, cancer and in severe cases even death. Horizon Technology, Inc., 45 Northwestern Dr. Salem, NH, 03079 USA Tel: (603) 893-3663 Fax: (603) 893-4994 The Horizon Technology SPE-DEX® 4790 Automated Extraction System, with the Envision® Platform Controller, DryVap® Concentration System, and the Reclaimer™ Solvent Recovery System Instrumentation • • • Horizon Technology -SPE-DEX® 4790 Automated Extractor System -Envision® Platform -Atlantic™ HLB-M 47mm disks -DryVap® Concentrator System -DryDisk® Separation Membranes Agilent -6890 GC with Dual ECD detectors -5890 GC with 5971 MSD Restek -Primary Column: Rtx-CLP1, 30m x 0.2mm ID x 0.25µm film. -Confirmation Column: Rtx-CLP2, 30m x 0.25mm ID x 0.25µm film. Method Summary Pesticide Loss Analysis on the DryVap 1) Place six concentration tubes onto the DryVap containing 25 mL of DCM. 2) Configure the DryVap settings as shown in Table 1. 3) Spike 20 µg of pesticide spike into each tube, then press start on the DryVap. 4) All six spiked samples will automatically dry and concentrate to a final volume of 1.0 mL. 5) Add internal standards then analyze by GC/MS *Alternative Procedure: use 25 ml of hexane, then concentrate and analyze by GC-ECD. Pesticide Extraction 1) 2) 3) Adjust a 1 L aqueous sample to a pH of 2 with HCL. Cap the bottle and mix. Spike the sample with pesticide standard and surrogates (varying concentrations were used: 0.5 µg/L-1.25 µg/L). Place the sealed sample bottle on the SPE-DEX 4790 Extractor System and place the Atlantic HLB-M disk, in the disk holder. Pg. 1 of 3 AN067-101230 Extracting Organochlorine Pesticides from Water With Atlantic™ HLB-M Disks (EPA Method 8081) 4) 5) 6) 7) 8) Run the SPE-DEX 4790 using the pesticides method in Table 2 using acetone and hexane as the extraction solvents After the extraction is complete collect the extract (the final volume should be around 25 mL). Clean the extract using florisil. Concentrate the extract to a final volume of 5.0 mL. Analyze by GC/ECD. Table 1: DryVap Conditions. PARAMETER Dry Volume Heat Power Auto Rinse Mode Heat Timer Nitrogen Sparge SETTING 100 5 OFF OFF 20 psi Vacuum @ -15 in Hg. Table 2: Extraction Method Step Solvent Soak Time Dry Time Prewet 1 Acetone 1:00 min 1:30 min Prewet 2 Hexane 1:00 min 2:00 min Prewet 3 Methanol 30 sec 2 sec Prewet 4 Reagent Water 10 sec 0 Sec Sample Process Air Dry 3:00 min Rinse 1 Acetone 3:00 min 2:00 min Rinse 2 Hexane 3:00 min 2:00 min Rinse 3 Hexane 1:00 min 1:00 min Rinse 4 Hexane 1:00 min 1:00 min Rinse 5 Hexane 1:00 min 1:00 min Results Concentration Results To show the efficiency of the SPE-DEX 4790, a study was done with the DryVap to determine the highest possible percent recoveries that could be achieved with concentration alone. Six DryVap tubes were spiked with 20 µg of pesticide standard into 25 mL of solvent and concentrated to 1.0 mL and analyzed. This study was performed to recover the selected pesticides under ideal conditions. The result of this study is shown in Table 3. The recoveries indicate that the DryVap alone is able to produce great recoveries with minimal loss. This concentration process was fully automated, and did not require any attention once the process was started. Extraction Results With the sample extracted in acetone and hexane instead of DCM, the solvent exchange step has been eliminated. The results shown in Table 4 below indicate that when acetone and hexane are used as the extraction solvents, they produced excellent recoveries on the primary column along with the confirmation column. Horizon Technology, Inc., 45 Northwestern Dr. Salem, NH, 03079 USA Tel: (603) 893-3663 Fax: (603) 893-4994 Table 3: Pesticides Spike Recovery on the DryVap Compounds Avg.% Recovery a-BHC 96 b-BHC 94 g-BHC 91 d-BHC 92 Heptachlor 89 Aldrin 93 Heptachlor Epoxide 92 a-Chlordane 92 g-Chlordane 98 Endosulfan I 91 4,4’-DDE 95 Dieldrin 95 Endrin 96 4,4’-DDD 96 Endosulfan II 101 Endrin Aldehyde 100 4,4’-DDT 95 Endosulfan Sulfate 94 Methoxychlor 98 Endrin Ketone 98 Conclusions The sample preparation step is an essential element of this method development, as such, the advancement of an automated disk extraction enables less solvent use, an elimination of the solvent exchange step, reduced glassware use, emulsion elimination, and faster extraction times with highly particulate or sediment laden samples. This in turn produces consistent and reproducible results. By using Horizon Technology’s SPE-DEX 4790 automated solid phase extraction system with the Atlantic HLB-M disks we were able to achieve excellent recoveries of all organochlorine pesticides. When using the HLB-M disk the extraction process duration was about 30 minutes per sample. Concentrating a 25 mL extract of hexane to a final volume of 5 mL will take approximately 10 minutes with the DryVap. Including the 10 minute sample run times on the GC/ECD, samples were extracted, concentrated, cleaned, and analyzed within two hours with excellent recoveries. Acknowledgements Our thanks go to Sharlene Robinson from GEL Laboratories for her time and assistance with this study. Pg. 2 of 3 AN067-101230 Extracting Organochlorine Pesticides from Water With Atlantic™ HLB-M Disks (EPA Method 8081) Table 4: Organochlorine Pesticides Recoveries Pesticide Compounds Alpha-BHC Gamma-BHC ( Lindane) Beta-BHC Delta-BHC Heptachlor Aldrin Heptachlor Epoxide Gamma-Chlordane Alpha-Chlordane 4,4’DDE Endosulfane I Dieldrin Endrin 4,4’DDD Endosulfane II DDT Endrin Aldehyde Methoxychlor Endosulfan Sulfate Endrin Ketone Tcmx DCB Concentration (ug/L) 0.50 0.50 0.50 0.50 0.50 0.50 0.50 0.50 0.50 1.25 0.50 1.25 1.25 1.25 1.25 1.25 1.25 5.00 1.25 1.25 1.00 1.00 Horizon Technology, Inc., 45 Northwestern Dr. Salem, NH, 03079 USA Tel: (603) 893-3663 Fax: (603) 893-4994 Primary Secondary Column Column CLP 1 CLP 2 Recovery% Recovery% 98 100 94 100 91 87 92 87 91 97 88 95 92 98 89 90 90 89 94 98 81 88 86 88 85 87 82 80 82 82 84 85 81 78 81 86 76 86 76 81 87 86 76 76 Pg. 3 of 3 AN067-101230
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