UCT ENVIRO-CLEAN HL DVB

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E N V I R O UCT ENVIRO-CLEAN HL DVB I N N O VAT I O N T H R O U G H C H E M I S T R Y

ENVIRO-CLEAN HL DVB UCT Part# ENVIRO-CLEAN HL DVB extraction columns are manufactured from an extremely clean, and highly cross-linked divinylbenzene based sorbent. The material was developed with the environmental market in mind. It has been successfully used to clean up water samples for testing a wide range of analytes. By varying the sample ph, wash and extraction solvents ENVIRO-CLEAN HL DVB has been used to analyze for acidic, neutral (both polar & non-polar), and basic compounds. Product Part Number Description Units ECHLD156-P 500 mg ENVIRO-CLEAN HL DVB in 6 ml Cartridge 30 per pack Accessories Part Number Description Units VMF016GL 16 Position - Glass Block Manifold 1 VMFSTFR06 Large Volume Sample Transfer Tubes 6 VMFSTFR12 Large Volume Sample Transfer Tubes 12 VMFSTFR06-PFC VMFSTFR12-PFC Large Volume Sample Transfer Tubes - PTFE Free - For Perfluorinated Compound Analysis Large Volume Sample Transfer Tubes - PTFE Free - For Perfluorinated Compound Analysis VMF02125 12 Postion Large Volume Collection Rack 1 ECSS15M6 5g ENVIRO-CLEAN Sodium Sulfate in 6 ml Cartridge 30 6 12 Extraction of Various Organic Compounds in Water Introduction This application describes the use of a novel, versatile polymeric sorbent for the solid phase extraction (SPE) of a range of organic compounds. Depending on the extraction protocol used analysts are able to extract acids, bases, and neutrals including non-polar and even some mid-polar to polar compounds. Several of the compounds extracted are typically not well retained by silica-based sorbents, such as C8 and C18. The analytical performance of this new sorbent is demonstrated by selectively extracting acidic compounds (phenols), neutrals (explosives, organophosphorus pesticides, triazine herbicides, and other polar/non-polar compounds), and bases. The SPE methods are simple and easy to use. It involves cartridge washing and conditioning, sample loading, cartridge drying and analyte elution with proper organic solvents. To ensure good extraction efficiency, the water sample must be de-chlorinated and the sample ph adjusted so that the target analytes are in their uncharged molecular forms. It is only in the neutral form that the analytes are retained by reverse phase functionality on the polymeric sorbent. For acidic compounds, sample ph should be adjusted to 2 units below the lowest pka of the compounds to be extracted. For basic compounds, sample ph should be 2 units above the highest pka of the compounds. For neutral compounds sample ph is not as critical as with acids or bases and can be extracted as received, unless one or more compounds to be extracted are sensitive under certain ph. Sample ph should be adjusted to the value at which any sensitive compounds are most stable to avoid low recovery caused by analyte hydrolysis or degradation. For example, captan and flumioxazin degrade much faster under alkaline conditions; therefore the sample should be adjusted to acidic conditions to avoid analyte degradation. Some compounds hydrolyze under both alkaline and acidic condition (e.g. organophosphorus esters), thus the optimum sample ph is neutral. Knowing the chemical and physical properties of the target analytes helps reduce overall method development time.

UCT created sample transfer tubes (VMFSTFR12) fit SPE cartridges of varying sizes (1, 3, 6, 15, and 25 ml). These transfer tubes allow analysts to load large sample volumes onto SPE cartridges with limited attendance. Simply connect the transfer tube to the SPE cartridge and drop the opposite end, outfitted with a SS sinker into the sample container. Another time and effort saving option is utilized by connecting a drying cartridge (ECSS15M6) directly to the end of the SPE cartridge (ECHLD156P) using a cartridge adaptor (AD0000AS) during the elution step. This eliminates the need for an additional eluate drying step. This procedure can be used when the elution solvents are more nonpolar, such as ethyl acetate or dichloromethane. Another drying option is available when eluting using more polar solvents, such as methanol or acetone. Pack 15 gm of bulk sodium sulfate (ECSS25K) into a 15-mL fritted reservoir (RFV1F15P) and place in-line at the end of the SPE cartridge. Polar solvents elute more water residue from the SPE cartridges than non-polar solvents. The use of the 15mL reservoir with 15 gm of bulk sodium sulfate ensures plenty of drying capacity. 1: Acidic compounds (EPA Method 528) Sample pretreatment 1 L water sample, ph adjusted to < 2 3 x 3 ml dichloromethane (DCM) Cartridge conditioning 3 x 3 ml methanol (MeOH); 4 x 3 ml 0.05 N HCl 15 ml/min 15 min under full vacuum Elution with in-line drying 10 ml DCM bottle rinse; 3 ml DCM to cartridge Eluate evaporation Nitrogen at 40 ºC to 1 ml Analyte Single-lot-results Mutiple-lot-results Recovery% RSD% (n=5) Recovery% RSD% (n=35) Phenol 88.2 2.2 86.4 4.0 2-chlorophenol d4 (Surr) 88.7 1.6 87.3 4.7 2-chlorophenol 87.4 1.3 85.3 3.5 2-methylphenol 88.6 1.5 86.8 3.6 2-nitrophenol 85.6 0.8 85.5 3.8 2,4-dimethylphenol d3 (Surr) 88.5 1.4 86.9 6.6 2,4-dimethylphenol 88.4 1.1 85.1 6.5 2,4-dichlorophenol 87.4 1.3 86.5 3.8 4-chloro-3-methylphenol 90.4 1.0 89.5 2.9 2,4,6-trichlorophenol 88.3 0.6 87.8 3.2 2,4-dinitrophenol 103.2 7.6 108.4 5.6 4-nitrophenol 96.5 1.2 97.4 4.2 2-methyl-4,6-dinitrophenol 92.9 2.5 97.9 6.7 2,4,6-tribromophenol (Surr) 88.7 0.9 89.5 4.3 Pentachlorophenol 94.3 1.1 95.8 4.7

ENVIRO-CLEAN HL DVB 2: Basic compounds Sample pretreatment 1 L water sample, ph adjusted to 12 3 x 5 ml DCM Cartridge conditioning 3 x 5 ml MeOH; 10 ml DI water 25 ml/min 10 min under full vacuum Elution with in-line drying 10 ml EtOAc and 10 ml DCM Eluate evaporation Nitrogen at 40 ºC to 1 ml Analyte pka Recovery % RSD% (n=5) Aniline 4.64 95.5 1.4 o-toluidine 4.48 95.0 1.4 Quinoline 4.50 86.8 1.4 2,3-dichloroaniline 2.09 86.8 1.6 Benzidine 3.65; 4.73 85.9 1.2 3,3'-Dichlorobenzidine 1.97; 2.95 105.6 1.1 Abundance 1400000 1300000 1200000 1100000 1000000 Aniline o-toluidine Quinoline 2,3-dichloroaniline Benzidine 3,3'-Dichlorobenzidine 900000 800000 700000 TPP 600000 500000 400000 300000 200000 100000 Time--> 0 7.00 8.00 9.00 10.00 11.00 12.00 13.00 14.00 15.00 16.00 17.00 18.00 19.00 Chromatogram of a sample spiked with 20 µg/l analytes

3: Neutral compounds 3a. Organophosphorus pesticides and triazine herbicides (EPA Method 8141B) Sample pretreatment 1 L water sample, at neutral ph 3 x 5 ml DCM Cartridge conditioning 2 x 5 ml MeOH; 2 x 5 ml DI water 15 ml/min 10 min under full vacuum Elution 5 ml acetone bottle rinse; 5 ml DCM bottle rinse; 5 ml DCM to cartridge Eluate drying 15 g sodium sulfate in 15 ml fritted reservoir Eluate evaporation Concentrate to 0.5 ml under nitrogen at 40 ºC Solvent exchange Solvent exchange to n-hexane Analyte Class Recovery % RSD% (n=5) o,o,o-triethyl phosphorothioate Organophosphorus 87.8 1.8 Thionazin Organophosphorus 100.9 1.8 Sulfotep Organophosphorus 96.2 0.9 Phorate Organophosphorus 93.0 1.2 Dimethoate Organophosphorus 108.7 7.3 Simazine Triazine 104.2 2.1 Atrazine Triazine 101.5 1.2 Disulfoton Organophosphorus 85.5 1.7 Methyl parathion Organophosphorus 112.4 1.8 Malathion Organophosphorus 110.7 1.3 Parathion Organophosphorus 106.8 1.3 Ethion Organophosphorus 107.8 0.7 Famphur Organophosphorus 120.0 1.8 Abundance 2900000 2800000 2700000 2600000 2500000 2400000 2300000 2200000 2100000 2000000 1900000 1800000 1700000 1600000 1500000 1400000 1300000 1200000 1100000 1000000 900000 800000 2 3 4 1 12 8 10 11 TPP 9 7 13 700000 600000 500000 400000 300000 200000 100000 0 8.00 10.00 12.00 14.00 16.00 18.00 20.00 Time--> Chromatogram of a sample spiked with 10 µg/l analytes 5 6 Peak list: 1. o,o,o-triethyl phosphorothioate; 2. Thionazin; 3. Sulfotep; 4. Phorate; 5. Dimethoate; 6. Simazine; 7. Atrazine; 8. Disulfoton; 9. Methyl parathion; 10. Malathion; 11. Parathion; 12. Ethion; 13. Famphur.

ENVIRO-CLEAN HL DVB 3b. Other polar and non-polar neutral compounds Sample pretreatment 1 L water sample, ph adjusted to <5 3 x 5 ml DCM Cartridge conditioning 3 x 5 ml MeOH; 10 ml DI water 30 ml/min 10 min under full vacuum Elution with in-line drying 10 ml EtOAc and 10 ml DCM Eluate evaporation Concentrate to 1 ml under nitrogen at 40 ºC Analyte LogP Recovery % RSD% (n=5) Butylated hydroxyanisole 3.06 84.7 1.7 Diethyl phthalate 2.42 91.0 2.2 Dimethipin -1.53 94.7 1.9 Methyl parathion 2.80 91.9 2.7 Carbaryl 2.36 107.0 6.9 Malathion 2.36 97.2 2.7 Captan 2.35 91.7 2.6 Nitrofen 4.62 87.9 4.0 Ethion 3.93 90.6 3.5 4,4'-DDT 6.46 88.1 3.3 Captafol 3.95 92.2 4.2 Bis(2-ethylhexyl) phthalate 4.89 92.9 4.1 Abundance 2000000 12 1800000 1600000 1400000 1200000 1000000 800000 600000 1 2 3 4 5 6 7 8 9 10 TPP 11 400000 200000 Time--> 0 11.00 12.00 13.00 14.00 15.00 16.00 17.00 18.00 19.00 Chromatogram of a sample spiked with 20 µg/l analytes Peak list: 1. Butylated hydroxyanisole; 2. Diethyl phthalate; 3. Dimethipin; 4. Methyl parathion; 5. Carbaryl; 6. Malathion; 7. Captan; 8. Nitrofen; 9. Ethion; 10. 4,4 -DDT; 11. Captafol; 12. Bis(2-ethylhexyl) phthalate.

3c. Explosives (EPA Method 529 and 8330) Sample pretreatment 1 L water sample, ph as received 3 x 5 ml ethyl acetate (EtOAc) Cartridge conditioning 3 x 5 ml MeOH; 2 x 10 ml DI water 15 ml/min 10 min under full vacuum Elution with in-line drying 5 ml EtOAc bottle rinse; 5 ml EtOAc to cartridge Eluate evaporation Concentrate to 1 ml under nitrogen at 40 ºC Analyte Single-lot-results Mutiple-lot-results Recovery% RSD% (n=5) Recovery% RSD% (n=35) Nitrobenzene d5 Surr 92.4 3.5 88.9 4.3 Nitrobenzene 86.8 2.7 88.8 4.6 2-Nitrotoluene 87.6 3.6 89.1 4.7 3-Nitrotoluene 86.6 3.6 87.7 4.6 4-Nitrotoluene 84.4 3.3 87.2 4.9 1,3-Dinitrobenzene 102.4 5.3 99.7 4.2 2,6-Dinitrotoluene 98.2 5.7 97.3 4.8 2,4-Dinitrotoluene 91.2 5.3 92.9 4.2 1,3,5-Trinitrobenzene 100.0 9.1 100.4 5.5 2,4,6-Trinitrotoluene 103.0 6.3 100.9 5.3 RDX 107.0 1.7 111.1 5.8 4-Amino-2,6-Dinitrotoluene 100.1 7.5 99.6 5.8 3,5-Dinitroaniline 104.3 5.6 103.6 6.3 2-Amino-4,6-Dinitrotoluene 103.3 5.2 105.7 5.0 Tetryl 102.2 3.7 105.4 4.7 Conclusions A novel and versatile polymeric sorbent effectively retains a range of organic compounds, including acids, neutrals (polar and non-polar compounds), and bases Cross-linked polymeric sorbent with > 5 times greater capacity than silica-based sorbents Stable in samples with ph ranged from 0 to 14 Straightforward SPE extraction protocols with excellent precision and accuracy Unique polymeric structure contributed to consistent analytical performance with minimum lotto-lot variations

ENVIRO-CLEAN HL DVB PRICES AND TERMS Our prices are subject to change without notice. The price in effect when we receive your order will apply. All prices are in US Dollars and are F.O.B. Terms of payment are net 30 days. MINIMUM ORDERS We welcome all orders, therefore, we do not have a minimum order requirement. When ordering, please include your purchase order number, complete Ship To and Bill To address, catalog number, quantity, and description of product(s). Also include your name and a phone number where you can be reached should we have any questions concerning your order. SHIPMENTS Normal processing is within 24 hours after receipt of an order. Unless special shipping requests have been made, our trained staff will send all orders by UPS Ground service. The appropriate shipping charges (freight & insurance costs) will be added to the invoice, unless otherwise instructed by the customer. SPECIAL PRICING We offer special pricing for volume purchases and standing orders. These discounts apply to bonded phase extraction column purchases only. Please call a sales representative for more information on special pricing qualifications. RETURN POLICY Our Quality Manager will handle all returns. Before returning merchandise, please call to obtain a return authorization number from the quality manager. We will need to know the reason for the return, date of purchase, purchase order number and invoice number in order to issue a return authorization number. Return merchandise must be received before a credit can be issued. Returns will not be accepted after 90 days. A restocking fee of 25% of the price paid, or a minimum of $25.00 (whichever is greater) will be charged on all returns. WARRANTY All products manufactured by UCT are guaranteed against defects in materials and workmanship for a period of 90 days after shipment. UCT will replace any items that prove to be defective during this time period. The exclusive remedy requires the end user to first advise UCT of the defective product by phone or in writing and must include order number, the lot number and the shipping date. To initiate this action, photographs of the product, including packaging and labeling of the containers, must be submitted to the UCT Representative for approval. With approval a return authorization can be initiated, and must be received within 30 days. Once the materials arrive at UCT a further inspection of the materials must be completed and accepted by our Quality Manager prior to further action of credits or replacement. UCT s total liability is limited to the replacement cost of UCT products. This warranty does not apply to damage resulting from misuse. Placing An Order Phone: 215.781.9255 800.385.3153 Fax: 215.785.1226 UCT, Inc. 2731 Bartram Rd. Bristol, PA 19007 Email: info@unitedchem.com Web: www.unitedchem.com 4110-03-04 UCT ENVIRO