Using a Reagent-Free ion chromatography system to monitor trace anion contamination in the extracts of electronic components

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APPLICATION UPDATE 157 Using a Reagent-Free ion chromatography system to monitor trace anion contamination in the extracts of electronic components Authors Sumate Pengpumkiat, Weerapong Worawirunwong, Jeff Rohrer Thermo Fisher Scientific, Sunnyvale, CA Keywords Ion chromatography, IC, Dionex ICS-5000 +, Integrion, carbonate removal, IonPac AS17, fluoride, acetate, formate, acrylate, methacrylate, chloride, 2-ethylhexanoate, bromide, nitrate, benzoate, sulfate, oxalate, phosphate, citrate, water extract, electronic components Introduction Thermo Scientific Application Note 153 (AN153 showed that ion chromatography (IC successfully determines low µg/l and, for some analytes, high ng/l anions in extracts of electronic components. 1 Keeping the anionic contamination of electronic components low can reduce the incidence of component failure. The IC method in AN153 separated 14 inorganic anions and organic acids on a Thermo Scientific Dionex IonPac AS17 column set after either a 1 ml direct injection or a 5 ml sample preconcentration. In this application update a hydroxide gradient program similar to, but faster than, the program used in AN153 separates a new set of 14 anions. This set of anions differed from the original set by the replacement of nitrite and phthalate with 2-ethylhexanoate and citrate. 2-Ethylhexanoate is the byproduct of an adhesive sometimes used in the disk drive industry. We have also incorporated the recently introduced Carbonate Removal Device (CRD. The CRD removes most of the carbonate from a 1 ml sample injection allowing a more reliable quantification of sulfate, oxalate, and other anions eluting just after carbonate. 2

Experimental Equipment Thermo Scientific Dionex ICS-3000* system consisting of: DP Dual Pump EG Eluent Generator with CR-ATC and Thermo Scientific Dionex EluGen EGC-KOH cartridge CRD (Carbonate Removal Device (P/N 62983 DC Detector/Chromatography compartment Thermo Scientific Chromeleon 6.7 Chromatography Management Software * Equivalent or improved results can be achieved using any Thermo Scientific Dionex Reagent-Free Ion Chromatography (RFIC system. An autosampler was not used for the work presented in this application update, but either a Thermo Scientific Dionex AS40 Autosampler or a Thermo Scientific Dionex AS Autosampler can be used as long as the proper precautions are taken to produce a clean blank. For these precautions, see the Sample Loading and the Precautions sections of Application Note 153. 1 Reagent and standards Deionized water (DI, Type I reagent grade, 18.2 MΩ cm resistivity Sodium fluoride (NaF Sodium acetate anhydrous (C 2 H 3 Na Formic acid (CH 2 Acrylic acid (C 3 H 4 Methacrylic acid (C 4 H 6 Sodium chloride (NaCl Potassium bromide (KBr Sodium nitrate (NaNO 3 Benzoic acid (C 7 H 6 Sodium sulfate (Na 2 SO 4 Potassium dihydrogen phosphate (KH 2 PO 4 Citric acid (C 6 H 8 O 7 2-ethylhexanoic acid (C 8 H 16 All compounds were ACS reagent grade or better and obtained from reliable sources. 2-Ethylhexanoic acid was purchased from Fluka Biochemika, Milwawkee, WI. Conditions Column: Guard: Eluent: Gradient: Time (min Thermo Scientific Dionex IonPac AS17, 4 250 mm Thermo Scientific Dionex IonPac AG17, 4 50 mm Dionex EGC-KOH cartridge 0.3 mm isocratic to 7 min; gradient to 15 mm at 20 min; gradient to 40 mm at 25 min; isocratic to 26.9 min; step change to 0.3 mm at 27 min Concentration (mm -7.0 0.3 0.0 0.3 7.0 0.3 20.0 15 25.0 40 26.9 40 27.0 0.3 Flow Rate: 1 ml/min Temperature: 30ºC Sample Loop: 25 µl Detection: Suppressed conductivity, Thermo Scientific Dionex ASRS ULTRA II in external water mode with CRD Preparation of solutions and reagents Eluent The KOH eluent is prepared automatically by pumping DI water through the Eluent Generator equipped with a Dionex EGC-KOH cartridge. Oxalic acid (C 2 H 2 O 4 2

Standard solutions Stock standards Prepare 1,000 mg/l standards for each of the anions in DI water. Standards should be prepared from the highest purity compounds available (i.e., ACS reagent grade or better. Table 1 provides the amounts needed to prepare 100 ml of each standard. Concentrated standards are stable for at least one month when stored at 4ºC. Table 1. Mass of compounds used to prepare 100 ml of 1,000 mg/l anion standards Anion Compound Amount (g Fluoride Sodium Fluoride 0.2210 Acetate Sodium Acetate 0.1389 Formate Formic Acid 0.1022 Acrylate Acrylic Acid 0.1014 Methacrylate Methacrylic Acid 0.1011 Chloride Sodium Chloride 0.1646 2-Ethylhexanoate 2-Ethylhexanoic Acid 0.1006 Bromide Potassium Bromide 0.1487 Nitrate Sodium Nitrate 0.1370 Benzoate Benzoic Acid 0.1008 Sulfate Sodium Sulfate 0.1479 Oxalate Oxalic Acid 0.1008 Phosphate Potassium Dihydrogen Phosphate 0.1432 Citrate Citric Acid 0.1005 System preparation and setup Application Note 153 provides a thorough discussion of the system preparation and setup used in this application update. See Technical Note 62 for instructions describing CRD installation. 2 Results and discussion To separate the 14 anion set of fluoride, acetate, formate, acrylate, methacrylate, chloride, 2-ethylhexanoate, bromide, nitrate, benzoate, sulfate, oxalate, phosphate, and citrate, we evaluated the Dionex IonPac AS17 separation used in AN153 and the Dionex IonPac AS15 separation used in Application Update 142. 3 Both columns use hydroxide eluent gradients making them ideally suited for use with an RFIC system. This allows the most sensitive and reproducible analyses with the additional benefit of removing the time and possible errors associated with manual eluent preparation. We found that the Dionex IonPac AS17 column offered the fastest analysis and best resolution for this set of 14 anions. If glycolate must be determined, consider using the Dionex IonPac AS15 column. Figure 1 shows the separation of a standard mixture of the 14 anions at 0.188 (fluoride to 1.88 (2-ethylhexanoate mg/l concentrations on an AS17 column set. 2-Ethylhexanoate elutes just before bromide at 13.8 min and citrate is the last anion to elute. This method is about six minutes faster than the method described in AN153. To achieve this time savings, one short gradient ramp was eliminated and the other gradient ramps were made steeper. These faster conditions may not completely resolve nitrite from chloride or phthalate. 2.0 µs Peaks: 1. Fluoride 0.1875 mg/l 2. Acetate 0.875 3. Formate 0.625 4. Acrylate 0.625 5. Methacrylate 0.625 6. Chloride 0.25 7. 2-Ethylhexanoate 1.875 8. Bromide 0.5 1 2 4 5 3 6 0.10 0 5 10 15 20 25 Minutes Figure 1. Separation of a mixed anion and organic acid standard. 7 8 9 10 9. Nitrate 0.625 10. Benzoate 1.25 11. Carbonate (n.a. 12. Sulfate 0.5 13. Oxalate 0.5 14. Phosphate 0.5 15. Citrate 1.0 Tables 2 and 3 show the standards used for method calibration and the calibration results. The method reported here uses a 25 µl injection volume. For determining lower concentrations of contaminating anions, up to 1 ml of sample can be used and the system should be calibrated with lower concentration standards using the same injection volume as the sample, as described in AN153. Despite using only a 25 µl injection volume, this method has good sensitivity as shown in the chromatogram of the MDL standard (Figure 2 and the results of the MDL determination (Table 4. The excellent sensitivity can be attributed to the RFIC system. 11 12 13 14 15 3

Table 2. Standard concentrations for method calibration. Analyte Level 1 (mg/l Level 2 (mg/l Level 3 (mg/l Fluoride 0.094 0.188 0.375 Acetate 0.438 0.875 1.750 Formate 0.313 0.625 1.250 Acrylate 0.313 0.625 1.250 Methacrylate 0.313 0.625 1.250 Chloride 0.125 0.250 0.500 2-Ethylhexanoate 0.938 1.875 3.750 Bromide 0.250 0.500 1.000 Nitrate 0.313 0.625 1.250 Bezoate 0.625 1.250 2.500 Sulfate 0.250 0.500 1.000 Oxalate 0.250 0.500 1.000 Phosphate 0.250 0.500 1.000 Citrate 0.500 1.000 2.000 3.0 µs Peaks: 1. Fluoride 1.0 µg/l 2. Acetate 5.0 3. Formate 3.0 4. Acrylate 5.0 5. Methacrylate 5.0 6. Chloride 0.75 7. Unknown 8. 2-Ethylhexanoate 10.0 9. Bromide 3.0 10. Nitrate 2.5 11. Unknown 1 2 12. Benzoate 5.0 13. Unknown 14. Carbonate n.a. 15. Unknown 16. Unknown 17. Sulfate 2.5 18. Oxalate 2.5 19. Phosphate 5.0 20. Unknown 21. Unknown 22. Citrate 0.5 14 17 10 16 19 20 22 12 21 13 4 9 15 18 3 5 6 7 8 11 Table 3. Method calibration results as reported by Chromeleon software. %Coeff. Analyte r 2 Det. Offset Slope Fluoride 99.99 99.9899-0.006 0.4714 Acetate 99.99 99.9899-0.0006 0.1237 Formate 99.995 99.9954-0.0032 0.0977 Acrylate 100 99.9999-0.0019 0.0968 Methacrylate 99.995 99.9948-0.0003 0.0968 Chloride 99.993 99.9931-0.0038 0.2873 2- Ethylhexanoate 99.712 99.7117-0.0089 0.0313 Bromide 99.996 99.9945-0.0023 0.1177 Nitrate 99.995 99.9945-0.0058 0.1548 Benzoate 100 100-0.0032 0.0663 Sulfate 99.988 99.9882-0.0064 0.2183 Oxalate 99.992 99.9925-0.0029 0.1585 Phosphate 99.967 99.9672-0.003 0.0965 Citrate 99.996 99.9958 0.0002 0.0746 0.10 0 5 10 15 20 25 Minutes Figure 2. Separation of a low concentration mixed anion and organic acid standard. Table 4. Determination of MDLs for 14 anions. Analyte Concentration (μg/l RSD (% MDL (μg/l Fluoride 1.0 15.4 0.48 Acetate 5.0 16.0 2.5 Formate 3.0 23.5 2.2 Acrylate 5.0 23.9 3.7 Methacrylate 5.0 16.4 2.6 Chloride 0.75 17.8 0.42 2-Ethylhexanoate 10.0 12.5 3.9 Bromide 3.0 16.3 1.5 Nitrate 2.5 12.1 0.95 Bezoate 5.0 20.5 3.2 Sulfate 2.5 17.9 1.4 Oxalate 2.5 19.1 1.5 Phosphate 5.0 17.3 2.7 Citrate 2.5 17.5 1.4 4

Summary An RFIC system equipped with a Dionex IonPac AS17 column separated anions and organic acids in high-purity water. This method can be used to determine fluoride, acetate, formate, acrylate, methacrylate, chloride, 2-ethylhexanoate, bromide, nitrate, benzoate, sulfate, oxalate, phosphate, and citrate in the water extracts of electronic components. Precautions For a successful trace-level anion determination, contamination must be minimized. Please see the Precautions section of Application Note 153 for advice on minimizing contamination. References 1. Determination of Inorganic Anions in Environmental Waters Using a Hydroxide-Selective Column. Thermo Scientific Application Note 153, AN71782, Sunnyvale, CA, 2003. https://tools.thermofisher.com/content/sfs/brochures/an-153-ic-trace-anion- Electronic-Components-AN71782-EN.pdf 2. Reducing Carbonate Interference in Anion Determinations with the Carbonate Removal Device (CRD. Thermo Scientific Technical Note 62, AN70441, Sunnyvale, CA, 2006. https://tools.thermofisher.com/content/sfs/brochures/tn-62-reducing-carbonate- Interference-Anion-Determinations-CRD-TN70441-EN.pdf 3. Improved Determination of Trace Anions in High Purity Water by High-Volume Direct Injection with the EG40. Thermo Scientific Application Update 142, Sunnyvale, CA, 2001. http://tools.thermofisher.com/content/sfs/ brochures/4192-au142_lpn1291-01.pdf Find out more at thermofisher.com/ic 2016, 2017 Thermo Fisher Scientific Inc. All rights reserved. All trademarks are the property of Thermo Fisher Scientific and its subsidiaries. This information is presented as an example of the capabilities of Thermo Fisher Scientific products. It is not intended to encourage use of these products in any manners that might infringe the intellectual property rights of others. Specifications, terms and pricing are subject to change. Not all products are available in all countries. Please consult your local sales representatives for details. AU72542-EN 1017S