Determination of Trace Cations in Power Plant Waters Containing Morpholine

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Application Note 8 Determination of Trace Cations in Power Plant Waters Containing Morpholine INTRODUCTION Morpholine and ammonium are used as additives in power plant waters. Morpholine acts as a corrosion inhibitor, whereas ammonium is used to control ph. In this matrix, it is critical to determine the presence of inorganic cation contaminants. This method uses the IonPac CS1 column to quantify trace concentrations of lithium, sodium, potassium, magnesium, and calcium in the presence of high levels of ammonium and morpholine. Acetonitrile can be added to the eluent to improve peak shape and optimize resolution for some of the cations of interest. EQUIPMENT Dionex Chromatography system comprising: Advanced Gradient Pump (AGP) Liquid Chromatography Module (LCM-), equipped with Model 91-08 Rheodyne Injector or equivalent Preparation Module (SPM) [ for 800 Process Analyzer ] Conductivity Detector Module (CDM-) ing Pump, RP-1 REAGENTS AND STANDARDS Deionized water (DI HO), Type I reagent grade, 17.8MW / cm resistance or better. Methanesulfonic Acid (MSA) (+99% pure) Acetonitrile (ACN) HPLC grade CONDITIONS : () IonPac CG1 (-mm) guard columns, one used as a guard column, the other as a concentrator column (1) IonPac CS1 (-mm) analytical column Eluent : 8 mm Methanesulfonic acid or 8 mm Methanesulfonic acid in % acetonitrile (v/v) Eluent Flow Rate: 0. ml/min Rinsing Flow Rate: 1.0 ml/min Volume: 1.0 ml Detection: Suppressed Conductivity Suppressor: CSRS-I (-mm), AutoSuppression, Recycle Mode (without acetonitrile); External Water Mode (with acetonitrile) Pump programs: 1) 8 mm methanesulfonic acid Time E1 V V Remarks 0.0 100 1 0 Prime RP-1.0 100 0 0 sample to CG-1.0 100 0 0 Inject

.) 8 mm methanesulfonic acid with % acetonitrile Time E1 V V Remarks(rinse) 0.0 100 1 0 Prime RP-1.0 100 0 0 sample to CG-1.0 100 0 1 CG-1 with w/ 8.0 100 1 1 Inject Timed Events Programs ( for operation of 800 Process Analyzer): 1.) 8 mm methanesulfonic acid Step Time Description Initial - ACI SPM valve OFF Initial - ACI RP-1 OFF 1 0. ACI RP-1 ON.0 AGP Run Gradient Clock 9.9 CDM- AutoOffset ON 10.0 ACI SPM valve OFF 10.0 ACI RP-1 OFF 10.0 Start Sampling.) 8 mm methanesulfonic acid with % acetonitrile Step Time Description Initial - ACI SPM valve OFF Initial - ACI RP-1 OFF 1 0. ACI RP-1 ON.0 AGP Run Gradient Clock 11.9 CDM- AutoOffset ON 1.0 ACI SPM valve OFF 1.0 ACI RP-1 OFF 1.0 Start Sampling note: ACI = Advanced Computer PREPARATION OF SOLUTIONS AND REAGENTS 1 M Methanesulfonic acid (MSA) Eluent Concentrate Weigh 9.10 g of methanesulfonic acid (MSA). Carefully add this amount to a 1-L volumetric flask containing about 00 ml of deionized water. Dilute to the mark and mix thoroughly. 8 mm Methanesulfonic acid (MSA) Pipette 8.0 ml of the 1.0 M MSA eluent concentrate into a 1-L volumetric flask. Dilute to 1 L using deionized water. Degas the eluent. 8 mm Methanesulfonic acid (MSA) / % Acetonitrile Pipette 8.0 ml of the 1.0 M MSA eluent concentrate into a 1-L volumetric flask. Dilute to approximately 800 ml using deionized water. Degas the eluent. Add 0 ml of acetonitrile and mix until all components are in solution. Dilute to a final volume of 1.0 L using deionized water. % Acetonitrile for Rinsing Add 0 ml of acetonitrile to approximately 800 ml using deionized water in a 1-L volumetric flask and mix until all components are in solution. Dilute to a final volume of 1.0 L using deionized water. Stock standard solution (1000 mg/l) Lithium (Li+) 1000 mg/l: Dissolve.108 g of lithium chloride (LiCl) in deionized water and dilute to 1.000 liter. Sodium (Na+) 1000 mg/l: Dissolve. g of sodium chloride (NaCl) in deionized water and dilute to 1.000 liter. Ammonium (NH+) 1000 mg/l: Dissolve.9 g of ammonium chloride (NHCl), in deionized water and dilute to 1.000 liter. Potassium (K+) 1000 mg/l: Dissolve 1.907 g of potassium chloride (KCl) in deionized water and dilute to 1.000 liter. Morpholine (tetrahydro-1,-oxazine [CH9NO] ) 1000 mg/l: Pipet 1.00 ml of morpholine into 800 ml of deionized water and dilute to 1.000 liter. Magnesium (Mg+) 1000 mg/l: Dissolve 8. g of magnesium chloride, hexa- hydrate MgCl.HO in deionized water and dilute to 1.000 liter. Calcium (Ca+) 1000 mg/l: Dissolve.8 g of calcium chloride, dihydrate CaCl.HO in deionized water and dilute to 1.000 liter. Calibration Determination of Trace Cations in Power Plant Waters Containing Morpholine

Intermediate standards (low mg/l) are prepared by appropriate dilutions of the stock solutions. Calibration standards (mg/l) are prepared by further diluting the intermediate standards. Prepare a minimum of three concentration levels to bracket the expected concentrations of the sample of interest. DISCUSSION AND RESULTS Trace cations in a power plant morpholine matrix are determined by concentrating 1 ml of sample on a - mm CG1 concentrator column. No sample pre treatment is necessary. The -mm column and suppressor system used in this application has advantages over a - mm system: lower eluent flow rates, higher suppression capacity, and less waste generation. Two different eluents can be used, 8 mm MSA with or without % acetonitrile. The benefit of having organic solvent in the eluent results in improved morpholine peak shape, better separation between morpholine and magnesium, and increased response for the divalent cations. The CSRS is operated in the external water mode with % acetonitrile in the eluent. When using the eluent containing acetonitrile, the sample is loaded onto the CG1 concentrator column and then rinsed with ml of % acetonitrile. This process replaces the aqueous mobile phase in the concentrator with one more nearly matched to the eluent while still retaining the cations of interest. The concentrator column is then switched in line with the eluent stream and the analytical columns. The cations of interest are eluted from the concentrator and separated on the guard and analytical columns. Figures 1 - illustrate how the system performs these tasks. When 8 mm MSA without acetonitrile is used as the eluent, the CSRS is operated in the recycle mode and the step represented by Figure is omitted. To validate this method, precision and linearity were determined for the case with % acetonitrile in the eluent. A multilevel calibration based on the values listed in Table 1 yielded good r values over a wide range. A sample with analyte concentrations within the calibration range showed acceptable precision for both concentration and retention time. Figure shows a representative chromatogram of the sample and Table summarizes the precision results for 1 replicates. For comparison, Figure shows the same sample run with 8 mm MSA and the CSRS in the recycle mode. The maximum sample volume that can be loaded for this method without significant deviation from linearity is 0 mg/l morpholine. A system blank is determined by running deionized water as a sample. Figure 7 illustrates a chromatogram of a blank for the % acetonitrile method. This method using the IonPac CS1 is a useful analytical procedure to determine trace cations in power plant waters containing high morpholine and ammonium. Reproducibility and linearity are within acceptable limits. This method is applicable to on-line and grab sample analysis. The addition of acetonitrile to the eluent improves morpholine peak shape and resolution, permitting quantitative analysis of morpholine. Table 1. Multilevel Calibration for Trace Cations in Morpholine Mix for 8 mm MSA w/ Cation Level 1 Level Level Level r^ Lithium 0.1 0.7 1..7 0.997 Sodium 0. 1..0 1.0 0.998 Ammonium 7. 11. 7.0 11.0 0.999 Potassium 0. 1..0 1.0 0.9990 Morpholine 00.0 100.0 000.0 1000.0 0.9978 Magnesium 0. 1..0 1.0 0.987 Calcium. 7..0 7.0 0.991 Concentration in mg/l Table caption goes here Table. Reproducibility for Trace Cations in Morpholine Mix for 8 mm MSA w/ Conc (mg/l) RSD, Retention RSD Cation Conc Time Retention (%) (min) Time (%) Lithium 0...0 0. Sodium.0.8.7 0. Ammonium 10.0.8. 0. Potassium.0.7.78 0.8 Morpholine 000.0.0 8.1 0. Magnesium.0.0 11.1 0. Calcium 10.0.7 1.9 0. Application Note 8

Prime RP-1 Value =1 Prime RP-1 Value =1 Inj. CG1 1 CG1 Inj. 1 Value =0 Value =1 Figure 1 Prime RP-1 Figure CG1 with Prime RP-1 Value =1 Prime RP-1 Value =1 CG1 Inj. 1 Inj. CG1 1 Value =0 Value =1 Figure sample to CG1 Figure Schematic of IC system: chromatographing the retained ions Determination of Trace Cations in Power Plant Waters Containing Morpholine

1 Ammonium 10 Potassium µs Morpholine Calcium µs 0 Lithium Sodium Magnesium 0 Sodium Morpholine Ammonium Lithium Calcium Potassium 0 10 1 0 Minutes 0 10 1 0 Minutes Figure Trace cations in Morpholine mix: Method Figure Trace cations in Morpholine mix: method 1 10 µs 0 Ammonium Sodium Morpholine Calcium Lithium Potassium Magnesium 0 10 1 0 Minutes PRECAUTIONS Several factors can affect the success of this method. Morpholine can decompose to a variety of compounds such as: formic acid, methylamine, ethylamine, and glycolic acid. The presence of amines could potentially interfere with the separation of the analytes of interest. In addition, it is important to minimize contamination by using the highest quality deionized water and using special care when handling chemicals and instrumentation. REFERENCES Bostic, D.; Burns, G.; Harvey, S. J. Chromatogr. 199, 0, 1-171 Figure 7 Typical blank chromatograms: Method Application Note 8

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