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User Benefits Application News (1) The sample passes through TXA-04 absorption unit manufactured by Nittoseiko Analytech, where adsorbable compounds are adsorbed onto GAC. (2) Inorganic fluorine compounds are washed out. (3) GAC is set in a ceramic boat and combusted. (4) Combustion products are collected in adsorbent solution. (5) The adsorbent solution is injected into ion chromatograph. Fig. 1 Combustion ion chromatograph Nexera IC suppressor ion chromatograph for anion analysis manufactured by Shimadzu Corporation (left) and AQF-5000H automatic quick furnace manufactured by Nittoseiko Analytech. (right) Table 1 Analytical Conditions Table 1 shows the analytical conditions for combustion unit and ion chromatograph. Introduction The U.S. Environmental Protection Agency has published EPA 1621 1) , which is the screening method for the detection of AOF in solutions using combustion ion chromatograph (CIC). This method involves passing the sample through a granular activated carbon (GAC) column to adsorb AOF onto the activated carbon, followed by combustion to decompose AOF. The resulting gas from AOF is then captured in the adsorbent solution and measured as fluoride ions by ion chromatography. The advantage of CIC is that not only PFAS but also their degradation products and derivatives can be measured as the total amount of organic fluorinated compounds. In this article, an AOF analysis using a CIC system consisting of an automatic combustion device and ion chromatograph, as well as integrated control software C-IC Solution, is introduced. Not only integrated controlling of combustion device and ion chromatograph, but also AOF analysis in accordance with EPA 1621 can be performed efficiently using C-IC Solution. Entire process—from sample combustion to analysis—can be performed automatically by combination use of AQF-5000H automatic quick furnace and Nexera IC ion chromatograph. Integrated C-IC Solution software enables integrated operation of the combustion ion chromatograph and analysis in accordance with EPA 1621. Analysis of Adsorbable Organic Fluorine (AOF) in Accordance with EPA 1621 Using Combustion Ion Chromatograph(CIC) —Efficient Workflow Using C-IC Solution— Tomoka Kaseda 1 , Shiho Ishimoto 1 , Tamaki Tomoyori 2 , Nanako Ikeda 2 Ion Chromatograph Nexera IC 1 Shimadzu Corporation, 2 Nittoseiko Analytech Instrumentation and analysis AQF-5000H automatic quick furnace for CIC manufactured by Nittoseiko Analytech and Nexera IC suppression chromatograph for anion analysis manufactured by Shimadzu Corporation were employed as the combustion unit and the ion chromatograph of CIC, respectively (Fig. 1). The sample pretreatment and analytical procedures are as follows. System : AQF-5000H Sample boat : Ceramic Pyrolysis tube : Ceramic inner + quartz outer tube Furnace inlet temperature : 1000 ℃ Furnace outlet temperature : 1100 ℃ Oxygen flow : 400 mL/min Argon flow : 200 mL/min Humidified argon flow : 100 mL/min Absorption solution : Reagent Water Final absorption solution volume : 11.1 mL System : Nexera IC Column : Shim-pack IC-SA2 *1 (250 mm × 4.0 mm I.D., 9 µm) Guard Column Shim-pack IC-SA2(G) *2 ( 10 mm × 4.6 mm I.D., 9 µm ) Mobile phase : 1.8 mmol/L Na2CO3 1.7 mmol/L NaHCO3 Flow rate : 1.0 mL/min Column temperature : 30 ℃ Injection volume : 50 µL Suppressor unit : ICDS-Ai Detection : Conductivity *1 P/N:228-38983-91 *2 P/N:228-38983-92 In this article, the analytical results are presented following the procedure described in EPA 1621 as follows. (1) Creation and evaluation of calibration curve (2) Verification of initial performance Calculation of retention time window Calculations of initial precision and recovery (IPR), method detection limit (MDL), and minimum level (ML) (3) Analysis of unknown samples
Application News Fig. 2 Analytical control screen of C-IC Solution C-IC Solution, integrated control software C-IC Solution integrated control software enables centralized control of both combustion unit and ion chromatograph. It allows users to: (1) view the total time to complete the analysis; (2) confirm the current run number and the start time of the analysis; and (3) monitor the operational status of both combustion unit and ion chromatograph. Fig. 2 shows the analysis screen of C-IC Solution. When starting an analysis, simply enter the sample name and the number of calibration levels, and the software automatically creates analytical batch for combustion system and ion chromatograph; it is also possible to create an analytical schedule in accordance with EPA 1621 (Fig. 3). Creation and evaluation of calibration curve EPA 1621 employs the combustion calibration curve method, in which standard solutions are also subjected to combustion pretreatment (without concentration). In this analysis, 200 µL each of sodium fluoride aqueous solutions ranging from 0.1 to 25 mg/L were combusted and adsorbed into 11.1 mL of ultrapure water. Based on the analysis results of standard solutions, a five-level calibration curve was created. The concentration at each calibration level (fluoride ion concentration in adsorbent solution) was calculated as: prepared concentration × sample combustion volume (0.2 mL) / adsorbent solution volume (11.1 mL). The calibration curve was plotted as a straight line, and it was verified that the recovery rates (%) calculated from the set concentrations and measured concentrations at all calibration levels range within 80–120% specified in EPA 1621. Table 2 shows the set concentration, measured concentration, and recovery rate for each calibration level. Fig. 3 Analytical schedule creation window Conc. (mg/L) Calibration levels (µg/L) Measured Conc. (µg/L) Recovery(%) 0.1 1.8 1.717 95.4 0.5 9.0 8.926 99.2 1.0 18 17.847 99.2 10.0 180 180.503 100.3 25.0 450 449.807 100.0 Table 2 Measured concentration and recovery of each calibration level Using the measured values shown in Table 2, we calculated relative standard error (RSE) according to the following formula. The RSE was 2.7%, which was less than the criterion of 20% specified in EPA 1621. xi = Nominal concentration (true value) of each calibration standard x´i = Measured concentration of each calibration standard n = Number of standard levels in the curve p = Type of curve (2 = linear, 3 = quadratic)  = 100 × � =1 ′  −   2 − Verification of initial performance Calculation of the Retention Time Window EPA 1621 requires the establishment of an allowable retention time range (retention time window). This range is set based on the results of three analyses of standard solution for calibration curve. Then average retention time ± 3-fold of standard deviation is defined as retention time window. In this article, the retention time window was calculated as ±0.1 min based on the results of three analyses of the sodium fluoride standard solution. IPR EPA 1621 requires that, as the verification of initial performance, the relative standard deviation (RSD) of measured concentrations from four consecutive analyses of PFHxS standard solution shall be less than 20%, and that the average recovery rate shall be within 80–120%. Both results were verified to be within the specified ranges. Fig. 4 shows the chromatogram of the PFHxS fluoride ion standard solution of 25 µg/L. 0.0 5.0 10.0 15.0 20.0 25.0 min 0.0 5.0 10.0 15.0 µS/cm F (3) Instrument status monitoring (2) Current line being executed and analysis start time (1) Remaining time to complete analysis Fig. 4 Chromatogram of PFHxS standard solution
Application News Analysis of unknown sample The performance of the analytical system for each analytical batch shall be verified when analyzing unknown samples. First, it shall be verified that the recovery rates are within 80–120% and the retention times are within the retention time window calculated in the “verification of initial performance” step (Calibration Verification) through quantitative determination of the calibration standard solution using the calibration curve created in the “Creation and evaluation of calibration curve”. The method blank shall be prepared using the same procedure described above and it shall be verified that the quantified concentration is less than 4.0 µg/L (Method Blank). Furthermore, it shall be verified that the recovery rate for PFHxS standard solution of known concentration is within the range of 70–130% (Ongoing Precision and Recovery, OPR). Furthermore, when analyzing unknown samples, a matrix-spiked sample (Matrix Spike, MS) and its duplicate (Matrix Spike Duplicate, MSD) shall be analyzed to verify that the retention times are within the retention time window and within ±0.2 min of the retention time during the verification of initial performance, that the spiked recovery rate is within 50– 150%, and that the Relative Percent Difference (RPD) is within 30%. The analytical procedure is shown below. (1) Boat Blank Measurement (at least 2) (2) Calibration Verification (Low-level) (3) Method Blank Measurement (4) OPR Measurement (5) Samples (10 or fewer) (6) Matrix Spike Measurement (7) Calibration Verification (Mid-level) (8) Samples (10 or fewer) (9) Calibration Verification (Mid-level) Result Criterion RSD for AOF concentration(%) 2.07 ≦20 Average Recovery (%) 94.8 80-120 AOF(µg/L)=C MB × V abs V MB 0.0 5.0 10.0 15.0 20.0 25.0 min -5.0 0.0 5.0 10.0 2.0 3.0 4.0 min -0.1 0.0 0.1 F µS/cm µS/cm F Result Criterion Method Blank (µg/L) 0.57 < 4.0 MDL b =x+ t (n-1,1-α=0.99) S b MDL S =t (n-1,1-α=0.99) S S MDL b MDL S MDL ML 0.74 1.16 1.16 5 ML=MDLx3.18 On the C-IC Solution analysis screen (Fig. 5), the fluoride ion concentration (IC concentration) measured by ion chromatograph is automatically converted to the concentration in the sample. Both the IC concentration and the concentration in the sample are simultaneously confirmed on the same screen. The quantitative results (not shown in the table) were calculated by converting them to AOF concentrations (µg/L) in the solution before the activated carbon treatment in accordance with the procedure described in EPA 1621. The conversion formula is shown below, and Table 3 presents the repeatability and recovery rate of AOF concentration (µg/L) from four consecutive analyses of the PFHxS standard solution. MDL and ML To verify the presence of fluoride ions originating from reagents and equipment used in the pretreatment process, 100 mL of ultrapure water was passed through activated carbon and subjected to the same pretreatment as the sample (method blank). Fig. 6 shows the chromatogram of the method blank, and Table 4 presents its quantitative result. The EPA 1621 standard specifies that the quantitative result for the method blank must not exceed 4.0 µg/L, and it was confirmed that the sample met this criterion. Furthermore, it is stated that the ML calculated using the following equation shall be reported after rounding off to make a form as 1, 2, or 5 × 10n (where n is 0 or integer). In this article, the ML is reported as 5 since the calculation resulted in 3.7. The calculated results for the MDL and the ML are shown in Table 5. AOF = Concentration of adsorbable organic fluorine in μg F-/L C MB = Method blank measured concentration (sum of top and bottom GAC) reported without volume corrections V abs = Total volume of absorption solution in mL of the sample prior to injection to IC V MB = Volume in mL of method blank adsorbed Fig. 5 Data analysis screen of C-IC Solution Table 3 IPR calculation result Table 4 Determination result of method blank Fig. 6 Chromatogram of method blank In EPA 1621, MDL was calculated in accordance with the description of method procedure and 40 CFR Appendix B to Part 136 2) . In this method, MDL is defined as the greater of MDL b , which is calculated from the result of consecutive analyses of the method blank and MDL S , which is calculated from the result of consecutive analyses of 25 µg/L of PFHxS standard solution. The formula used to calculate MDLb and MDLS is shown below. Table 5 MDL and ML (µg/L) MDL b = the MDL based on method blanks X = mean of the method blank results t (n−1, 1α= 0.99) = the Student's t-value appropriate for the single-tailed 99th percentile t statistic and a standard deviation estimate with n−1 degrees of freedom. S b = sample standard deviation of the replicate method blank sample analyses. MDL s = the method detection limit based on spiked samples t (n-1, 1−α= 0.99) = the Student's t-value appropriate for a single-tailed 99th percentile t statistic and a standard deviation estimate with n-1 degrees of freedom. S s = sample standard deviation of the replicate spiked sample analyses. C-IC Solution contains QC evaluation function that determines whether the analytical results meet the criteria specified in EPA 1621 or not, enabling support for analyses that are in accordance with testing requirements. Both MS and MSD met the retention time criterion, verifying that the retention time window set during the verification of initial performance was appropriate (Fig. 7). Fig. 7 QC examination result screen of C-IC Solution
Application News www.shimadzu.com/an/ Shimadzu Corporation © Shimadzu Corporation, 2026 For Research Use Only. Not for use in diagnostic procedures. This publication may contain references to products that are not available in your country. Please contact us to check the availability of these products in your country. The content of this publication shall not be reproduced, altered or sold for any commercial purpose without the written approval of Shimadzu. See https://www.shimadzu.com/about/trademarks/index.html for details. Third party trademarks and trade names may be used in this publication to refer to either the entities or their products/services, whether or not they are used with trademark symbol “TM” or “”. Shimadzu disclaims any proprietary interest in trademarks and trade names other than its own. The information contained herein is provided to you "as is" without warranty of any kind including without limitation warranties as to its accuracy or completeness. Shimadzu does not assume any responsibility or liability for any damage, whether direct or indirect, relating to the use of this publication. This publication is based upon the information available to Shimadzu on or before the date of publication, and subject to change without notice. First Edition: Oct. 2026 01-01285-EN Nexera, Shim-pack, and ICDS are trademarks of Shimadzu Corporation or its affiliated companies in Japan and/or other countries. Fig. 9-11 show chromatograms of river water, matrix-spiked samples (MS) in which PFHxS standard solution was added to river water to make fluoride ion concentration of 25 µg/L in the sample solution, and sample (MSD) obtained by diluting the MS within the calibration curve range. In this analysis, the dilution factor for the MSD was set to 2.5. Conclusion In this article, AOF was successfully determined in accordance with EPA 1621 using C-IC system consisting of AQF-5000H automatic combustion unit Nittoseiko Analytech and the Nexera IC ion chromatograph from Shimadzu. The system demonstrated excellent precision and recovery performance in the IPR test, confirming its suitability for reliable AOF screening. Beyond analytical performance, the combination of the AQF- 5000H, Nexera IC, and C-IC Solution provides a streamlined workflow from combustion and IC analysis to data processing and quality control evaluation. Through a single software platform, users can centrally control the entire CIC system, automate EPA 1621-compliant analytical sequences, and simplify QC assessment. This integrated workflow helps improve laboratory efficiency, reduce manual operations, and support consistent, reliable AOF analysis. References 1) EPA 1621 Screening Method for the Determination of AOF in Aqueous Matrices by CIC 2) 40 CFR Appendix B to Part 136—Definition and Procedure for the Determination of the Method Detection Limit—Revision 2 0.0 5.0 10.0 15.0 20.0 25.0 min 0.0 5.0 10.0 15.0 20.0 µS/cm F 3.0 4.0 min -0.2 0.0 0.2 0.4 µS/cm F 0.0 5.0 10.0 15.0 20.0 25.0 min 0.0 5.0 10.0 15.0 0.0 5.0 10.0 15.0 20.0 25.0 min 0.0 5.0 10.0 15.0 µS/cm F µS/cm F Measured Conc. (µg/L) Recovery(%) RPD *1 Sample 0.925 -- -- MS 24.1 92.6 -- MSD 25.6 98.7 6.3 RPD= MS−MSD MS+MSD /2 ×100 EPA 1621 specifies that the spiked recovery and RPD must be calculated based on these analytical results. The determined concentration in MSD was converted to the concentration of the undiluted solution prior to the 2.5-fold dilution, and the RPD was calculated using the following formula. The calculated recovery rate and RPD are shown in Table 6. QC evaluation can be performed easily by just entering the values calculated during the verification of initial performance—such as the retention time window—into the settings because the recovery rate and RPD are automatically calculated (Fig.8). Fig. 8 QC examination setting window of C-IC Solution Fig. 9 Chromatogram of river water Fig. 10 Chromatogram of MS Fig. 11 Chromatogram of MSD (2.5-fold diluted) MS = Percent recovery of the MS MSD = Percent recovery of the MSD Table 6 measured concentration, recovery rate, and RPD *1:RPD was calculated using the recovery rates before rounding off
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