Determination of BTEX in Cigarette Filter Fibers Using GC-MS with Automated Calibration

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Determination of BTEX in Cigarette Filter Fibers Using GC-MS with Automated Calibration Zhang Xuebin 1, Yu Chongtian 1, Liang Lina 1, Hans-Joachim Huebschmann 2, Thermo Fisher Scientific Shanghai, 1 China, 2 Singapore Application Note 1399 Keywords: Tobacco, cigarettes, C-fiber filter, BTEX, automated calibration, GC-MS Introduction Benzene and its alkyl derivatives toluene, ethylbenzene, and xylene (BTEX) have been classified by the World Health Organization (WHO) as a strong carcinogens causing cancer affecting human skin, lungs, and the nervous system. [1] Quality control in the cigarette filter manufacturing process is a critical procedure for the tobacco industry. The reagents, accessories and raw filter material used in the production process may be a source of residual BTEX contamination, and hence require quality control. Therefore, the BTEX monitoring of cigarette filters in the tobacco industry has a significant impact on the choice and quality of filter materials. China is by far the largest tobacco producing country today, followed from a distance by Europe, North America and Latin America. [2] In China, the directive YC/T 373-21 for the control of propylene and C-fiber filter material requires the analysis of BTEX residue contaminations by gas chromatography-mass spectrometry (GC-MS). [3] The YC/T 373-21 standard has high sensitivity requirements for the detection of BTEX. In this application note, we employ the method used in YC/T 373-21 with the Thermo Scientific TM ISQ TM GC-MS for detection of BTEX compounds in propylene fiber cigarette filters. Figure 1. TriPlus RSH robotic sample handler with automated calibration dilution cycle.

2 Sample Preparation Calibration Preparing calibration solutions for BTEX analysis is typically a manual procedure. The low boiling point of the BTEX compounds makes precise low volume pipetting and diluting of a BTEX stock solution into vials particularly critical due to their volatility. In addition, handling such volatile carcinogenic compounds presents a serious health risk for the operators. The procedure described in this application note utilizes the Thermo Scientific TM TriPlus TM RSH autosampler platform to prepare the BTEX calibration standard series and then to seamlessly perform the injection into the GC-MS system. The autosampler allows fully automated calibration and sample measurement with minimal contact between the analyst and potentially hazardous materials. Experimental Conditions Carry out BTEX analyses using an ISQ single quadrupole system, equipped with the Thermo Scientific TM TRACE TM 131 GC and a TriPlus RSH autosampler with an automated tool changer and vortexing unit as described in Figure 1. Use the detailed configuration provided in Table 1. Figure 2 illustrates the preparation of the calibration dilution levels using dedicated syringes, which are automatically changed by the TriPlus RSH as required by the liquid handling cycle. Use the analytical conditions provided in Tables 2 and 3. Table 1. TriPlus RSH autosampler configuration used for automated BTEX analysis. Automatic tool changer Syringe tool D7 (1 µl used for dilutions) Syringe tool D7 (1 µl dedicated for GC injection) Syringe tool D8 (1 µl used for dilutions) Vortexer (for vial mixing before injections) Large washing station (2 1 ml solvent) Standard washing station (2 1 ml) Tray holder Vial tray VT4 (3 pcs, for 2 ml vials) Cooled tray recommended if the lab temperature goes above 2 Preparation of Standard Solutions The reagents and reference standards mix comprised of benzene, toluene, ethylbenzene, o-xylene, m-xylene, and p-xylene was purchased locally from Sinopharm Chemical Reagent Co. Ltd. 2-hexanone was purchased from Beijing J&K Technology Co. Ltd. n-pentane, extra pure, from Fisher Scientific was also used. Figure 2. Schematics of the calibration dilution cycle. Dedicated syringes are used for standards, solvent and injection. Automated Calibration Dilution Cycle Use the built-in automatic dilution liquid handling cycle of the TriPlus RSH autosampler to prepare the calibration. This function automatically prepares the required calibration level solutions in 2 ml vials (VT4 sample tray type) and adds the internal standard. Inject the prepared calibration standard dilutions before analyzing the samples controlled by the acquisition sequence. Prepare up to three replicates of the calibration samples. See the available vial positions in Figure 3. Program the TriPlus RSH automatic calibration dilution cycle to prepare seven additional vials with the concentration levels of 1., 2.,., 1., 2.,. and 1. using the BTEX standard mix. Use the initial 1. (.1 ppm) stock solution as a seventh calibration point. Clean the syringe using the large volume solvent station three times after each use. Place the following solutions and vials into the dedicated TriPlus RSH autosampler tray positions: - Place empty 2mL vials, capped with septum, on the sample tray, as the target vials receive the calibration dilutions for 1 Pos. 1, Pos. 2, 2 Pos. 3, 1 Pos. 4, Pos., 2 Pos. 6, 1 Pos. 7 - Place the BTEX stock solution with the standard mix with six compounds, ml,.1 ppm, in Pos. 4 of the solvent tray - Place blank solvent in Pos. 12 ISTD As required by the Chinese method, use 2-hexanone as the internal standard. Dilute mg of 2-hexanone with n-pentane to. ml for an initial 1 ppm internal standard solution. Dilute this solution to a concentration of.1 ppm 2-hexanone internal standard work solution, and use for standards preparation and sample extraction.

3 Table 2. TRACE 131 GC conditions. Column type Column dimensions Thermo Scientific TM TraceGOLD TM TG-WaxMS length 3 m, ID.2 mm, film thickness.2 μm (p/n 2688-142) Injector, temperature Instant connect split/splitless injector 24 C Injection mode, volume split injection, 3 µl Figure 3. TriPlus RSH VT4 sample tray positions for calibration dilution. Pos. 1 1 first calibration series Pos. 19 28 second calibration series Pos. 37 46 third calibration replicate Pos. 11, 29, 47 solvent with internal standard Pos. 12, 3, 48 solvent blank Pos. 4 internal standard Other positions not used Table 3. ISQ MS Conditions. Ionization EI, 7 ev Filament current µa Split flow 1 ml/min (ratio 1:1) Solvent vent open until.17 min closed until 4.17 min open until end of run Carrier gas, flow helium, constant flow 1 ml/min Oven program 3 C, 2 min C/min to 1 C 2 C/min to 22 C 22 C, 3 min Transfer line temperature 2 C Scan mode SIM, see Table 3 Acquisition rate.1 s Ion source temperature 28 C RT: 2.8-6.99 4 3 4.9 NL: 4.2E TIC MS 3 Relative Abundance 2 2 4.38.42.6 6.11 1 2.83 3.22 3.3 3.41 3.67 3.97 4.97.19 6.9 4.8.82 6.4 6.82 6.92 3. 3. 4. 4... 6. 6. Time (min) Figure 4. BTEX chromatogram of the standard mix,, ISQ GC-MS SIM. Sample Measurements For preparation of the samples, weigh about 3. g of the C-fiber filter rod (length of about 1 cm) into 6 ml bottles, adding. ml of the 2-hexanone internal standard stock solution at a concentration of.1 ppm. Close the bottle and shake at 2 rpm for 1 hour. Take the supernatant and filter over a.4 µm membrane and prepare in 2 ml vials for GC-MS analysis.

4 Table 4. BTEX ISQ SIM method-instrument and method detection limits (MDL) (* internal standard). Compound name CAS# Retention time Quantitation Ion Qualifier Ion Detection limit MDL [min] [m/z] [m/z] [] [] Benzene 71432 3.21 78 1 6 17 Toluene 18883 4.39 91 6 2 17 2-Cyclohexanone* 91786 4.9 8 1 - - Ethylbenzene 1414.42 91 16 2.2 17 p-xylene 9476.3 91 16 3.8 17 m-xylene 18383.6 91 16 2. 17 o-xylene 16423 6.11 91 16 2. 17 Results Figure 4 shows the ISQ GC-MS chromatogram of the six BTEX compounds at the standard mix concentration of. It shows that all components in the BTEX analysis were well resolved. The meta-, para-, and ortho-xylene isomers were baseline resolved in only 7 minutes. Each substance showed symmetrical peak shape and a solid base for reliable peak integration and determination, even at very low concentration levels. The method detection limit (MDL) of the described method for the six BTEX compounds was calculated based on the equation shown to the left in which M is the sample weight and C is the lowest calibration point. It is based on the assumption of a similar response for the six BTEX compounds and the use of ml of extraction solvent. See Table 4. 2 Benzene Y =.18629+.191377*X R^2 =.9994 W: Equal 2 Toluene Y =.7742+.22319*X R^2 =.999 W: Equal 1 2 1 2 4 6 8 1 2 4 6 8 1 2 2 1 Ethylbenzene Y =.38983+.22743*X R^2 =.9994 W: Equal 2 1 P-xylene Y =.848+.196694*X R^2 =.999 W: Equal 2 4 6 8 1 2 4 6 8 1 M-xylene Y =.29939+.21342*X R^2 =.999 W: Equal O-xylene Y =.224333+.223*X R^2 =.9994 W: Equal 2 1 2 4 6 8 1 2 1 2 4 6 8 1 Figure. BTEX calibration curves in the range of 1. to 1 with R2 better than.999 for all compounds.

C-fiber filter rods provided by the tobacco industry were analyzed using the method described above. A recovery test was carried out using the prepared standard solution with a spiked amount of ng/ml ( ) in order to examine the reliability of the method. Due to a lack of confirmed blank fiber material, a previously determined low level sample was spiked. The recovery results of the spiked sample experiment are shown in Table. The results show that at the level the recoveries range between 82.% and 9.8% and are in line with values for daily analysis and detection requirements. The selected ion chromatograms of the spiked sample and a contaminated fiber rod sample are shown in Figure 6. The experimentally determined concentrations of the C-fiber filter rod had been calculated as: Benzene n.d. Toluene n.d. Ethylbenzene 42. ng/g p-xylene 16.8 ng/g m-xylene 2.2 ng/g o-xylene 28. ng/g Benzene and toluene were not detected (n.d.) with levels below the limit of quantification. Table. Recovery results from a spiked sample. Compound name Sample measured Standard addition Spiked calculated Spiked measured Recovery [] [] [] [] % Benzene.. 4.4 9.8 Toluene.21..21 4.43 84.4 Ethylbenzene 2.2. 7.2 6.62 82. p-xylene 1.1. 6.1.49 89.6 m-xylene 3.13. 8.13 7.19 81.2 o-xylene 1.71. 6.71.9 83.8 RT: 2.8-6.99 4.9 3 3 Relative Abundance 2 2 1.43.6 6.11 4.39.6 6.19 2.82 3.21 3.23.42 4.38 6.11 2.84 2.88 3.21 4.96 4.97 6.73 6.78 6.98 3.24 3.36 3.9 4. 4.82 4.73.6.93 3. 3. 4. 4... 6. 6. Time (min) Figure 6. Chromatograms of a sample (blue) and sample spike (red) (overlay, run with high peaks).

Conclusions This application note describes an easy-to-handle n-pentane solvent extraction method for the quality control of BTEX compounds in cigarette fiber filters using the TriPlus RSH autosampler and the TRACE 131 ISQ single quadrupole GC-MS system. This analytical method can also be applied to similar sample types. Very precise, correct, and freshly prepared calibration solutions for each batch of samples are provided by the automated calibration dilution function of the TriPlus RSH autosampler. This fully automated and optimized method provides short analysis cycle times for a more economical sample throughput. The need for fewer manual pipetting steps improves the method precision significantly for such highly volatile compounds. In addition, human contact with hazardous and carcinogenic compounds is minimized. References [1] G.D. Byrd, K.W. Fowler, R.D. Hicks, M.E. Lovette, M.F. Borgerding, Isotope dilution gas chromatography-mass spectrometry in the determination of benzene, toluene, styrene and acrylonitrile in mainstream cigarette smoke, J. Chromatogr. A (199) 3, 39-368. [2] Food and Agriculture Organization of the United Nations, Projections of tobacco production, consumption and trade to the year 21, Rome, 23. [3] People's Republic of China tobacco industry standards, YC / T 373-21, measuring propylene filament bundles and C-fiber filter rod benzene, toluene, ethylbenzene and xylene residue by gas chromatography-mass spectrometry. Application Note 1399 This analytical method provides high BTEX compound recovery with a wide method linearity and high sensitivity. The linear concentrations cover seven concentration levels in the automatic preparation of samples in the 1-1 range, with precision greater than.999 for all compounds. The detection limits of BTEX compounds are 2.-6. (ng/g) with quantification limit of the method at 17 (ng/g). Recoveries were determined to be 82.-9.8%. The described analytical ISQ GC-MS method and its resulting performance data readily meet the high routine analytical testing requirements of the tobacco industry. www.thermoscientific.com 214 Thermo Fisher Scientific Inc. All rights reserved. ISO is a trademark of the International Standards Organization. All other 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 representative for details. Thermo Fisher Scientific, Austin, TX USA is ISO 91:28 Certified. Africa +43 1 333 34 Australia +61 3 977 43 Austria +43 81 282 26 Belgium +32 3 73 42 41 Canada +1 8 3 8447 China 8 81 118 (free call domestic) 4 6 118 Denmark +4 7 23 62 6 Europe-Other +43 1 333 34 Finland +38 9 3291 2 France +33 1 6 92 48 Germany +49 613 48 114 India +91 22 6742 9494 Italy +39 2 9 91 Japan +81 4 43 91 Korea +82 2 342 86 Latin America +1 61 688 87 Middle East +43 1 333 34 Netherlands +31 76 79 New Zealand +64 9 98 67 Norway +46 8 6 468 Russia/CIS +43 1 333 34 Singapore +6 6289 119 Spain +34 914 84 96 Sweden +46 8 6 468 Switzerland +41 61 716 77 UK +44 1442 233 USA +1 8 32 472 AN1399