ORGANIC ALKALI METAL SALT ESTIMATION BY ICP-OES IN THERMOPLASTIC Rosa AD, SABIC Technology Center, Bangalore, India; Xu Jenny, Wen Liang, STC-Shanghai, China; Akshay Gouda, Benoi, Singapore; Lin Chen, Nansha, China. Abstract Thermoplastic based films are widely used for electrical and electronic (EE) insulation applications. For EE applications, high flame retardant properties are required with increasingly stricter regulations against chlorinated or brominated formulations. The ongoing research is focused on developing new grades with alternate flame retardant (FR) additives giving comparable VTM0 and V0 ratings. In order to deliver this excellent FR performance, one of the key factor is to control the loading of the FR additive (organic alkali metal salt) as per formulation during the production stage. Hence, there was a need to develop XRF based fast screening method that could be implemented in manufacturing sites for regular monitoring of additive loading in new grade of thermoplastic containing complex inorganic fillers. Establishment of XRF method requires generation of absolute standard values for the organic alkali metal salt with this new formulation. Analytical efforts were tried to extract the FR additive by two extraction techniques followed by analysis using instrumental techniques such as ion chromatography and LC-MS. However the results were not consistent due to insufficient extraction of the salt from the thermoplastic containing complex organic and inorganic matrix and other inorganic fillers due to adsorption issues. To overcome these challenges, absolute method using ICP-OES was developed to quantitatively estimate the potassium content in the organic alkali metal salt in this grade and back calculate the % FR additive. Specific formulations with known concentration of organic alkali metal salt were compounded and analyzed by ICP-OES to generate standard values which were used for XRF calibration. This presentation covers the development of successful XRF method based on ICPOES results. Details of method development approach, comparison of results obtained by two different techniques (ICP and XRF), translation and implementation of methods to manufacturing sites and detailed round robin studies at multiple manufacturing sites to validate the new method are discussed. Introduction The use of additive in thermoplastics always has an influence on the characteristics of the polymer, but the improvement of some of its properties is often accompanied by unfavorable side effects. In the case of some thermoplastics often the addition of small quantity of an additive may affect the optical characteristics and the transparency of the final product. Also the characteristics of the additive itself can limit its utilization. In the case of brominated flame retardants, increasing concern for environmental and health issues, is encouraging users to look for bromine and chlorine free flame retardants. This increases the interest of thermoplastic producers and compounders to find alternatives to these additives. The main objective of this study was to establish a standard curve in XRF for the FR additive in the new grade of thermoplastic. In order to deliver excellent UL performance, one of the key factor was to control the loading of the FR additive as per specification during the production stage. The FR additive is quantitatively characterized using a XRF method. In order to establish the XRF method for routine analysis of FR additive in the new grade, absolute quantification of FR additive was essential to build a calibration curve in XRF. In our efforts to develop quantification method, we first chose chromatographic techniques such as ion chromatography and LC-MS (1) by two different extraction techniques. The extraction methods used failed to extract the complete FR additive into the solvents used for extraction. The samples were then estimated for potassium by ICP-OES and back calculated for FR additive as it is a salt containing potassium. The ICP-OES data was accurate however due to inhomogeneity in the samples, consistent data was not obtained. Therefore an in-house formulation and compounding study by controlled conditions was carried out to obtain accurate results by ICP-OES. This report covers the result for the round robin study conducted with the absolute numbers generated by ICP-OES to validate the new ICP-OES method. Methodology For ion chromatography studies, two different extraction procedures were used to extract the FR additive into the solvents followed by ion chromatography. Extraction 1: Around 0.50 g sample was accurately dissolved in 10 ml chloroform for 1 hour or till the sample dissolved completely. Then 25 ml of water was added and shaken for 5 minutes and allowed for settling till chloroform and water layer separated. The aqueous layer was filtered and injected into IC. The instrument conditions used is as given below. Instrument used: Dionex ICS 3000, Column: AS 19 Ion Pac Analytical Column: 4 × 250 mm, Ion Pac AG19 Guard Column: and 4 × 50 mm, Eluent: 20mM KOH, Flow rate: 1.0 ml, Detector: Conductivity. SPE ANTEC™ Indianapolis 2016 / 1408 Extraction 2: Around 0.5 g sample was accurately dissolved in 5 ml chloroform and precipitated with 25 ml methanol. From this solution, 10ml of the methanol was filtered and evaporated and residue re-dissolved in 10 ml of water and injected into IC. The instrument conditions were same as followed for extraction 1. ICP for total potassium content: About 0.2 g of the sample was digested with 7 ml conc. nitric acid using Anton paar microwave digester. The solutions were analyzed for potassium using ICP-OES. The instrumental conditions were as follows. Instrument make: Spectro Cirros, Nebulizer- cross flow, Plasma power- 1400 W, Coolant flow14 l/min, Nebulizer flow- 0.8 l/min, auxiliary flow-1 l/min, calibration standards- 0.5 ppm to 5 ppm range, internal standard -1 ppm of scandium. ingredients. Microwave digestion was carried out for sample preparation and estimated total potassium using ICP–OES. The values obtained by the two extraction processes and also by ICP-OES Vs the formulation values are as shown in Figure 1. Discussion Figure 1: % FR additive recovery by IC, ICP-OES from actual loading from formulation FR additive estimation was carried out based on the report which was used to estimate the FR additive in thermoplastic without inorganic fillers. However, the formulation of the samples in our study contained complex inorganic fillers. Based on the solubility property of FR additive, it has solubility in water and also good solubility in methanol. In the first extraction method, water was used as solvent to extract and in the second extraction method, methanol was used for extraction. In all these samples there were inorganic fillers which remained undissolved in the solution after the sample dissolution in chloroform. The extracts were analyzed by ion chromatography. However the extraction process was not efficient enough to extract the complete FR additive into water or even methanol by both the extraction techniques due to adsorption properties of the additives. The values obtained from extraction 1 was only one third of the actual FR loading in the formulation. This indicated that the extraction was incomplete in water and hence extraction 2 process was followed. In this method, polymer was dissolved first in chloroform and reprecipitated with methanol in which the FR additive is known to have good solubility. This solution was evaporated to remove methanol and the residue was redissolved in water and injected into IC. By extraction method 2, values obtained were higher compared to extraction method 1 however the actual FR additive content as per formulation could not be extracted. All the extractions were carried out at room temperatures. ICP-OES, an elemental technique, was considered as both the extraction techniques failed to extract the FR additive completely into the extraction solutions. ICP-OES is a technique which can determine the total metals present in a sample at sub ppm levels. Since this FR additive is made of an organic alkali metal salt containing potassium, total potassium content estimation in the sample present can be back calculated to % FR additive, provided there is no contamination of potassium from other formulation The values based on total potassium by ICP-OES was higher than the two extraction techniques by IC by 2 to 3 times. However the values were still lower than the expected formulation values. Although ICP-OES is an absolute technique by which the absolute number could be estimated, however there was inhomogeneity in the sample due to which inconsistent readings were obtained. Therefore an in-house formulation and compounding with small batch (100 g) was carried out to understand how the distribution happens during mixing and compounding. 5 batches were formulated and compounded and FR additive was analyzed by ICP-OES. Batches 1, 2, 3 had FR additive in formulation whereas the batch 4 and batch 5 did not contain FR additive. The results of first three batches were close to the formulation values which was above 93% of actual loading. Batches 4 & 5 and also plain thermoplastic did not show any presence of potassium by ICP-OES, indicating that the other formulation ingredients do not contain potassium as contaminant. If the mixing and compounding is done under controlled conditions, the FR additive distribution in the sample can be controlled and accurate results can be obtained as shown in Figure 2. Figure 2: % FR additive recovered based on ICP-OES from in-house formulation with 100g batch SPE ANTEC™ Indianapolis 2016 / 1409 This study generated the values of FR additives to be used as standards for generating standard calibration by XRF (2). The values were repeatable with standard deviations between 0.006 to 0.01. Based on these data, 10 more samples were re-compounded and absolute values for FR additive were generated by ICP-OES. The values lied between 80 to 88 % of the actual loading but with good standard deviation as given in Table 1. The Z-score test indicated the data lies within allowable limit (±2) thus validating the round robin as shown in Figure 4. Table 1: % of FR measured by ICP-OES with standard deviation % Recovery of FR from formulation std dev Sample 1 80 0.001 sample 2 79 0.005 Sample 3 88 0.015 Sample 4 87 0.012 Sample 5 83 0.013 Sample 6 83 0.036 Sample 7 84 0.021 Sample 8 79 0.006 Sample 9 88 0.011 Sample 10 83 0.005 These results were used as calibration values in XRF and it was translated to 5 manufacturing sites. To validate the calibrations set up in XRF at the different sites based on the values generated by ICP-OES, an unknown sample was analyzed using the new calibration at all sites and the same was analyzed by using ICP-OES (3). The values of all the sites were very close to the actual loading of FR both by XRF and ICP-OES as shown in Table 2. Table 2: % of FR data match with the unknown sample by XRF and ICP-OES Site 1 (XRF) Site 2 (XRF) Site 3 (XRF) Site 4 (XRF) Site 5 (ICP-OES) % match 93 95 96 93 96 std dev 0.004 0.005 0.006 0.005 0.170 Statistical tools were used to evaluate the data obtained from across the sites. Homogeneity of variance test was used to see variances are equal across groups or samples. The Levene test was used to verify that assumption. The homogeneity of variance test showed the P value greater than 0.05 (0.096) indicating there is no significant variation between the values as shown in Figure 3. Figure 4: Z-score statistical analysis Z scores (4) are measures of standard deviation. This distribution relates standard deviations with probabilities and allows significance and confidence to be attached to Z scores and p-values. The statistical tools further validated the method adopted for the estimation of FR additive. Conclusions In summary, a method was developed to accurately estimate FR additive concentration in thermoplastic formulations containing inorganic fillers. It was observed that while the FR additives estimation in neat thermoplastic was straight forward, the presence of inorganic fillers in formulations inhibited the complete extraction and estimation of the FR additives due to adsorption. This issue is compounded if the samples are not homogeneous in nature (well mixed and compounded). To address and understand this issue, inhouse formulation and compounding studies were carried out. ICP-OES was used to estimate total potassium content as this FR additive is an organic salt containing potassium. The potassium values were used to back calculate the % FR additive. The results generated by ICP-OES was used as calibration standards for XRF. This method would enable the preparation of similar formulations for improved FR performance. References 1. 2. 3. 4. Figure 3: Homogeneity of variance test C. Wold and R. Grampel, Polymer testing 28 495-499 (2009). H. A. van Sprang, Fundamental parameter methods in XRF Spectroscopy, Advances in XRay Analysis 42 (2000) T. R. Crompton, Polymer Reference book, Smithers Rapra Publishing, (2006). L.P. Van Reeuwijk and V.J.G. Houba, Guidelines for Quality Management in Soil and Plant Laboratories. (FAO Soils Bulletin - 74), (1998). SPE ANTEC™ Indianapolis 2016 / 1410
© Copyright 2026 Paperzz