Characterization of polymers by py-GC-MS

This metal screening analysis includes the semi-quantitative determination of 70 elements. The method can be used, for example, to determine the background concentrations of metals in environmental samples or to study the elemental distribution of unknown samples. Screening is also often performed to assess which metals should be analyzed by a quantitative method. The measurement is performed using a high-resolution ICP-MS technique (ICP-SFMS), which can identify very low elemental concentrations. A semi-quantitative determination of the following elements is included: Ag, Al, As, Au, B, Ba, Be, Bi, Br, Ca, Cd, Ce, Co, Cr, Cs, Cu, Dy, Er, Eu, Fe, Ga, Gd, Ge, Hf, Hg, Ho, I, Ir, K, La, Lu, Mg, Mn, Mo, Na, Nb, Nd, Ni, Os, P, Pb, Pd, Pr, Pt, Rb, Re, Rh, Ru, S, Sb, Sc, Se, Si, Sm, Sn, Sr, Ta, Tb, Te, Th, Ti, Tl, Tm, U, V, W, Y, Yb, Zn and Zr. However, please note that some elements may not be determinable due to matrix interference. During this semi-quantitative analysis, the instrument is calibrated for about 30 elements and the rest of the analytes are quantified using sensitivity factors for calibrated elements with similar mass and first ionization potential considering isotope abundances. Quantitative analysis is also available at an additional price. During this analysis, all elements are calibrated (excluding halogens and Os). Please ask for an offer for this service.

Determination of carbon, hydrogen, nitrogen, sulfur, and oxygen content of an organic sample. CHNS analysis (”LECO analysis”) is performed using a flash combustion method, where the sample is combusted under 25 kPa of O2 at an elevated temperature (1000 °C), followed by gas chromatography separation and detection using a thermal conductivity detector. Oxygen is analyzed by reduction on granulated carbon at 1480 °C, utilizing high-temperature thermal decomposition and conversion of oxygen into carbon monoxide before gas chromatography separation and detection with a thermal conductivity detector. The sample can be either solid or liquid, but water in the sample affects the results. In the case of aqueous samples, it is possible to dry the sample before analysis. The price includes two parallel measurements. The results are reported as wt-% of the initial sample. The ash, drying and dry loss measurements will increase the minimum required sample material need to 300 mg. The analysis gives the total carbon, hydrogen, nitrogen, sulfur, and oxygen content of the material, but it does not identify any chemical structures. The measurement can be combined with other methods, such as GC-MS, 1H, and 13C NMR, to perform substance structure identification. Possible element packages: O, CHNS, and CHNOS.

This analysis provides quantitative information about the crystalline and amorphous phases within your sample using high-resolution synchrotron X-ray diffraction (XRD). A standard analysis includes: Quantification of crystalline phases as weight percentages, Quantification of the total amorphous content, High-resolution powder diffraction data and the resulting diffractogram, A comprehensive test report detailing the findings. For more advanced needs, we also offer total scattering/pair distribution function (PDF) analysis to reveal the local atomic structure in amorphous or nano-structured materials.

GC-MS analysis of 16 PAH compounds, which are listed as high-priority pollutants by the U.S. Environmental Protection Agency (EPA). The analyzed PAH compounds are: naphthalene [CAS: 91-20-3], acenaphthylene [CAS: 208-96-8], acenaphthene [CAS: 83-32-9], fluorene [CAS: 86-73-7], phenanthrene [CAS: 85-01-8], anthracene [CAS: 120-12-7], fluoranthene [CAS: 206-44-0], pyrene [CAS: 129-00-0], benz(a)anthracene [CAS: 56-55-3], chrysene [CAS: 218-01-9], benzo(b)fluoranthene [CAS: 205-99-2], benzo(k)fluoranthene [CAS: 207-08-9], benzo (a) pyrene [CAS: 50-32-8], dibenzo(ah)anthracene [CAS: 53-70-3], benzo (ghi) perylene [CAS: 191-24-2], indeno (123cd) pyrene [CAS: 193-39-5].

Total oxidizable precursor (TOP) assay can be used when estimating the presence of PFAS precursors and intermediates by oxidizing them into stable end-products. The analysis can be combined with traditional PFAS analysis methods to obtain additional information. The following are examples of compounds that can be analyzed: Abbreviation Compound CAS number PFBA perfluorobutanoic acid 375-22-4 PFPeA perfluoropentanoic acid 2706-90-3 PFHxA perfluorohexanoic acid 307-24-4 PFHpA perfluoroheptanoic acid 375-85-9 PFOA perfluorooctanoic acid 335-67-1 PFNA perfluorononanoic acid 375-95-1 PFDA perfluorodecanoic acid 335-76-2 PFUnA; PFUdA perfluoroundecanoic acid 2058-94-8 PFDoA perfluorododecanoic acid 307-55-1 PFTrDA; PFTriA perfluorotridecanoic acid 72629-94-8 PFTeA perfluorotetradecanoic acid 376-06-7 PFHxDA perfluorohexadecanoic acid 67905-19-5 PFODA perfluorooctadecanoic acid 16517-11-6 PFBS perfluorobutanesulfonic acid 375-73-5 PFPeS perfluoropentanesulfonic acid 2706-91-4 PFHxS perfluorohexanesulfonic acid 355-46-4 PFHpS perfluoroheptanesulfonic acid 375-92-8 PFOS perfluorooctanesulfonic acid 1763-23-1 PFNS Perfluorononanesulfonic acid 68259-12-1 PFDS perfluorodecanesulfonic acid 335-77-3 PFUnDS perfluoroundecanesulfonic acid 749786-16-1 PFDoS perfluorododecanesulfonic acid 79780-39-5 HFPO-DA (Gen X) 2,3,3,3-Tetrafluoro-2-(heptafluoropropoxy)propanoic acid 13252-13-6 HFPO-TA perfluoro-2,5-dimethyl-3,6-dioxanonanoic acid 13252-14-7 DONA; ADONA 4,8-dioxa-3H-perfluorononanoic acid 919005-14-4 PFMOPrA perfluoro-3-methoxypropanoic acid 377-73-1 NFDHA perfluoro-3,6-dioxaheptanoic acid 151772-58-6 PFMOBA perfluoro-4-methoxybutanoic acid 863090-89-5 PFecHS cyclohexanesulfonic acid, 1,2,2,3,3,4,5,5,6,6-decafluoro-4-(1,1,2,2,2-pentafluoroethyl)-, potassium salt (1:1) 335-24-0 3:3 FTCA 2H,2H,3H,3H-perfluorohexanoic acid 356-02-5 5:3 FTCA 2H,2H,3H,3H-perfluorooctanoic acid 914637-49-3 7:3 FTCA 2H,2H,3H,3H-perfluorodecanoic acid 812-70-4 PFEESA perfluoro(2-ethoxyethane)sulfonic acid 113507-82-7 6:2 Cl-PFESA; 9Cl-PF3ONS 9-chlorohexadecafluoro-3-oxanonane-1-sulfonic acid 756426-58-1 8:2 Cl-PFESA; 11Cl-PF3OUdS 11-chloroeicosafluoro-3-oxaundecane-1-sulfonic acid 763051-92-9 4:2 FTSA; 4:2 FTS 4:2 fluorotelomer sulfonic acid 757124-72-4 6:2 FTSA; 6:2 FTS 6:2 fluorotelomer sulfonic acid 27619-97-2 8:2 FTSA; 8:2 FTS 8:2 fluorotelomer sulfonic acid 39108-34-4 FBSA perfluorobutane sulfonamide 30334-69-1 FHxSA perfluorohexanesulfonamide 41997-13-1 FOSA perfluorooctanesulfonamide 754-91-6 MeFOSA; N-MeFOSA n-methylperfluorooctanesulfonamide 31506-32-8 EtFOSA; N-EtFOSA n-ethylperfluorooctanesulfonamide 4151-50-2 MeFOSE n-methylperfluorooctanesulfonamidoethanol 24448-09-7 EtFOSE n-ethylperfluorooctanesulfonamidoethanol 1691-99-2 NMeFOSAA; MeFOSAA n-methylperfluorooctanesulfonamidoacetic acid 2355-31-9 NEtFOSAA; EtFOSAA n-ethylperfluorooctanesulfonamidoacetic acid 2991-50-6 FOSAA perfluorooctane sulfonamidoacetic acid 2806-24-8 10:2 FTS 10:2 Fluorotelomer sulfonic acid 108026-35-3 The analysis is suitable for different matrices, such as water and fire-fighting foams. Contact us for more information and a quote for analyzing your samples.

Lignin sample ash content measurement at 525°C. The result is expressed as a mass percentage of the ash from the initial sample on a dry matter basis.

Analysis to screen a material for the presence of brominated fire retardants (BFRs), including polybrominated biphenyls (PBBs) and polybrominated diphenyl ethers (PBDEs). The test is performed with a pyrolysis gas-chromatography mass spectrometer (py-GC-MS) according to the ISO 7270-1 standard. The sample is pyrolyzed, which is followed by separation and identification with GC-MS. The obtained pyrogram is then compared to a blank sample that does not contain any brominated fire retardants. We also offer the analysis for electrotechnical products as per IEC 62321-6. Please ask our experts for more information about this option.

Determination of Be, Ba, Co, Al, Mg, Cu, Li, Mn, Ag, Sn, Ti, V, Zn, Tl, B, Hg, Mo, Fe, Ca, K, U, P, Cd, Na, Cr, Ni, Pb, Sb, As, and Se in water samples with ICP-MS-technique. The sample is homogenized and acidified (HNO3), after which the analysis is performed from the liquid phase. The analysis is suitable for natural waters. If the sample contains a lot of solids or the matrix is significantly different from natural water (for example waste and industrial waters), please contact our testing expert and ask for an offer. The concentration of each element is reported in µg/l.

Analysis of gaseous samples using Raman spectroscopy.

Determination of volatile organic compounds (VOC) in water using the GC-MS technique. The analysis determines the concentrations of 67 volatile compounds including BTEX, DIPE, ETBE, MTBE, TAEE, TAME, and TBA. The results of the analysis are reported in µg/l.