Persistent Organic Pollutants (POP) for Regulation (EU) 2019/1021

This analysis package covers the persistent organic pollutants (POPs) most relevant to plastic waste and recyclates, including plastics from waste electrical and electronic equipment (WEEE). The package is designed to support risk assessments under the POPs Regulation (EU) 2019/1021. The analysis is divided into the following subsets: Polybrominated diphenyl ethers (PBDEs), Hexabromocyclododecane (HBCDD), Short- and medium-chain chlorinated paraffins (SCCPs and MCCPs), Polychlorinated biphenyls (PCBs), dioxins and furans, Dechlorane Plus, UV-328. Individual subsets can be ordered on their own or in any combination at a reduced price. A package covering all POPs listed in Regulation (EU) 2019/1021 is also available. Solid samples must be ground before analysis. Milling can be provided at an additional cost, but it will extend the turnaround time.

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].

Determination of dissolved hormones and pharmaceuticals in wastewater by UPLC-MS/MS according to ISO 21676, or by an in-house LC method. Samples must be stored and shipped below 8°C after sampling to preserve analyte stability. The analysis covers more than 150 pharmaceutical and hormone compounds, all with a typical LOQ of 0.1 µg/l. Examples include: Estriol, Ethinyl estradiol, 17β-Estradiol, Estrone, Sulfadiazine, Fenbendazole, Norfloxacin, Ofloxacin, Ciprofloxacin. The full list of analytes is available upon request. The method is commonly applied to monitor wastewater treatment performance, assess environmental emissions of pharmaceutical residues, and support monitoring under EU water quality frameworks.

Determination of the following elements in wastewater and water solutions with high solid matter content with ICP-OES/MS (AFS is used for Hg measurement): Element LOQ (µg/L) Ag 1 Al 5 As 1 B 10 Ba 1 Be 0.2 Ca 50 Cd 0.2 Co 0.5 Cr 5 Cu 1 Fe 5 Hg 0.05 K 15 Li 1 Mg 10 Mn 0.5 Mo 1 Na 30 Ni 3 P 20 Pb 1 Sb 1 Se 5 Sn 1 Ti 5 Tl 0.5 U 0.1 V 5 Zn 2 The sample is digested with HNO3 in an autoclave before analysis. Detection limits may vary depending on sample properties. This method is suitable for wastewater samples that are relatively neutral (pH ~ 5-9). If the sample material is more acidic or alkaline, please select "Elemental analysis of liquid chemicals and process liquids by ICP-SFMS" instead of this method. An express turnaround option (~1 week) is available for a 50% surcharge. Ask our experts for more information through the form below.

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. 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.

Simultaneous determination of the following elements in water samples with the ICP-MS technique (AFS is used for Hg): Element LOQ (µg/L) Ag 1 Al 5 As 1 B 10 Ba 0.5 Be 0.2 Ca 50 Cd 0.02 Co 0.5 Cr 0.2 Cu 1 Fe 2 Hg 0.005 K 50 Li 1 Mg 3 Mn 0.5 Mo 1 Na 30 Ni 2 P 50 Pb 0.5 Sb 0.05 Se 1 Sn 1 Ti 1 Tl 0.5 U 0.1 V 1 Zn 2 The sample is homogenized and acidified (HNO3), after which the analysis is performed from the liquid phase. The displayed price applies to natural waters (for example, river or lake water). If the sample contains a lot of solids or the matrix is otherwise significantly different from natural water (for example, wastewater and industrial water), different analysis methods need to be used, which will affect the price and the quantification limits. The concentration of each element is reported in µg/l.

Pyrolysis gas chromatography-mass spectrometry (py-GC-MS) analysis to determine the identity of an unknown polymer sample. During the measurement, the sample is instantaneously heated in an inert atmosphere or vacuum. This causes the sample to decompose into smaller molecular fragments, which are then analyzed with GC-MS. Different types of polymers can be identified by their unique decomposition products. This includes, but is not limited to: PE, PP, PS, ABS, PMMA, PET, PC, PVC, polyamides, natural & synthetic rubbers, and more. The price includes the basic preparation and qualitative analysis of the sample. More extensive sample preparation and quantitative analyses are subject to additional costs.

Determination of selected volatile organic compounds (VOC) in water using the GC-MS and GC-FID techniques. Analysis can be conducted according to the following standard methods: EPA 624, EPA 5021A, EPA 8260, EPA 8015, EN ISO 10301, ISO 11423-1, and EN ISO 15680 The results of the analysis are reported in µg/L. Analysis includes the following analytes: Analyte: Reporting limits: chloromethane 1 µg/l bromomethane 1 µg/l dichloromethane 0.1 µg/l dibromimetaani 1 µg/l bromochloromethane 2 µg/l trichloromethane (chloroform) 0.1 µg/l tribromomethane (bromoform) 0.2 µg/l bromodichloromethane 0.1 µg/l dibromochloromethane 0.1 µg/l sum 4 trihalometanit 0.5 µg/l tetrachloromethane 0.1 µg/l trichlorofluoromethane 1 µg/l dichlorodifluoromethane 1 µg/l monochloroethane 1 µg/l 1,1-dichloroethane 0.1 µg/l 1,2-dichloroethane 0.1 µg/l 1,2-dibromietaani 0.5 µg/l 1,1,1-trichloroethane 0.1 µg/l 1,1,2-trichloroethane 0.1 µg/l 1,1,1,2-tetrachloroethane 0.1 µg/l 1,1,2,2-tetrachloroethane 1 µg/l vinyl chloride 0.1 µg/l 1,1-dichloroethene 0.1 µg/l cis-1,2-dichloroethene 0.1 µg/l trans-1,2-dichloroethene 0.1 µg/l amount of 1,2-dichloroethene 0.2 µg/l trichloroethylene 0.1 µg/l sum of 11 chlorinated hydrocarbons 1.1 µg/l tetrachloroethene 0.1 µg/l Sum of trichloroethylene and tetrachloroethylene 0.2 µg/l sum 5 chlorinated ethylenes 0.5 µg/l 1,2-dichloropropane 1 µg/l 1,3-dichloropropane 1 µg/l 2,2-dichloropropane 1 µg/l 1,2,3-trichloropropane 1 µg/l 1,2-dibromo-3-chloropropane 1 µg/l 1,1-dichloro-1-propene 1 µg/l cis-1,3-dichloro-1-propene 1 µg/l trans-1,3-dichloropropene 1 µg/l hexachlorobutadiene 1 µg/l 2-chlorotoluene 1 µg/l 4-chlorotoluene 1 µg/l monochlorobenzene 0.1 µg/l bromobenzene 1 µg/l 1,2-dichlorobenzene 0.1 µg/l 1,3-dichlorobenzene 0.1 µg/l 1,4-dichlorobenzene 0.1 µg/l amount of 3 dichlorobenzene 0.3 µg/l 1,2,3-trichlorobenzene 0.1 µg/l 1,2,4- trichlorobenzene 0.1 µg/l 1,3,5-trichlorobenzene 0.1 µg/l amount of 3 trichlorobenzene 0.4 µg/l benzene 0.1 µg/l toluene 0.5 µg/l ethylbenzene 0.1 µg/l o-xylene 0.1 µg/l m/p-xylene 0.2 µg/l sum of xylenes 0.3 µg/l sum of BTEX 1 µg/l styrene 0.2 µg/l isopropylbenzene 1 µg/l n-propylbenzene 1 µg/l 1,2,4-trimethylbenzene 1 µg/l 1,3,5-trimethylbenzene 1 µg/l n-butylbenzene 1 µg/l sec-butylbenzene 1 µg/l tert-butylbenzene 1 µg/l p-isopropyltoluene 1 µg/l naphthalene 1 µg/l Diisopropyl ether (DIPE) 0.6 µg/l ETBE (ethyl tert-butyl ether) 0.2 µg/l MTBE (methyl tert-butyl ether) 0.2 µg/l tert-amyl ethyl ether (TAEE) 0.2 µg/l TAME 0.2 µg/l tert-butyl alcohol (TBA) 5 µg/l ethanol 100 µg/l A customized offer can also be prepared if you are interested in analyzing only individual compounds from a sample. Suitable sample containers for analysis can be ordered through us. Sample containers picked up from Measurlabs are included in the price of the analysis, but sample containers can also be shipped to the customer for a separate fee.

We offer several accredited methods for determining the total fluorine (TF) content of combustible materials: EN 14582, based on combustion ion chromatography (CIC). The method is recommended by the Nordic Council of Ministers as a quick and powerful total fluorine screening technique., EN 15408 using oxygen bomb combustion treatment followed by ion chromatography (IC). This method can be applied to plastic sheets and granules, and it is also possible to determine the total content of S, Cl, and Br., ASTM D7359-23, based on oxidative pyrohydrolytic combustion, followed by CIC.. The most suitable method is typically selected based on the sample matrix. However, please let us know if you wish a specific standard to be followed. Sample preparation (air drying and milling of the sample to particles <1 mm) is included in the displayed price. This analysis is commonly used to evaluate packaging materials' compliance with the PFAS restriction outlined in the new EU Packaging and Packaging Waste Regulation (PPWR). If TF content does not exceed 50 mg/kg (ppm), the material can be considered compliant without further testing.

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.