OECD 201: Freshwater alga and cyanobacteria, growth inhibition test

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.

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 (1,000 °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 displayed price includes the full CHNOS package with two parallel measurements and applies to conventional organic samples. The results are reported as wt-% of the initial sample. The addition of ash, drying, and dry loss measurements will increase the minimum required sample material 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. Analysis can be split into the following packages: CHN, O, and S.

Analysis of gaseous samples using Raman spectroscopy.

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.

The 48-hour acute daphnid immobilisation test according to OECD 22 assesses short-term aquatic toxicity by measuring immobilisation of daphnids, usually Daphnia magna, and using those observations to derive concentration–response values. The primary reported metric is the EC50 at 48 hours, with an optional EC50 at 24 hours calculated from dose–response analysis. The protocol is the following: The test begins with neonates less than 24 hours old exposed for 48 hours to at least five concentrations plus a control, with a minimum of twenty animals per concentration typically arranged in replicate groups (for example, four replicates of five). , Immobilisation is observed and recorded at 24 and 48 hours, and the numbers or proportions immobilised at each concentration and in the control are tabulated for statistical modelling. , Test solutions are prepared by diluting the substance into acceptable test water, avoiding solvents or emulsifiers when possible. Analytical measurements of test substance concentration, dissolved oxygen, and pH are performed at the start and end of the exposure to document conditions. , The biological endpoint is direct observation of loss of swimming activity consistent with immobilisation, EC50 values are derived from dose–response modelling and are normally reported in concentration units such as mg/L.. The report includes the counts or proportions immobilised per concentration and control at each time point, the calculated EC50(s), and supporting water chemistry and analytical concentration data. The method is accepted under REACH for aquatic hazard characterization in registration dossiers submitted to ECHA, where OECD TG 202 is equivalent to EU Method C.2 under Commission Regulation (EC) No. 440/2008. Under the U.S. Toxic Substances Control Act (TSCA), EPA may require daphnid acute toxicity testing to OPPTS 850.1010/OECD 202 for new chemical substances expected to be acutely toxic.

The bacterial reverse mutation (AMES) test is used to evaluate the genotoxic effect of a medical device or its extract when in contact with a bacterial suspension. The test is conducted according to OECD 471 and ISO 10993-3 by exposing a bacterial suspension of Salmonella spp and Escherichia coli to 5 concentrations of the medical device or its pure extracts. The AMES test is a preliminary "screening test" for genotoxicity. A full genotoxicity evaluation usually includes testing the device with two in vitro methods, of which AMES is typically performed first. An additional in vivo method can be used if needed. Measurlabs can support you with the full genotoxicity evaluation. Please contact our experts for a quote.

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.

The following analyses are included in this nanoparticle analysis package, intended to characterize nanoforms according to the REACH Regulation. Particle size distribution and aspect ratios by SEM-EDX Preparation with isopropanol, Sample dispersion on a slide, with centrifugation, SEM analysis and particle count by image analysis, Nanoparticle detection and classification according to the 2022 EC recommendation on the definition of nanomaterial, Reporting of PSD parameters for ~300 particles, including the following: PSD diagram, accumulated and individual., Feret min (min, d10, d25, d50, d75, d90, d95, max), Feret max (min, d10, d25, d50, d75, d90, d95, max), Equivalent circular diameter (min, d10, d25, d50, d75, d90, d95, max), Aspect ratio (calculated based on individual Feret min and Feret max measurements), Number based nano-fraction (%).. Crystal phase analysis by XRD/Rietveld method Sample preparation: drying, grinding, X-ray preparation, XRD analysis over an angular range extending from 10° to 90°, Identification of the crystalline phases present in the sample, Semi-quantitative analysis of phase distribution, using the Rietveld method, Interpretation of diffractograms. Chemical composition/purity by ICP-AES and CHNS analysis ICP-AES quantification of inorganic and metallic elements: Ag, Al, As, B, Ba, Be, Bi, Ca, Cd, Co, Cr, Cu, Fe, K, Li, Mg, Mn, Mo, Na, Ni, P, Pb, S, Se, Sb, Si, Sn, Sr, V, Zn, Ti, and Tl, Determination of C, H, N, and S with an elemental analyzer. Volume-specific surface area (VSSA) and VSSA diameter calculations (optional) BET specific surface area measurement of powder by nitrogen adsorption, True (skeletal) density measurement by He pycnometry, excluding intergranular and intragranular porosity, Both analyses include sample preparation. You can request a quote for the analysis using the form below. Please note that the OECD 125 guideline does not apply to this analysis.

Determination of bromide, fluoride, chloride, nitrate, nitrite, and sulfate (Br-, F-, Cl-, NO2-, NO3- ja SO42-) in soil, sludge, and sediment samples with ion chromatography. The analysis is carried out after a water extraction. Ask about the price for other solid matrices and aqueous matrices. Please store the samples in refrigerated conditions and in gas-sealed containers.