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The proposed work item is the standardisation of an analytical method applied for measurement of MEL, AMN, AMD, CYA, CYRO, and HMMM in aqueous matrices. Quantification of the substances is achieved by calibration with analytical standards in drinking water. For all substances except for HMMM, isotopelabelled internal standards are applied to correct for intensity variations. The method can be applied for various water matrices, including drinking water, surface water, and wastewater.
For most samples, the method can be used with direct injection, or, for wastewater, after dilution of samples. In this case, water samples only have to be diluted with 90% acetonitrile prior to analysis to create the necessary matrix. If lower limits of quantification (LOQs) need to be achieved, preconcentration by evaporation can be applied. However, it should be noted that in wastewater, HMMM should only be measured with direct injection, due to significant matrix effects during evaporation. In undiluted water samples, the following LOQs apply: With direct injection MEL 0.10 μg/L, AMN 0.2 μg/L, AMD 0.1 μg/L, CYA 1.0 μg/L, CYRO 0.10 μg/L, and HMMM 0.10 μg/L ; with evaporation MEL 0.010 μg/L, AMN 0.010 μg/L, AMD 0.010 μg/L, CYA 0.050 μg/L, CYRO 0.010 μg/L, and HMMM 0.010 μg/L.
Measurements are performed by highperformance liquid chromatography (HPLC) and MS/MS detection. A hydrophilic interaction liquid chromatography (HILIC) column (Luna HILIC (150 x 2 mm, 3 μm, Phenomenex) with HILIC security guard cartridge (4 x 2 mm, Phenomenex)) is applied on an HPLC Infinity 1290 System (Agilent Technologies). An injection volume of 10 μL and a column temperature of 30 °C is used. Acetonitrile and ultrapure water with addition of 10 mM ammonium acetate and 0.1% formic acid are applied as eluents with isocratic elution of 90% acetonitrile and a flow rate of 0.4 mL/min. The mass spectrometric detection is performed on an API5500 Triple Quad (Sciex) after electrospray ionisation (ESI). All analytes are detected in multiple reaction monitoring (MRM) detection mode, with MEL, AMN, CYRO, and HMMM measured in positive mode, and AMD and CYA detected in negative mode. The analytes show retention times between 1.2 min (HMMM) and 3.4 min (AMN), while the chromatographic run is continued until 10 min to avoid carryover.
The method has been validated concerning recovery of evaporation, calibration linearity, matrix effects, and reproducibility. Stability tests showed no analyte degradation in glass, polyethylene, or polystyrene containers over 28 days, regardless of the storage temperature.
Recommendations for sampling strategies of different water matrices and sample storage were also derived from the conducted tests as well as from established sampling standards. During preparation of the European standard, a round robin test with several laboratories participating in the application of the analytical method should be conducted.
Melamine (MEL) serves as starting material in the synthesis of MEL resins which find broad application in industry (e.g. for the production of laminates, adhesives, surface coatings, tyres, textiles, moulding compounds). The MEL substance as such can also be used as flame retardant in polyurethane foam (upholstered products) and as blowing agent in intumescent coatings. Therefore, MEL can be described as a highproductionvolume chemical in the European Economic Area. Since its release to the aquatic environment can occur not only from industrial processes, but possibly also from the use phase of household products like dinnerware, flooring, furniture, toys, leather products, paper and cardboard products, electronic equipment and upholstered products, it is important to monitor its discharge and gain more insight into the distribution pathways of MEL.
In addition, MEL derivatives ammeline (AMN), ammelide (AMD), and cyanuric acid (CYA) which may be formed in aqueous solutions are of special relevance. Also, potential precursors cyromazine (CYRO), which is an approved EU biocidal, and hexa(methoxymethyl)melamine (HMMM), which serves as cross linker in the tyre and coatings industries, should be considered. However, occurrence and transformation of MEL, its derivatives, and precursors in water resources has not yet been thoroughly investigated. Several methods for tracelevel determination of MEL and related substances in different media have already been published. However, no standardised analytical method including all target analytes of interest is currently available for water samples In order to be prepared for any regulations that may arise, e.g. in the area of SVHC regulation, a uniform standardised method is required to create a uniform database. Additionally, a sampling protocol for the collection of samples which are to be measured with the standardised analytical method should be provided.
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