ÍST EN 16181:2018

Staða:

Fellur úr gildi - 20.3.2022

Enskt heiti:

Soil, treated biowaste and sludge - Determination of polycyclic aromatic hydrocarbons (PAH) by gas chromatography (GC) and high performance liquid chromatography (HPLC)

Tækninefnd:

CEN/TC 400

ICS flokkur:

13.030, 13.080

Auglýst:

16.3.2022

Umfang (scope):

This European Standard specifies the quantitative determination of 16 polycyclic aromatic hydrocarbons (PAH) (see Table 2) in sludge, soil and treated biowaste using GC-MS and HPLC-UV-DAD/FLD covering a wide range of PAH contamination levels (see also Annex B). When using fluorescence detection, acenaphthylene cannot be measured. (...) The limit of detection depends on the determinants, the equipment used, the quality of chemicals used for the extraction of the sample and the clean-up of the extract. Typically, a lower limit of application of 0,01 mg/kg (expressed as dry matter) can be ensured for each individual PAH. This depends on instrument and sample. Sludge, soil and treated biowaste can differ in properties and also in the expected contamination levels of PAHs and presence of interfering substances. These differences make it impossible to describe one general procedure. This European Standard contains decision tables based on the properties of the sample and the extraction and clean-up procedure to be used. Two general lines are followed, an agitation procedure (shaking) or use of soxhlet/pressurized liquid extraction. NOTE Other PAH compounds can also be analysed with this method, provided suitability has been proven.

Hafðu samband í síma 520-7150 varðandi þennan staðal.

* Mynd sem fylgir ÍST EN 17503:2022

ÍST EN 17503:2022

This document specifies different methods for quantitative determination of 16 polycyclic aromatic hydrocarbons (PAH) (see Table 2) in soil, sludge, treated biowaste, and waste, using GC-MS or HPLC-UV-DAD/FLD covering a wide range of PAH contamination levels (see Table 2). NOTE The method can be applied to sediments provided that validity is demonstrated by the user. When using fluorescence detection, acenaphthylene cannot be measured. [Table 2 -Target analytes of this document] The limit of detection depends on the determinants, the equipment used, the quality of chemicals used for the extraction of the sample and the clean-up of the extract. Under the conditions specified in this document, the lower limit of application from 10 g/kg (expressed as dry matter) for soils, sludge and biowaste to 100 g/kg (expressed as dry matter) for solid waste can be achieved. For some specific samples (e.g. bitumen) the limit of 100 g/kg cannot be reached. Sludge, waste and treated biowaste can dif
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