Survey and health assessment of chemical substances in hobby products for children 3 Quantitative chemical analyses
In consultation with the Danish EPA we selected a number of the identified substances for quantification. 3.1 Applied method for the quantitative analysesThe quantitative analyses are based on GC/MS and X-ray analysis. The specific parameters for the applied method are described in the following: 3.1.1 Quantitative GC/MS analysis3 different extractions have been made dependent on product type: Marker pens and gel pens Half of a marker pen equivalent to 0.1-1 g sample (excl. felt cartridge and depending on type), was extracted with 10 ml dichloromethane with bromobenzene and o-terphenyl as internal standards. Glitter glue 1 g was weighed out, suspended in water and subsequently and extracted in 3 ml pentane with brombenzene and o-terphenyl as internal standards. Acrylic paints 0.1 g weighed out and extracted in a mix of 10 ml methanol and 15 ml dichloromethane with brombenzene and o-terphenyl as internal standards. The extracts were subsequently analysed by GC/MS. Table 3.1 GC/MS analysis parameters
Calibration of the applied method is made from the detection limit to approx. 2-20 mg/g sample dependent on the individual parameter and the weighed-out sample. The detection limit appears from the following tables. The uncertainty factor is calculated based on double determination and will appear from the following tables. For the selected samples the extracts from the qualitative screening have been re-analysed. No weight and double determination have been recorded in connection with the qualitative determination, thus the uncertainty for these analyses cannot be determined. 3.1.2 X-ray measurementThe samples were cut in sizes to fit into the X-ray equipment. The samples were analysed directly and the content of elements with atomic number higher than 10 were analysed against standards of pure elements or simple salts. The degree of accuracy of the analysis method is ± 20 %. Table 3.2 Parameters for X-ray analysis
3.1.3 Formaldehyde measurement0.01-0.5 g sample was suspended in 5 ml water. The content of formaldehyde is derivated with PFBOA and analysed by SPME-GC/MS. Table 3.3 GC/MS analysis parameters
Calibration of the applied method has been made in the range of 0.05 -1500 mg/kg. The detection limit for the applied analysis method is determined to 0.05 mg/kg and the uncertainty factors appear from Table 3.8. 3.1.4 Ingredients in marker pensTable 3.4 Analysis results - marker pens mg/g (± standard deviation in mg/g)
”-” Below the detection limit. Table 3.4 Analysis results - marker pens mg/g (± standard deviation in mg/g)
”-” Below the detection limit Table 3.5 Analysis results for sample no. 16, mg/g (± standard deviation in mg/g)
”-” Below the detection limit 3.1.5 Ingredients in acrylic paintTable 3.6 Analysis results for acrylic paint, mg/g (± standard deviation in mg/g)
”-” Below the detection limit. Table 3.7 Elements in acrylic paint, mg/g
”-” Below the detection limit. Table 3.7 Elements in acrylic paint, mg/g
”-” Below the detection limit. 3.1.6 Content in glitter glueTable 3.8 Formaldehyde in glitter glue
Table 3.9 Analysis results - glitter glue, mg/g (± standard deviation in mg/g)
”-” Below the detection limit Table 3.10 Elements in glitter glue, mg/g
”-” Below the detection limit 3.1.7 Elements in shrink plasticTable 3.11 Elements in shrink plastic, mg/g
”-” Below the detection limit The X-ray analysis revealed no other elements. 3.2 Comments on the results of the quantitative analysesBy a comparison of the findings of the quantitative analysis and the findings of the chemical screening it has been observed that the different colour variations in the same product often contain different components. Within the scope of this project it has not been possible to analyse all colour variations of the selected products. Therefore, it is possible that one or more of the products may contain components with a larger content of the identified substances than recorded in the quantitative analyses, or may contain not identified hazardous substances, because the colour variation was not taken out for analysis. These variations are also assumed to be the reason why more of the components, revealed by the qualitative screenings, were not detected in the same product in connection with the quantitative analyses, as these were carried out on different colours variations. In addition, deconvolution software was used in the qualitative analysis, making it possible to detect contents in small amounts, which could not subsequently be quantified. Sample no. 4 was selected for the quantitative analysis. In the colour variation selected for the analysis it was not possible to detect any of the substances, which were identified in connection with the screening. 3.3 Legislation and standardsLiquids in marker pens, glue, and acrylic paint are thus covered by the requirements in Statutory Order No. 329 on classification, packaging, labelling, sale, and storage of chemical substances and products, 2002 cf. § 1 and § 2. The Danish Safety Technology Authority has classified the hobby products to be covered by the regulations stipulated in the Statutory Order No. 1116 on toys. The order stipulates that toys may not be marketed if they constitute a hazard to the safety or the health of the consumers. Appendix 2 of the order includes the limit values for heavy metals and states that toys may not contain dangerous substances or preparations as defined in directive 67/548/EØF and directive 88/379/EØF in amounts which may be hazardous to children. As mentioned in the Statutory Order, Appendix 3, there are a number of standards regarding safety regulations for toys (DS/EN 71-1 to DS/EN 71-7). Three new standards have been completed for organic chemical substances (DS/EN 71-9, EN 71-10 and EN 71-11), but these standards are not harmonised. This standard lay down requirements to accessible liquids in toys under item 4.2, saying that the liquids may not be classified as toxic, harmful, corrosive, irritant or sensitizing according to directive 1999/45/EC. Beyond this, there may not be any substances classified as carcinogenic, mutagenic or reprotoxic classified as category 1 and 2. Table 1 standard EN 71-9 specifies limits for coloured liquids, as the requirements to colorants (table 2b) and primary aromatic amines (table 2C) shall be observed. Table 2c specifically mentions 4-chloraniline, o-anisidine and aniline, which were all found in the products. Under A11 it is stated that these substances may not be detected in toys according to (DS/EN 71-11). It should be mentioned that the detected concentration of substances is in the range of 100-400 ppm, which is far beyond the detection limits stipulated in the standard. The conclusion is that primary aromatic amines have been detected in marker pens and acrylic paint in concentrations beyond the requirements to the detection limits in (DS/EN 71-9 and DS/EN 71-11). Marker pens and acrylic paint with primary amines do not comply with the standards for content organic substances. 3.4 Prioritization of substances in hobby productsBased on the health screening described in chapter 2.2 and the quantitative analysis we have in consultation with the Danish EPA selected a number of substances for extended health assessment. The substances are:
The health effects of formaldehyde have also been assessed. Substances used for assessment of environmental effect:
These substances are extremely toxic for aquatic organisms and –chloraniline alone is difficultly degradable, and the substances are therefore suitable for assessment of a worst case effect.
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