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EU-SICHERHEITSDATENBLATT Dieselkraftstoff ... - Schmierstoffe

EU-SICHERHEITSDATENBLATT Dieselkraftstoff ... - Schmierstoffe

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PolyAr = poly-aromatics consisting of three or more ring aromatics that may include<br />

saturated rings<br />

Note that for certain HCBs, none of the possible structures may exist, e.g. there are no C5<br />

aromatics.<br />

The strategy to assess PBT/vPvB properties of HCBs consists of the following steps:<br />

QSAR models are applied to compute predictions of primary biodegradation halflives<br />

(P) and fish bioconcentration factors (B) for the CONCAWE library of<br />

representative structures (Appendix 1) as recommended by the REACH PBT<br />

guidance (R.11). Two modules from EPISuite v4.00 were used to screen for<br />

persistence and bioaccumulative properties, BioHCwin and BCFBAF.<br />

Where available for hydrocarbons, experimental primary biodegradation half-lives in<br />

un-acclimated freshwater or marine water as well as aqueous or dietary<br />

bioaccumulation test data are compiled and compared to model predictions. In<br />

addition, other relevant lab and field bioaccumulation studies are also considered to<br />

assess the potential of petroleum hydrocarbons to biomagnify in the foodchain. This<br />

information is an important compliment to bioconcentration data since<br />

biomagnification is regarded as the principal determinant for identifying substances<br />

posing a bioaccumulation concern (Weisbrod et al. 2009).<br />

In some cases, experimental data for hydrocarbons that have atypical structures (e.g.<br />

ethanediyl or isopropyl functional groups) are included in this analysis. This allows a<br />

more through appraisal of the reasonableness of model predictions based on available<br />

experimental information. However, such data are interpreted with caution, and<br />

judged relative to the weight of evidence provided by more typical structures, in<br />

deciding P and B properties of specific HCBs.<br />

Finally, all the available information on persistence and bioaccumulation are<br />

collectively reviewed to determine if a further assessment of toxicity was required. If<br />

a HCB was found to meet the P and B criteria, toxicity was evaluated in accordance<br />

with Annex XIII criteria. If necessary, the chronic aquatic toxicity for the structures<br />

comprising the HCB was computed using the target lipid model included in the<br />

PETROTOX model (Redman 2009).<br />

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