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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Ecotoxicological information

Long-term toxicity to fish

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Administrative data

Link to relevant study record(s)

Reference
Endpoint:
fish early-life stage toxicity
Data waiving:
other justification
Justification for data waiving:
other:

Description of key information

Key value for chemical safety assessment

Additional information

 According to EC 1907/2006, Annex IX, Column 2, long-term toxicity testing shall be proposed if the chemical safety assessment according to Annex I indicates the need to investigate further the effects on aquatic organisms. Amides, C16 and C18-C20 (even numbered, unsaturated), N,N’-ethylenebis did not exert toxicity to any of the aquatic organisms used in the experimental studies available (acute toxicity to invertebrates, algae, microorganisms, and acute toxicity to fish), including Daphnia after 21 days of exposure (long-term study). Since there is no indication that fish sensitivity would be greater than that of Daphnia, similar results for long-term fish studies can be expected. 

 Furthermore, the substance exhibits a log Koc of > 5 (OECD 121) and is poorly water soluble (< 0.01 mg/L). The Guidance on information requirements and chemical safety assessment, Chapter R7.B (ECHA, 2017) states that once insoluble chemicals enter a standard STP, they will be extensively removed in the primary settling tank and fat trap and thus, only limited amounts will get in contact with activated sludge organisms. Nevertheless, once this contact takes place, these substances are expected to be removed from the water column to a significant degree by adsorption to sewage sludge (Guidance on information requirements and chemical safety assessment, Chapter R.7a, (ECHA, 2008)). Thus, discharged concentrations of these substances into the aqueous/sediment compartment are likely to be negligible. Considering this one can assume that the availability of Amides, C16 and C18-C20 (even numbered, unsaturated), N,N’-ethylenebis in the aquatic environment is generally very low, which reduces the probability of chronic exposure to aquatic organisms in general. 

 In addition, the low BCF value (< 6.2) indicates a low potential for bioaccumulation. Therefore, bioaccumulation could be excluded for Amides, C16 and C18-C20 (even numbered, unsaturated), N,N’-ethylenebis, which reduces the possibility of chronic exposure to aquatic organisms additionally. 

 Overall, no chronic aquatic toxicity is expected and thus, no chronic fish toxicity testing is needed. 

 In conclusion, based on following facts, no long-term testing with fish is needed: 

 ·   - No acute and chronic toxicity to aquatic organisms observed. 

 ·   - No indication of higher sensitivity for fish. 

 ·   - A removal from the water column to a significant degree by adsorption to sewage sludge 

 ·   - A low bioavailability 

 ·   - A low potential for bioaccumulation