Registration Dossier

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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Administrative data

Hazard for aquatic organisms

Freshwater

Hazard assessment conclusion:
no hazard identified

Marine water

Hazard assessment conclusion:
no hazard identified

STP

Hazard assessment conclusion:
no hazard identified

Sediment (freshwater)

Hazard assessment conclusion:
no hazard identified

Sediment (marine water)

Hazard assessment conclusion:
no hazard identified

Hazard for air

Air

Hazard assessment conclusion:
no hazard identified

Hazard for terrestrial organisms

Soil

Hazard assessment conclusion:
no hazard identified

Hazard for predators

Secondary poisoning

Hazard assessment conclusion:
insufficient hazard data available (further information necessary)

Additional information

Aquatic toxicity (based on a read-across discussed under 6.1)

The following values have been obtained through GLP compliant studies conducted in accordance with recent guidelines. The studies were conclusive and the results are valid.

Short-term toxicity to fish: LC50(96h) > 100 mg/L, Rufli 1995

Short-term toxicity to aquatic invertebrates: EC50(48h) > 100 mg/L, Neumann 1996

Toxicity to aquatic algae and cyanobacteria: EC50(72h) = 331 mg/L, Memmert 1996

Toxicity to activated sludge: EC50(3h) > 100 mg/L, Grade 1996

One of the most conservative value LC50(96h)> 100 mg/L (fish) is carried forward for the purpose of risk assessment, classification and labelling.

Conclusion on classification

Acute aquatic toxicity

The lowest available effect level, LC50(96h) > 100 mg/L for Oncorhynchus mykiss (fish), does not trigger classification as Hazardous to the aquatic environment according to CLP Regulation (EC) No 1272/2008, Annex I, Part 4, 4.1.2.6.

The conclusion given above only takes into consideration the properties of the constituent in this mono constituent substance. As indicated in the composition under section 1.2 one of the impurities is relevant for classification and labelling of the substance. This is finally included in the Classification and Labelling section 2 where necessary based on the typical concentration value given and the harmonized classification and labelling that is available for this impurity under CLP/GHS.