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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Endpoint summary

Administrative data

Description of key information

IC50, 48h (Algae) = 46 mg/l

EC50, 48h (Daphnia Magna) = 4.3 mg/l

EC50, 96h (fish) = 5.4 mg/l

EL50, repro, Dapnia, 21d > 10 mg/l

NOELR (FELS, lenght) ca 1 mg/l

Additional information

In the following the overview of the available data for acute and long-term toxicity for aquatic organisms is shown:

 

SULPHATED

SULPHATED

SULPHATED

SULPHATED

ORIGIN

CASTOR OIL

ANIMAL OIL

VEGETABLE OIL

FISH OIL

EC

269-123-7

304-835-4

281-978-8

262-992-3

CAS

68187-76-8

94279-90-0

84082-30-4

61788-64-5

Chemical name

Castor Oil, sulphated

Oils, animal, sulphated

Rape oil, sulphated

Oils, fish, sulphated

Salt

Na

Na

Na

Na

Name of the tested sample

 

 

 

 

Short-term toxicity testing on Daphnia

EC50 = 4.3 mg/L

waiving

EC50 = 32.3*

EC50 >100

Growth inhibition study on algae

IC50 = 46 mg/L

RA

EC50 = 70.4

Proposed

Short-term toxicity testing on fish (freshwater;marine)

LC50 = 5.4 mg/L

waiving

LC50 > 100

waiving

Activated sludge respiration inhibition testing

EC0 >1500 mg/L

RA

 

RA

Long-term toxicity testing on Daphnia, 21-days

EL50, repro, Dapnia,
21d > 10 mg/l

RA

 

RA

Fish early-life stage (FELS) toxicity test

NOELR (FELS, lenght)
ca 1 mg/l

RA

 

Proposed

 

 

It is evident from the table and the results on acute tests that the representative substance for the Category is Castor oil, which also has reliable tests for all the trophic levels for the acute and long term exposures.

Effetcs are observed for all the tests. While in the acute tests Daphnia and Fish present comparable results, in the long term tests, Fish demonstrated as the most sensitive speciesand the relevant effect oberved has been a reduction in the lenght of the juvenile fish that sets the NOELR ca. 1 mg/l (test item).

Based on the chemical nature of the substance, no specific analytical technique is available, but the non-selective TOC analysis was performed for the determination of the test concentrations. Moreover, the dissolution of the substance in the different tests (normal shaking vs WAF technique) had a small impact in the final solubilisation of the substance, expecially when compared short to long term toxicity studies.

It is also important to notice that based on acute studies, the Castor oil derivative fish toxicity is much lower than the analogue derivative vegetable and fish, with whic animal oil is more similar; as a consequence, while calculating the DNEL and the risk assessment on the Castor oil results has been chosen in a conservative approach, on the other side, classification of the substance for the enviroment is not considered for the animal derivative