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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Aquatic invertebrates: Exposure of Daphnia magna to the test item gave EL50 values > 100 mg/L loading rate WAF. The No Observed Effect Loading Rate was 100 mg/L loading rate WAF (OECD 202 and EU Method C.2).

 

Algae: Exposure of Pseudokirchneriella subcapitata to the test item gave EL50 values > 100 mg/L loading rate WAF. The No Observed Effect Loading Rate was 100 mg/L loading rate WAF (OECD 201 and EU Method C.3).

Additional information

Daphnia magna

A key study was performed to assess the acute toxicity of the test item to Daphnia magna. The method followed was designed to be compatible with the OECD Guidelines for Testing of Chemicals (April 2004) No 202,"Daphnia sp., Acute Immobilisation Test" referenced as Method C.2 of Commission Regulation (EC) No. 440/2008.

 

Due to the low aqueous solubility and complex nature of the test item, for the purposes of the test the test item was prepared as a Water Accommodated Fraction (WAF). Twenty daphnids (4 replicates of 5 animals) were exposed to Water Accommodated Fractions (WAFs) of the test item over a range of nominal loading rates of 1.0, 10 and 100 mg/L for 48 hours at a temperature of 20 to 22 °C under static test conditions. The number of immobilised daphnia and any adverse reactions to exposure were recorded after 24 and 48 hours.

 

Chemical analysis of the 100 mg/L loading rate WAF test preparations at 0 and 48 hours showed measured test concentrations of less than the limit of quantification (LOQ) of the analytical method employed were obtained which was determined to be 0.10 mg/L. This does not infer that no test item was in solution, just that any dissolved test item was at a concentration of less than the LOQ. Given that the toxicity cannot be attributed to a single component or a mixture of components, but to the test item as a whole, the results were based on nominal loading rates only. 

Exposure of Daphnia magna to the test item gave EL50 values of greater than 100 mg/L loading rate WAF. The No Observed Effect Loading Rate was 100 mg/L loading rate WAF. It was considered unnecessary and unrealistic to test at concentrations in excess of 100 mg/L.

 

Algae

A key study was performed to assess the effect of the test item on the growth of the green alga Pseudokirchneriella subcapitata. The method followed was designed to be compatible with the OECD Guidelines for Testing of Chemicals (2006) No 201, "Freshwater Alga and Cyanobacteria, Growth Inhibition Test" referenced as Method C.3 of Commission Regulation (EC) 761/2009.

 

Due to the low aqueous solubility and complex nature of the test item for the purposes of the test the test item was prepared as a Water Accommodated Fraction (WAF). Following a preliminary range-finding test, Pseudokirchneriella subcapitata was exposed to a Water Accommodated Fraction (WAF) of the test item, at a single nominal loading rate of 100 mg/L (six replicate flasks) for 72 hours, under constant illumination and shaking at a temperature of 24 ± 1 °C. Samples of the algal populations were removed daily and cell concentrations determined for each control and treatment group, using a coulter Multisizer Particle Counter.

 

Analysis of the 100 mg/L loading rate WAF test preparations at 0 and 72 hours showed measured test concentrations of less than the limit of quantification (LOQ) of the analytical method employed, determined to be 0.058 mg/L were obtained. This does not infer that no test item was in solution, just that any dissolved test item was at a concentration of less than the LOQ. Given that the toxicity cannot be attributed to a single component or a mixture of components but to the test item as a whole, the results were based on nominal loading rates only.

 

Exposure of Pseudokirchneriella subcapitata to the test item gave EL50 values of greater than 100 mg/L loading rate WAF. The No Observed Effect Loading Rate was 100 mg/L loading rate WAF. It was considered unnecessary and unrealistic to test at loading rates in excess of 100 mg/L loading rate WAF