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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Additional information

Acute Fish Toxicity:

A water accommodated fraction of hydrocarbons, C12-C16, isoalkanes, cyclics, <2% aromatics, produced a 96-hour LL50 value of >88,444 mg/L and LL0 value of 88,444 mg/L with rainbow trout, Oncorhynchus mykiss. No mortality was observed in the treatment test system. The water accommodated fraction of hydrocarbons, C11-C14, n-alkanes, isoalkanes, cyclics, <2% aromatics, produced a 96-hour LL50 value of >1000 mg/L and LL0 value of 1000 mg/L with rainbow trout, Oncorhynchus mykiss. No mortality was observed in either the control or treatment test systems. The data from the latter study are used as supporting, read-across data to hydrocarbons, C12-C16, isoalkanes, cyclics, <2% aromatics.

Chronic Fish Toxicity:

The hydrocarbons, C12-C16, isoalkanes, cyclics, <2% aromatics, estimated freshwater fish 28-day NOELR (No Observed Effect Loading Rate) value is >1000 mg/l based on growth.

Acute Invertebrate Toxicity:

Freshwater:

The water accommodated fraction (WAF) of hydrocarbons, C11-C14, isoalkanes, cyclics, <2% aromatics, did not produce a 50% effect (immobility) with Daphnia magna at a loading of 1000 mg/L after a 48-hour exposure. Therefore, the 48-hour LL50 is reported as >1000 mg/L. There was no mortality at the 1000 mg/L loading level after 48 hours. Therefore, the 48-hour LL0 for mortality is reported as 1000 mg/L. There was also no mortality in the control. These data are used as read-across data to hydrocarbons, C12-C16 isoalkanes, cyclics, <2% aromatics.

Marine:

The water accommodated fraction of hydrocarbons, C12-C16, isoalkanes, cyclics, <2% aromatics, did not produce a 50% effect (mortality) with Chaetogammarus marinus at a loading of 10,000 mg/L after a 96-hour exposure. Therefore, the 96-hour LL50 is reported as >10,000 mg/L. There was no mortality at the 10,000 mg/L loading level after 96 hours and no effects on swimming and feeding behavior were observed. Therefore, the 96-hour NOELR for these endpoints is reported as 10,000 mg/L. There was also no mortality in the control.

Chronic Invertebrate Toxicity:

Hydrocarbons, C11-C13, isoalkanes, <2% aromatics, showed no effects on Daphnia magna survival, reproduction, or length at a nominal loading of 1 mg/L. Therefore, the 21-Day No Observed Effect Loading Rate (NOELR) = 1.0 mg/L for these endpoints based upon nominal loading levels. These data are used as read-across data to hydrocarbons, C12-C16, isoalkanes, cyclics, <2% aromatics.

Algal Toxicity:

Growth in an alga culture, as measured by biomass and growth rate, exposed to a 1000 mg/L water accommodated fraction of hydrocarbons, C11-C14, n-alkanes, isoalkanes, cyclics, <2% aromatics, was not inhibited when compared to the control after a 72-hour exposure. Therefore, the 72-hr EL50 and NOELR values for these two endpoints are reported as >1000 mg/L and 1000 mg/L, respectively. The data from this study are used as read-across data to hydrocarbons, C12-C16, isoalkanes, cyclics, <2% aromatics.

Toxicity to microorganisms:

The hydrocarbons, C11-C14, isoalkanes, <2% aromatics, estimated protozoan, Tetrahymena pyriformis, 48-hr EL50 value for this substance is >1000 mg/L based on growth inhibition. Isododecane at the highest loading rate, 2 ml/L, did not inhibit the respiration rate of Pseudomonas putida over an exposure period of 5 hours. The data from the latter study are used as supporting, read-across data to hydrocarbons, C11-C14, isoalkanes, cyclics, <2% aromatics.