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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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:
PNEC aqua (freshwater)
PNEC value:
0.1 mg/L
Assessment factor:
1 000
Extrapolation method:
assessment factor
PNEC freshwater (intermittent releases):
1 mg/L

Marine water

Hazard assessment conclusion:
PNEC aqua (marine water)
PNEC value:
0.01 mg/L
Assessment factor:
10 000
Extrapolation method:
assessment factor

STP

Hazard assessment conclusion:
PNEC STP
PNEC value:
100 mg/L
Assessment factor:
10
Extrapolation method:
assessment factor

Sediment (freshwater)

Hazard assessment conclusion:
PNEC sediment (freshwater)
PNEC value:
62.02 mg/kg sediment dw
Extrapolation method:
equilibrium partitioning method

Sediment (marine water)

Hazard assessment conclusion:
PNEC sediment (marine water)
PNEC value:
6.202 mg/kg sediment dw
Extrapolation method:
equilibrium partitioning method

Hazard for air

Air

Hazard assessment conclusion:
no hazard identified

Hazard for terrestrial organisms

Soil

Hazard assessment conclusion:
PNEC soil
PNEC value:
12.307 mg/kg soil dw
Extrapolation method:
equilibrium partitioning method

Hazard for predators

Secondary poisoning

Hazard assessment conclusion:
no potential to cause toxic effects if accumulated (in higher organisms) via the food chain

Additional information

Although the substance did not show any toxic effects in acute aquatic toxicity studies on the throphic levels (fish, daphnia and algae) and also no toxicity towards sludge microorganisms was seen, PNECs have been derived for freshwater, marine water, intermittent release and sewage sludge treatment. Based on these PNEC, by using the partitioning method, PNECs for sediment, marine sediment and soil were derived in order to show that sediment and soil exposure is non-critical and the substance can be used safely.

No hazards to air are present, diven the lack of halogens in the molecule structure (ozone depletion) and the extremely low vapour pressure of 0.00000088 Pa.

Also, the substanc has no potential to cause toxic effects if accumulated through the food chain as no toxic effects were seen in ecotoxicological and toxicological studies performed. Despite this, based on the aquatic BCF of 143.4 as conservative value form QSAR predictions, potential for bioaccumulation is considered low.

Conclusion on classification

Although the substance in non-biodegradable and poorly water soluble (0.3 mg/L) the aquatic BCF derived by QSAR is 143.4 and thus well below 500. This, in combination with the lack of aquatic toxicity in three trophic levels (fish, daphni and algae) results in no classification for aquatic toxicity in accordance with CLP (Regulation EC No 1272/2008).