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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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:
0.79 µg/L
Assessment factor:
10
Extrapolation method:
assessment factor
PNEC freshwater (intermittent releases):
0.239 µg/L

Marine water

Hazard assessment conclusion:
PNEC aqua (marine water)
PNEC value:
0.079 µg/L
Assessment factor:
100
Extrapolation method:
assessment factor
PNEC marine water (intermittent releases):
0.239 µg/L

STP

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

Sediment (freshwater)

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

Sediment (marine water)

Hazard assessment conclusion:
PNEC sediment (marine water)
PNEC value:
0.044 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:
2.42 mg/kg soil dw
Assessment factor:
10
Extrapolation method:
assessment factor

Hazard for predators

Secondary poisoning

Hazard assessment conclusion:
PNEC oral
PNEC value:
3.33 mg/kg food
Assessment factor:
90

Additional information

The PNEC for aquatic freshwater toxicity was derived based on three long-term studies with freshwater organisms. As no results for marine organisms were available, the PNEC aquatic marine water was based on the PNEC aquatic freshwater with a higher AF.


No studies on the toxicity to sediment dwelling organisms are available. The PNECs were therefore calculated with the help of the EPM based on aquatic toxicity data. As the substance has a log Kow of < 5 (3.83) no additional assessment factor has to be applied for the risk assessment.


The PNEC soil was derived based on long-term studies for four species from three diffenent trophic levels.

Conclusion on classification

CLP Regulation:


Aquatic acute toxicity:


The lowest EC50 is < 1.0 mg/L (0.0239mg/L) and thus the substance has to be classified as category acute 1 (H400). Additionally a M-factor of 10 has to be applied.


Aquatic chronic toxicity:


According to Table 4.1.0 in the 2nd Amendment of Regulation (EC) No 1272/2008, for substances for which adequate chronic toxicity data are not available for all three trophic levels, chronic toxicity has to be assessed based on the chronic data and on the acute data for the levels where no chronic data are available. Based on the lowest available chronic value (ErC10 = 0.0079 mg/L) a classification as category chronic 1 (H410) applies (M-factor 10).