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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Marine water

Hazard assessment conclusion:
PNEC aqua (marine water)
PNEC value:
0.001 mg/L
Assessment factor:
100
Extrapolation method:
assessment factor
PNEC marine water (intermittent releases):
0.002 mg/L

STP

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

Sediment (freshwater)

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

Sediment (marine water)

Hazard assessment conclusion:
PNEC sediment (marine water)
PNEC value:
0.052 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:
1 mg/kg soil dw
Assessment factor:
1 000
Extrapolation method:
assessment factor

Hazard for predators

Secondary poisoning

Hazard assessment conclusion:
no potential for bioaccumulation

Additional information

Conclusion on classification

Environmental fate and pathways

Biodegradation:

The substance is not readily biodegradable according to OECD criteria. In soils and sediment systems a rapid formation of metabolites was observed. The determined half-life of the parent substance in sediment systems was < 2 d at 20°C. In soils a half-life of 12 d at 20°C was determined.

 

Bioaccumulation:

Log Kow: 3.83 (OECD 107)

 

Acute aquatic toxicity:

- Fish: LC50 (96 h): 2.4 mg/L (nominal)

- Aquatic invertebrates: EC50 (48 h): 5.9 mg/L (nominal)

- Aquatic algae: ECr50 (96 h): 12.57 mg/L (nominal)

 

Chronic aquatic toxicity:

- Fish: NOEC (28 d): 0.1 mg/L (nominal)

- Aquatic invertebrates: NOEC (21 d): 0.32 mg/L (nominal)

- Algae: NOErC (72h): 4.35 mg/L (nominal)

 

Classification justification according to CLP

Based on the data above, the substance has a low potential to bioaccumulate. The effect concentrations for acute aquatic toxicity L(E)C50 are > 1 mg/L for fish, daphnia and algae. The lowest chronic effect concentration was determined for fish NOEC (28 d): 0.1 mg/L. Thus the CLP trigger value for Category Chronic 2 is > 0.01 to ≤ 0.1 mg/L (EC No 1272/2008). In the available chronic fish study no effect occurred at the threshold concentration of 0.1 mg/L. First effects were seen at the next higher test concentration (0.32 mg/L).Therefore the Maximal Acceptable Toxicant Concentration (MATC) in this study was determined to be 0.18 mg/L (geometric mean of 0.1 – 0.32 mg/L). However the reported NOEC of this study is 0.1 mg/L is considered as trigger value.

The substance is not readily biodegradable. The half-lives for primary degradation in soil and sediment are < 12 days. The degradation productsdo notfulfil the criteria for classification as hazardous to the aquaticenvironment.All available acute and chronic effect concentrations for the metabolites are> 1 mg/L (fish, daphnia and algae).

Therefore, the substance needs to be classified and labelled as environmental hazard Chronic Cat. 2 according to the Regulation (EC) No. 1272/2008 (CLP) and the Regulation (EU) No. 286/2011.