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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Marine water

Hazard assessment conclusion:
PNEC aqua (marine water)
PNEC value:
3 µg/L
Assessment factor:
10 000
Extrapolation method:
assessment factor
PNEC marine water (intermittent releases):
30 µg/L

STP

Hazard assessment conclusion:
no hazard identified

Sediment (freshwater)

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

Sediment (marine water)

Hazard assessment conclusion:
PNEC sediment (marine water)
PNEC value:
8.09 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:
16.2 mg/kg soil dw
Extrapolation method:
equilibrium partitioning method

Hazard for predators

Secondary poisoning

Hazard assessment conclusion:
PNEC oral
PNEC value:
23.33 mg/kg food
Assessment factor:
300

Additional information

Due to the complex nature of the test item, for test media for investigations of short-term aquatic toxicity were prepared as a Water Accommodated Fractions (WAFs). PNECs have been calculated based onmean measured WAF loading rates and immobility datafor the most sensitive species (Daphnia).

Conclusion on classification

The test item is not classified as acutely toxic to the environment because the LL50 value determined using mean measured loading rates for the most sensitive species (Daphnia) was > 1 mg/L. However, the substance is not readily biodegradable, water solubility is relatively high (3.1 g/L) and Log Kow was determined to range from unretained (less than -1.02) to ≥ 4 (upper value reported 4.65). These data indicate some concern for the environment and, since long-term toxicity data are available for only one trophic level (algae), aquatic toxicity results should be assessed in terms of substances for which adequate chronic toxicity data are available and substances for which adequate chronic toxicity data are not available. The most stringent classification outcome is then applied. Based on the EL50 value of 30 mg/L determined from mean measured loading rates for Daphnia magna, classification as H412: Aquatic Chronic 3 is applicable when the result is compared to criteria given by Regulation (EC) No 1272/2008 (2nd ATP; 10 March 2011) for non-rapidly biodegradable substances for which adequate toxicity data are not available.