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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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:
0.117 mg/L
Assessment factor:
50
Extrapolation method:
assessment factor
PNEC freshwater (intermittent releases):
0.208 mg/L

Marine water

Hazard assessment conclusion:
PNEC aqua (marine water)
PNEC value:
0.058 mg/L
Assessment factor:
100
Extrapolation method:
assessment factor

STP

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

Sediment (freshwater)

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

Sediment (marine water)

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

Hazard for air

Hazard for terrestrial organisms

Soil

Hazard assessment conclusion:
PNEC soil
PNEC value:
0.2 mg/kg soil dw
Assessment factor:
50
Extrapolation method:
assessment factor

Hazard for predators

Secondary poisoning

Hazard assessment conclusion:
no potential for bioaccumulation

Additional information

All PNECs are expressed for Br. CaBr2 dissociates in Ca and Br very quickly once in contact with water. The Ca ion is not toxic compared to the toxicity of the Br ion. Therefore NaBr studies have been used for read across because just like for CaBr2, the Na ion is not toxic compared to the toxicity of the Br ion.

The PNECs have all been derived based on the assessment factor approach except for the sediment which was derived based on the partitioning coefficient. The most sensitive reliable endpoint has been determined and an assessment factor based on the REACH guidance has been applied.

- For the aquatic environment the most sensitive endpoint was a NOECreproduction of 7.5 mg NaBr/l for Daphnia magna (Guilhermino et al. 1999).

- For the terristrial compartiment the most sensitive endpoint was a NOECweight of 10 mg Br/kg dw for Eisenia fetida (Goodband, 2008).

Conclusion on classification