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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Marine water

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

Sediment (freshwater)

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

Sediment (marine water)

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

Hazard for air

Hazard for terrestrial organisms

Soil

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

Hazard for predators

Secondary poisoning

Hazard assessment conclusion:
insufficient hazard data available (further information necessary)

Additional information

The determined aquatic toxicity of quinine sulphate to Ictalurus punctatus is 34 mg/L (LC50, 96 h). According to this, the LC50 (96 h) of quinine is 26.1 mg/L.

The aquatic toxicity of quinine to invertebrates was determined experimentally and published by Guilhermino, 2000. The EC50 of the read across substance quinine sulphate for Daphnia magna was determined in freshwater. The EC50 (24 h) of quinine sulphate for Daphnia magna is 44.8 mg/l. According to this, the EC50 of quinine is 34.4 mg/L.

In an own experimental study the EC50 for 48 h of the read across substance quinine sulphate for Daphnia magna is 91.93.mg/l. According to this, the EC50 of quinine is 70.59 mg/l. The aquatic toxicity to algae was also determined experimentally and published by Moreno-Garrido, 2001. In this publication, the toxicity for green algaeDunaliella salinawas determined for 72 h in saltwater. The determined EC50 of the read across substance quinine sulphate is 14.5 mg/L. According to this, the EC50 of quinine is 11.13 mg/L.

Conclusion on classification

The experimentally determined LC50/EC50 of quinine for fish, invertebrates and algae is > 10 mg/L and furthermore quinine is readily biodegradable. According to CLP 1272/2008 criteria for acute (short-term) aquatic toxicity, only substance with a toxicity of LC50/EC50 < 1 mg/L has to be classified. Therefore, quinine is not harmful to aquatic life and does not need to be classified.