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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Marine water

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

STP

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

Sediment (freshwater)

Hazard assessment conclusion:
no hazard identified

Sediment (marine water)

Hazard assessment conclusion:
no hazard identified

Hazard for air

Air

Hazard assessment conclusion:
no hazard identified

Hazard for terrestrial organisms

Soil

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

Hazard for predators

Secondary poisoning

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

Additional information

Due to the low aquatic toxicity, the PNECaquatic organisms can only be expressed a lower limit (> 7.12 mg/L based on an AF of 10). Due to the low sorption to organic matter an estimation based on the Equilibrium partitioning theory cannot be applied. No PNEC for the sediment compartment was derived because of the low sediment-water partition coefficient. Based on the available terrestrial data, a PNEC of 0.38 mg/kg dw for the soil compartment could be derived. Considering the salty character of GLDA partitioning to air is not considered to be relevant.

Conclusion on classification

No effects were observed in the short term ecotoxicity tests with 100 mg/L test substance (GLDA-Na4). When these results are read across to GLDA-H4, using MW correction, values below 100 mg/L are calculated which would point at a GHS classification of acute 3. But considering the results of the long term daphnia and sac fry test it is very unlikely that acute effects will be observed at 100 mg/L GLDA-H4. Classification for hazards to the environment of GLDA-H4 is therefore not deemed necessary.