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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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:
0.04 µg/L
Assessment factor:
3
Extrapolation method:
sensitivity distribution

Marine water

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

STP

Hazard assessment conclusion:
PNEC STP
PNEC value:
0.025 mg/L
Assessment factor:
1
Extrapolation method:
assessment factor

Sediment (freshwater)

Hazard assessment conclusion:
PNEC sediment (freshwater)
PNEC value:
438 mg/kg sediment dw
Assessment factor:
10
Extrapolation method:
assessment factor

Sediment (marine water)

Hazard assessment conclusion:
PNEC sediment (marine water)
PNEC value:
438 mg/kg sediment dw
Assessment factor:
10
Extrapolation method:
assessment factor

Hazard for air

Air

Hazard assessment conclusion:
no hazard identified

Hazard for terrestrial organisms

Soil

Hazard assessment conclusion:
PNEC soil
PNEC value:
1.41 mg/kg soil dw
Assessment factor:
3
Extrapolation method:
sensitivity distribution

Hazard for predators

Secondary poisoning

Hazard assessment conclusion:
no potential for bioaccumulation

Additional information

For silver cyanide, it is likely that the cyanide component will be degraded in STP, and the silver released to the environment from the silver cyanide complex will behave in a similar manner to ionic silver in the environment. Therefore, PNEC values for silver cyanide are read across from the ionic silver REACH dossier.

Conclusion on classification

Experimental ecotoxicity data are not available for silver cyanide, but there is a large amount of data available for the components of the substance (silver and free cyanide). Therefore, in order to minimise unnecessary testing, a calculation approach was used for determining the toxicity of silver cyanide to fish, invertebrates, algae and microorganisms using the extensive information that already exists on the toxicity of the metal ion and free cyanide, and on the speciation of silver cyanide in ecotoxicity test solutions.

The most sensitive endpoint was determined to be Daphnia, with a calculated EC50 of 0.00056 mg/L (wca 2012). The calculated EC50 for the most sensitive trophic level is ≤ 1 mg/L, therefore the test item is classified as hazardous to the aquatic environment with Acute Category 1, and an M-factor of 1000. The acute data has also been considered for assessing the long-term aquatic hazard. Therefore, based on the toxicity data, the test item is classified as Category Chronic 1, with M-factor of 100.