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Ecotoxicological information

Toxicity to other aquatic organisms

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Experimental data were reviewed by U. Hommen at the Fraunhofer Institute for Molecular Biology and Applied Ecology (IME). The report is a weight of evidence approach to an extensive body of literature on acute toxicity of aquatic organisms to cyanides, including 43 species (28 freshwater and 15 marine species) from eight major taxonomic groups; and an extensive body of literature on chronic toxicity of aquatic organisms to cyanides, including 13 species (eight freshwater and five marine species) from five major taxonomic groups. The report uses a methodology for species sensitivity distribution consistent with EU guidance (Technical Guidance Document for Deriving Environmental Quality Standards), from which an acute HC5 and a chronic HC5 were derived. In addition, acute aquatic toxicity of sodium cyanide was determined in three species of frog (Rana berlandieri, R. pipiens and Xenopus laevis), in three separate studies by Naddy (2005).  

Additional information

The acute HC5 value of 15.8 ug/L value served as the point of departure for the derivation of the PNECaquatic for intermittent releases for both freshwater and saltwater species.  The species sensitivity distribution (SSD) for acute aquatic toxicity developed by Hommen (2011) is similar to the SSD derived by the ECETOC Joint Assessment of Commodity Chemicals (2007).  The SSD by Hommen includes more recent guideline studies on acute aquatic toxicity.  The acute HC5 reported by Hommen for all aquatic species (15.8 ug/L) is substantially lower than the 96-h LC50 values (410.1 ug/L, 192 ug/L and 254.3 ug/L) in three species of frog (Rana berlandieri, R. pipiens and Xenopus laevis) in three separate studies by Naddy (2005). 

Potassium cyanide and sodium cyanide can be considered as a chemical category, along with hydrogen cyanide (HCN) and acetone cyanohydrin (ACH, also known as 2-hydroxy-2-methylpropanenitrile), based on structural similarity, similar physico-chemical properties and common breakdown/metabolic products in physical and biological systems. Particular attention is paid to the dissociation constant of HCN. In the vast majority of environmental and physiologic conditions, the cyanide salts will dissolve in water to form hydrogen cyanide. The physico-chemical hazards and toxicity result from the activity of this common proximal toxicant, HCN. Support for this category approach is provided in examination of acute and chronic toxicity by oral, dermal, ocular and intraperitoneal administration of various forms of cyanide and in aquatic and terrestrial compartments of the environment, which provide consistent and comparable values when expressed as mmol/kg bw.  An ECETOC Task Force, in the 2007 ECETOC Joint Assessment of Commodity Chemicals ( JACC ) Report No. 53, “Cyanides of Hydrogen, Sodium and Potassium, and Acetone Cyanohydrin (CAS No. 74-90-8, 143-33-9, 151-50-8 and 75-86-5)” supports the development of this chemical category. Hydrogen cyanide (Index No.006-006-00-X) and salts of hydrogen cyanide (Index No.006-007-00-5) are both listed in Annex VI, Table 3.1 of Regulation (EC) No. 1272/2008, entry 006-007-00-5, and are restricted in comparable ways taking into account physical characteristics. Thus, the assignment of potassium cyanide and sodium cyanide to a chemical category does not result in a less protective regulatory status.