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EC number: 200-821-6 | CAS number: 74-90-8
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data

Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 0.027 mg/L
Marine water fish
Marine water fish
- Effect concentration:
- 0.059 mg/L
Additional information
A search of the available literature on cyanides revealed an extensive database of aquatic toxicity. In cases where there is a sufficiently robust database, a probabilistic approach using the whole database is preferred to derive a species sensitivity distribution (SSD). The HC5 is regarded as a ‘safe’concentration for 95% of the species (Posthuma et al, 2002). It is used in the current EU chemical risk assessment paradigm that is based on a generic model representing the freshwater and terrestrial environment of Europe (ECB, 2003).
In this analysis, the use of freshwater acute effects data is used in addition to (pooled) saltwater data for risk assessment purposes, and is supported by the empirical data on cyanides reviewed in this report (ECETOC No. 53, 2007).
The dose-response curve for lethal effects on fish is usually very steep, with concentrations without mortality (LC0) or up to 10% mortality (LC10) close to the LC50, especially for the sensitive rainbow trout. For some species, LC50 values were only available for shorter exposure times. In principle, these 24-hour LC50 values are similar to those obtained for 96 hours. The similarity of the 24- and 96-hour LC50 values indicates that the onset of lethal effects of cyanides was very fast.
For a conservative analysis, the selection of tests was restricted to flow-through conditions and only the lowest LC50 per species was used resulting in a refined SSD curve. The lowest LC50 values were reported for salmonids, followed by the Atlantic silverside (Menidia menidia), bluegill sunfish (Lepomis macrochirus), perch (Perca flavescens) and cyprinids. The lowest relevant acute LC50 values are around 25 μg CN ion/l for salmonids (rainbow trout and salmon) under worst-case conditions (low temperature or low oxygen level). Under other conditions or for other species (including other salmonids), LC50 values were generally above 50 μg CN ion/l. The refined SSD’s estimated HC5 is 26 μg/l, corresponding well to the lowest LC50 of 27 μg/l reported for rainbow trout (Oncorhynchus mykiss).
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