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EC number: 200-909-4 | CAS number: 75-86-5
- 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
As indicated in the hydrolysis study acetone cyanhydrin hydrolyses rapidly within minutes to acetone and cyanide. The study was performed over 24 hours. Therefore the toxic principle is the cyanide ion. The hydrolysis products of acetone cyanhydrin were very toxic against fish.
Key value for chemical safety assessment
Additional information
(Following quotations taken with kind permission from ECETOC 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)
Acute toxicity of cyanides to aquatic organisms… has been studied
extensively. Acute toxicity to fish as 96-hour LC50 values ranged from
27 to 169 μg/l.
The lowest value was obtained for rainbow trout (O. mykiss) under
flow-through conditions. Saltwater species were generally less sensitive
than freshwater species (≈factor 2).
Reliable 96-hour LC50 values for cyanides are available for 19 fish
species ….
Most tests have been conducted with fathead minnow (Pimephales
promelas), brook trout (Salvelinus fontinalis), bluegill
sunfish (Lepomis macrochirus), rainbow trout (Oncorhynchus
mykiss, formerly named Salmo gairdneri) and perch (Perca
flavescens). Other taxa have only
been tested once or within one study at different temperatures. For species tested several times, the minimum and maximum LC50 values can vary by up to one order of magnitude, which is explained by differences in test conditions and life stages tested. For cold water fish, sensitivity is usually higher at lower temperature and eggs and fry are usually less sensitive
then juveniles.For a conservative analysis, the selection of tests was restricted to flow-through conditions and only the lowest LC50 per species was used (Table 27), resulting in a refined SSD curve (Species sensitivity distribution 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 SSD provides a HC5 of 26 μg/l, which predicts that for 95% of species the LC50 is higher than this value, corresponds to the lowest LC50 of 27 μg/l reported for rainbow trout (Oncorhynchus mykiss). This lowest reported LC50 was derived from a test with a water temperature at 6°C.
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. These data indicate that a factor of 5 applied to an LC50 should predict a safe concentration for survival. NOTE: Any of data in this dataset are disseminated by the European Union on a right-to-know basis and this is not a publication in the same sense as a book or an article in a journal. The right of ownership in any part of this information is reserved by the data owner(s). The use of this information for any other, e.g. commercial purpose is strictly reserved to the data owners and those persons or legal entities having paid the respective access fee for the intended purpose.
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