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EC number: 206-743-9 | CAS number: 372-09-8
- 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
Endpoint summary
Administrative data
Description of key information
ORAL
Oral LD50 Combined = 1010 mg/kg bw (95% C.I. 831 - 1228).
Cyanoacetic acid is of SLIGHT Toxicity based on the LD50 in males and females(OECD GHS Toxicity Category IV).
DERMAL
Dermal LD50 Combined > 2000 mg/kg bw (no mortality occurred, limit test).
Cyanoacetic acid is of LOW Toxicity based on an LD50 exceeding 2000 mg/kg bw.
INHALATION
LC50 Males = 1.4 mg/L.
LC50 Females = 2.6 mg/L.
LC50 Combined = 1.9 mg/L.
Cyanoacetic acid is of SLIGHT Toxicity based on the LD50 in males (OECD GHS Toxicity Category IV).
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 1 010 mg/kg bw
Acute toxicity: via inhalation route
Endpoint conclusion
- Dose descriptor:
- LC50
- Value:
- 0.002 mg/m³ air
Acute toxicity: via dermal route
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 2 000 mg/kg bw
Additional information
ORAL
In an acute oral toxicity study (BASF 1980), groups of fasted Sprague-Dawley (5/sex) were given a single oral dose of Cyanoacetic acid (purity not given) in water at doses of 464, 681, 1000, 1470, or 2150 mg/kg bw and observed for 14 days.
Oral LD50 Combined = 1010 mg/kg bw (95% C.I. 831 - 1228).
Clinical signs of toxicity were unspecific in nature and occurred at doses of 1000 and more. Mortality was 0/10, 1/10, 7/10, 7/10 and 10/10 in the groups administered 464, 681, 1000, 1470, and 2150 mg/kg bw, respectively; all deaths occurred within 24 hours after dosing. Stagnation/loss of body weight was observed during the first days after dosing at 1000 and 1470 mg/kg bw in both sexes. At the end of the observation period, body weight gain of the females were similar in all groups, whereas those of 1000- and 1470-mg/kg bw males was still slightly retarded when compared to the lower dose groups. Pathology of the decedents revealed unspecific changes of the heart, liver, and stomach while no pathological abnormalities were found in survivors that had been sacrificed at the end of the observation period.
DERMAL
In an acute dermal toxicity study (BASF 1980), groups of male and female Sprague-Dawley rats were dermally exposed to Cyanoacetic acid (purity not given) in water at a dose of 2000 mg/kg bw. Animals then were observed for 14 days.
Dermal LD50 Combined > 2000 mg/kg bw (no mortality occurred, limit test).
Signs of systemic toxicity were unspecific in nature. Signs of local irritation were noted at the application sites. Slight erythema, marked edema, and yellow-coloured residues of the test substance were observed at 24 hours after beginning of application. At 7 days after beginning of application, scaling and partially encrustation was observed. No pathological findings were observed.
INHALATION
In an acute inhalation toxicity study (BASF 1981), groups of young adult Sprague-Dawley rats (10/sex) were exposed by inhalation route to Cyanoacetic acid (purity 97%) in water for 4 hours to nose/head only at concentrations of 0.25, 0.65, 1.53, 2.56, or 3.94 mg/L. Animals then were observed for 14 days.
LC50 Males = 1.4 mg/L.
LC50 Females = 2.6 mg/L.
LC50 Combined = 1.9 mg/L.
Clinical signs of toxicity were mostly unspecific in nature (secretion at the eyes and nose, salivation, eyelid closure, swollen snouts with reddish encrustations, dyspnea, retarded pain reflex, tremor, squatting posture, high-legged gait, anemic paleness, and/or piloerection) and occurred at all dose levels. The symptoms persisted throughout the observation period at dose levels of 1.53 mg/L and more, but were reversible at lower concentrations. Mortality was 0/20, 3/20, 8/20, 9/20, and 19/20 in the groups exposed to 0.25, 0.65, 1.53, 2.56, or 3.94 mg/L, respectively; late deaths were observed. Animals exposed to 3.94 mg/L lost weight throughout the study. Body weight gain was retarded at 2.56 and 1.53 mg/L for both sexes and at 0.65 mg/L for males. No effect on body weight gain was noted at 0.25mg/L. Pathology of the decedents revealed changes of the heart, lungs, and liver while no pathological abnormalities were found in survivors that had been sacrificed at the end of the observation period.
Justification for classification or non-classification
Based on the oral LD50 of approximately 1010 mg/kg bw in rats, Cyanoacetic acid has to be classified as “harmful if swallowed” according to the Directive 67/548/EC. According to the GHS criteria, Cyanoacetic acid has to be classified as follows: Acute Oral Toxicity Cat. 4.
Based on the dermal LD50 of > 2000 mg/kg bw in rats, there is no need for classification according to the Directive 67/548/EC. According to the GHS criteria: On the basis of the available data on acute dermal toxicity, there is no need for classification.
Based on the inhalation LD50 of approximately 1.9 mg/L, Cyanoacetic acid has to be classified as “harmful by inhalation” according to the Directive 67/548/EC. According to the GHS criteria, Cyanoacetic acid has to be classified as follows: Toxicity by Inhalation Cat. 4.
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