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EC number: 213-030-6 | CAS number: 917-61-3
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1973
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: public available literature (non GLP, non Guideline) Read across to sodium cyanate. For justification of read across see endpoint summary.
Data source
Reference
- Reference Type:
- publication
- Title:
- Pharmacology of cyanate. II. Effects on the endocrine system
- Author:
- Graziano, J.H.; Thornton; Y. S.; Leong, J. K.; Cerami, A.
- Year:
- 1 973
- Bibliographic source:
- Journal of pharmacology and experimental therapeutics, Vol. 185, No. 3, page 667-675
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Public available literature. No guideline indicated. For details on method see materials and methods section.
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- Sodium cyanate
- EC Number:
- 213-030-6
- EC Name:
- Sodium cyanate
- Cas Number:
- 917-61-3
- Molecular formula:
- CNO.Na
- IUPAC Name:
- sodium cyanate
- Details on test material:
- no details given
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- Source: Holtzman Company (Madison, Wisconsin, USA)
weight: 200-250 g
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- water
- Details on exposure:
- Adult female rats were injected i.p. with 25 mg/kg bw/day of sodium cyanate (0.154 M) for 14 days before cohabitation and throughout pregnancy. Control rats received an equivalent amount of NaCl.
- Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- no data
- Details on mating procedure:
- no detail given.
- Duration of treatment / exposure:
- 14 days before cohabitation and throughout pregnancy
- Frequency of treatment:
- daily
- Duration of test:
- 14 days before cohabitation and throughout pregnancy
- No. of animals per sex per dose:
- 8 females per treatment group
- Control animals:
- yes, plain diet
- Details on study design:
- no further detail given.
Examinations
- Maternal examinations:
- - number of matings
- number of young born per litter
- birth weights of the litter
- vaginal smears - Ovaries and uterine content:
- - gross pathology of ovaries and testes
- Fetal examinations:
- - gross pathology:
Twenty newborn rats from each group were chosen at random and sacrificed with ether. Skeletal whole mounts were prepared by the alizarin red method (Dawson, 1926). - Statistics:
- mean and standard deviation
- Indices:
- not given
- Historical control data:
- not given
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:no effects
Details on maternal toxic effects:
Two groups of female rats were injected with 25 mg/kg bw/day of either sodium cyanate or NaCl for 14 days before cohabitation and throughout pregnancy. A normal four or five day estrus cycle was observed in all animals prior to mating. There were no significant differences in the number of successful matings.
Effect levels (maternal animals)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 25 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: overall effects
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:no effects
Details on embryotoxic / teratogenic effects:
No differences in number of young per litter or the birth weights of the pups. In addition, there were no gross or skeletal abnormalities of the young of the cyanate-injected animals.
Effect levels (fetuses)
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 25 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- other: overall effects
Overall developmental toxicity
- Key result
- Developmental effects observed:
- no
Any other information on results incl. tables
In a developmental toxicity study sodium cyanate was administered to 8 female Sprague-Dawley rats/dose i.p. at dose levels of 0 and 25 mg/kg bw/day.
Two groups of female rats were injected with 25 mg/kg bw/day of either sodium cyanate or NaCl for 14 days before cohabitation and throughout pregnancy. A normal four or five day estrus cycle was observed in all animals prior to mating. There were no significant differences in the number of successful matings.
The maternal LOAEL can not be determined as no effects occurred. The maternal NOAEL is 25 mg/kg bw/day.
No differences in number of young per litter or the birth weights of the pups were observed. In addition, there were no gross or skeletal abnormalities of the young of the cyanate-injected animals.
The developmental LOAEL can not be determined as no effects occurred. The developmental NOAEL is 25 mg/kg bw/day.
The developmental toxicity study in the rat is classified acceptable.
Applicant's summary and conclusion
- Conclusions:
- The i.p. administration of 25 mg/kg bw/day of sodium cyanate to rats had no effect on reproductive capacity and was not teratogenic.
- Executive summary:
In a developmental toxicity study sodium cyanate was administered to 8 female Sprague-Dawley rats/dose i.p. at dose levels of 0 and 25 mg/kg bw/day.
Two groups of female rats were injected with 25 mg/kg bw/day of either sodium cyanate or NaCl for 14 days before cohabitation and throughout pregnancy. A normal four or five day estrus cycle was observed in all animals prior to mating. There were no significant differences in the number of successful matings. The maternal LOAEL can not be determined as no effects occurred. The maternal NOAEL is 25 mg/kg bw/day.
No differences in number of young per litter or the birth weights of the pups were observed. In addition, there were no gross or skeletal abnormalities of the young of the cyanate-injected animals. The developmental LOAEL can not be determined as no effects occurred. The developmental NOAEL is 25 mg/kg bw/day.
The developmental toxicity study in the rat is classified acceptable.
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