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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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- 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 only (non GLP, non guideline).
Cross-reference
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- publication
- Title:
- Pharmacology of cyanate. I. general Effects on experimental animals
- Author:
- Cerami, A.; Allen, T.A..; Graziano, J.H. deFuria, F.G.; Manning, J.M.; Gillette, P.N.
- Year:
- 1 973
- Bibliographic source:
- J. Pharmacol. Exp. Ther. 185: 653-666, 1973
Materials and methods
- Objective of study:
- distribution
- excretion
Test guideline
- Qualifier:
- no guideline followed
- GLP compliance:
- not specified
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
Constituent 1
- Radiolabelling:
- yes
Test animals
- Species:
- mouse
- Strain:
- other: B6/D2 F1
- Sex:
- female
- Details on test animals or test system and environmental conditions:
- Source: The Jackson Laboratory (Bar Harbor, Maine, USA)
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- water
- Details on exposure:
- not indicated.
- Duration and frequency of treatment / exposure:
- Test 1: single exposure
Test 2: 156 injections (26 weeks), after 78 injections (13 weeks) injection in some mice were stopped and the distribution of 14C was observed for 130 days without further injections.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Test 1: Mice were given a single dose of 10 µmol 14C-sodium cyanate i.p.
Test 2: Mice were injected daily (six times per week) with 0.1 ml of 0.1 M NaN14CO
- No. of animals per sex per dose / concentration:
- Test 1: 1 mouse
Test 2: no data - Control animals:
- not specified
- Positive control reference chemical:
- no
- Details on study design:
- Test 1: single exposure to one mouse, determination of 14C concentration in blood, urine and organs.
Test 2: Female mice were injected daily (six times per week) with 0.1 ml of 0.1 M NaN14CO. At intervals the animals were sacrificed and the distribution of 14C radioactivity within various organs were determined. After 78 injections (13 weeks) injection in some mice were stopped and the distribution of 14C was observed at intervals for maximal 130 days without further injections. - Details on dosing and sampling:
- no details given
- Statistics:
- no details given
Results and discussion
- Preliminary studies:
- Test 1: Approximately 75% of the injected dose is broken down to form 14CO2 during the first six hours and another 8-10% is found in the urine. In oder to determine wether the 14CO2 came from breakdown of cyanate in an acidified urine or directly as CO2 from the lungs, a rat with an exteriorized bladder was anesthetized and injected with 10 µmol of 14C-cyanate. The cranial half of the animal was placed in a tight-fitting plastic bag with inlet and outlet openings; the expired air was then drawn by vacuum through an acid trap and then ethanolamine trap. The urine was also collected into ethanolamine and the radioactivity of both the exired CO2 and the urine was determined in a liquid scintillation counter. This experiment revealed the same distribution of radioactivity from the administered cyanate and pointed to a direct release as CO2 from the lungs.
7.5 % of the injected dose reacted specifically with amino-terminal valine of hemoglobin; this amount is significantly higher than in many of the other organs or tissues of the body. The muscle and the bones are the only parts with substantial amounts of radioactivity. Less than 3 % of the injected dose reacted with tissues other than red blood cells, bones and muscle. Negligible amounts of radioactivity were found in pituitary, adrenal and thyriod glands and in the ovaries.
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- not observed
- Details on distribution in tissues:
- Test 2: It is apparent from the data (distribution see table below) that the amount of radioactivity in the different organs plateaus after a different number of injections and probably refects a steady state of proteins being labeled with cyanate equaling the rate of labeled proteins being catabolized. The loss of radioactivity from the various organs after stopping the injections follows different rates and in fact might estimate the turnover of these proteins.
- Details on excretion:
- Evolved as CO2: 72.2 %
Urine: 7.0 %
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- CO2
Any other information on results incl. tables
Distribution of14C cyanate in a mouse after the injection i.p. of 10 µmol of14C cyanate
Organ/route of excretion |
% of injected dose |
Evolved as14CO2 |
72.2 |
Urine |
7.0 |
Erythrocytes |
7.5 |
Bones |
3.3 |
Muscle |
2.1 |
Skin |
0.8 |
Liver |
0.7 |
Serum proteins |
0.5 |
Intestine |
0.4 |
Brain |
0.17 |
Heart |
0.08 |
Stomach |
0.06 |
Kidney |
0.05 |
Lungs |
0.05 |
Spleen |
0.01 |
Other: ovary, uterus, thymus, fat |
0.01 |
Total recovery |
94.9 |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): no bioaccumulation potential based on study results
Approximately 75% of the injected dose is broken down to form 14CO2 during the first six hours and another 8-10% is found in the urine. - Executive summary:
In a distribution/excretion study 14C sodium cyanate was administered to female mice in single and multiple doses i.p. at dose levels of 10 µmol and 0.1 ml of 0.1 M solution. After 78 injections (13 weeks) injection in some mice were stopped and the distribution of 14C was observed at intervals for maximal 130 days without further injections.
Single dosing:
Approximately 75% of the injected dose is broken down to form 14CO2 during the first six hours and another 8-10% is found in the urine. In oder to determine whether the 14CO2 came from breakdown of cyanate in an acidified urine or directly as CO2 from the lungs, a rat with an exteriorized bladder was anesthetized and injected with 10 µmol of 14C-cyanate. The cranial half of the animal was placed in a tight-fitting plastic bag with inlet and outlet openings; the expired air was then drawn by vacuum through an acid trap and then ethanolamine trap. The urine was also collected into ethanolamine and the radioactivity of both the expired CO2 and the urine was determined in a liquid scintillation counter. This experiment revealed the same distribution of radioactivity from the administered cyanate and pointed to a direct release as CO2 from the lungs. 7.5 % of the injected dose reacted specifically with amino-terminal valine of hemoglobin; this amount is significantly higher than in many of the other organs or tissues of the body. The muscle and the bones are the only parts with substantial amounts of radioactivity. Less than 3 % of the injected dose reacted with tissues other than red blood cells, bones and muscle. Negligible amounts of radioactivity were found in pituitary, adrenal and thyroid glands and in the ovaries.
Multiple dosing:
It is apparent from the data that the amount of radioactivity in the different organs plateaus after a different number of injections and probably reflects a steady state of proteins being labelled with cyanate equalling the rate of labelled proteins being catabolized. The loss of radioactivity from the various organs after stopping the injections follows different rates and in fact might estimate the turnover of these proteins.
This distribution/excretion study in the mouse is classified acceptable.
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