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EC number: 200-315-5 | CAS number: 57-13-6
- 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
Urea is of very low acute toxicity by all routes investigated. The acute oral LD50 of urea is reported to be 14.3-15.0 g/kg bw in the rat and 11.5-13.0 g/kg bw in the mouse. The acute subcutaneous LD50 is reported to be 8.2-9.4 g/kg bw in the rat and 9.2-10.7 g/kg bw in the mouse. The acute intravenous LD50 of urea is reported to be 5.3-5.4 g/kg bw in the rat and 4.6-5.2 g/kg bw in the mouse.
Key value for chemical safety assessment
Acute toxicity: via oral route
Endpoint conclusion
- Dose descriptor:
- LD50
- Value:
- 14 300 mg/kg bw
Additional information
Acute oral toxicity
Urea is of very low acute oral toxicity in the rat and mouse. Sato et al (1977) report LD50 values of 14.3 (12.9 -15.9) and 15.0 (13.4 -16.8) g/kg bw in male and female rats; LD50 values of 11.5 (10.6 -12.5) and 13.0 (11.0 -15.4) g/kg bw in the mouse. Urea is of generally low acute oral toxicity in most species but higher toxicity is noted in ruminants due to the generation of ammonia by gastric flora. Stiles et al (1970) report an LDlo of approximately 600 mg/kg bw in cattle.
Acute dermal toxicity
No data are available: a waiver is proposed for this endpoint. Urea is demonstrated to be of very low acute toxicity by the oral, subcutaneous and intravenous routes in the rat and mouse. Testing for acute dermal toxicity is not justified on scientific grounds and for reasons of animal welfare. Specifically, the very low toxicity of urea by the subcutaneous and intravenous routes indicates that dermal toxicity would also be very low, even assuming rapid and total dermal penetration.
Acute inhalation toxicity
No data are available: a waiver is proposed for this endpoint. The substance is a non-volatile solid and is produced as crystals with a particle size of >100 µm. There is therefore no potential for inhalation exposure. In addition, the substance has been demonstrated to be of very low toxicity by other routes of exposure. Testing for acute inhalation toxicity is therefore not justified on scientific grounds or based on exposure considerations.
Acute toxicity by other routes of exposure
Urea is also of very low acute toxicity by the subcutaneous route. Sato et al (1977) report LD50 values of 9.4 (8.2 -10.8) and 8.2 (7.1 -9.5) g/kg bw in male and female rats and LD50 values of 9.2 (8.6 -9.8) and 10.7 (9.5 -12.1) g/kg bw in male and female mice. It is notable that the subcutaneous LD50 values are greatly in excess of the limit dose for acute dermal toxicity testing.
Urea is of very low toxicity following intravenous administration. Sato et al (1977) report LD50 values of 5.4 (4.9 -5.9) and 5.3 (4.8 -5.7) g/kg bw in male and female rats and LD50 values of 4.6 (4.3 -4.9) and 5.2 (4.8 -5.6) g/kg bw in male and female mice, respectively.
Justification for classification or non-classification
Urea is of inherently very low toxicity by all routes investigated. No data are available for the inhalation route, however low toxicity can also be predicted for this route. No classification is proposed for acute toxicity according to CLP.
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