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EC number: 200-543-5 | CAS number: 62-56-6
- 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
Available literature on phototransformation of thiourea in air reports that the substance is degraded from 0.23 to 4.7 % under the conditions of the GSF test (Schmidt-Bleek et al., 1982) and when irradiated at a wavelength of 290 nm (Freitag et al., 1985), respectively. In addition, Meylan & Howard (1993; as cited in the Hazardous Substances Data Bank) determined an atmospheric half-life t1/2of about 3 hours at an atmospheric concentration of 5.0E+05 hydroxyl radicals per cm³.
Regarding the phototransformation of thiourea in water, the calculated half-life of thiourea in sunlit natural water at a hydroxyl radical concentrations of 1.0E-17 M is 171 days (HSDB, citing results of Mill et al. (1980).
HSDB states that Kolyada observed measurable degradation in sterilized soils, although the mechanism for the degradation was not studied. The extent of degradation is also not reported.
Two data sources are available that describe the hydrolysis of thiourea at different pH. Schmidt-Bleek et al. (1982) report that thiourea is stable to hydrolysis at pH 4, 7, and 9. These results are consistent with the findings of Korte & Greim (1981) who observed no hydrolysis of thiourea at pH 1.2, 3, 7, and 9 under the conditions of OECD guideline A-79.74D.
Additional information
Available literature on phototransformation of thiourea in air reports that the substance is degraded from 0.23 to 4.7 % under the conditions of the GSF test (Schmidt-Bleek et al., 1982) and when irradiated at a wavelength of 290 nm (Freitag et al., 1985), respectively. In addition, Meylan & Howard (1993; as cited in the Hazardous Substances Data Bank) determined an atmospheric half-life t1/2 of about 3 hours at an atmospheric concentration of 5.0E+05 hydroxyl radicals per cm³.
Regarding the phototransformation of thiourea in water, the calculated half-life of thiourea in sunlit natural water at a hydroxyl radical concentrations of 1.0E-17 M is 171 days (HSDB, citing results of Mill et al. (1980).
HSDB states that Kolyada observed measurable degradation in sterilized soils, although the mechanism for the degradation was not studied. The extent of degradation is also not reported.
Two data sources are available that describe the hydrolysis of thiourea at different pH. Schmidt-Bleek et al. (1982) report that thiourea is stable to hydrolysis at pH 4, 7, and 9. These results are consistent with the findings of Korte & Greim (1981) who observed no hydrolysis of thiourea at pH 1.2, 3, 7, and 9 under the conditions of OECD guideline A-79.74D.
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