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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
For the assessment of the short-term toxicity of thiourea to fish five different studies are available. Species tested werePimephales promelas,Leuciscus idus(L.), Hong Kong guppy,Danio rerio,andOryzias latipes. In none of the studies could an LC50value be obtained that would be close to the regulatory cut-off value of 100 mg/L for classification. Therefore, classification of thiourea for acute toxicity to fish is not warranted.
The 14-d subchronic NOEC of thiourea to fish was determined to be 5000 mg/L.
The 96-hr effect concentrations of thiourea to the green algaScenedesmus subspicatusChodat used in the risk assessment of the substance are as follows: EC10= 0.3 mg/L, and EC50= 3.8 mg/L.
Conflicting results are available regarding the short-term toxicity of thiourea to daphnia. Several non-standard data of low reliability are available that provide information on the acute toxicity of thiourea towards daphnia. Reported EC50values were determined after 24 to 96 hours exposure and range between 1.8 mg/L and 4000-6000 mg/L. However, consistent results are reported with regard to the long-term toxicity to daphnia. All 21-d NOEC values (reproduction) are in the range of 0.1 to 1 mg/L. Following the precautionary principle, the lowest reported result of NOEC (21-d) of 0.1 mg/L is used in the assessment of thiourea.
Regarding the toxicity of thiourea to microorganisms, it could be demonstrated in several studies that thiourea is toxic to microorganisms, with nitrification being the most sensitive process. Toxic effects (75 % nitrification inhibition) were reported at thiourea concentrations ranging from 0.76 mg/L to 0.076 mg/L. However, acclimatisation to thiourea occurs over time, resulting in the microorganism's capability of degrading thiourea. In a study conducted by Tomlinson et al. (1966) incremental increase of thiourea concentrations up to 76 mg/l correlated with a gradual increase of the degradation products nitrate and sulphate, indicating complete mineralisation of thiourea. An EC50of 0.35 mg/l could be established with respect to the inhibitory effect of thiourea to STP microorganisms. This value was chosen for the risk assessment as it is the only result obtained making use of a (modified) standard guideline (ISO 9509).
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