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Diss Factsheets
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EC number: 202-506-9 | CAS number: 96-45-7
- 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
Biodegradation in soil
Administrative data
Link to relevant study record(s)
Description of key information
Under field conditions, ETU undergoes degradation processes and partial mineralization in a few days to a few weeks. Its main metabolite (ethyleneurea, CAS 120-93-4) is not considered as PBT or vPvB or harmful to the environment according to CLP criteria (EC 1272/2008 regulation) according to its disseminated dossier. Considering ETU as totally persistent would therefore be a worst-case assumption for chemical safety assessment. Under this assumption, ETU is not PBT/vPvB and the soil RCRs are all inferior to 1. Therefore, the chemical safety assessment performed under the worst-case assumption does not indicate the need to further investigate ETU degradation in soil.
Key value for chemical safety assessment
Additional information
Some studies using radiolabelled ETU show that ETU undergoes rapid degradation and partial mineralization within a fews days or weeks in soil. The process is mainly temperature dependent. All studies were performed with agricultural soils that may have been adapted to pesticides in the past. Taken together, the results indicate that ETU can degrade and mineralize in those soils and that its main metabolite is ethyleneurea (CAS 120 -93 -4). According to its disseminated dossier, ethyleneurea is readily biodegradable, not expected to bioaccumulate (log Kow = -1.16) and not hazardous to the environment according to CLP criteria (EC 1272/2008 regulation). Considering total persistency of ETU in soil would therefore be a worst case assumption. Under this assumption, no risk is identified for soil living organisms under any exposure scenario of the chemical safety assessment (RCR < 1). ETU should not be considered as PBT or vPvB as ETU is not expected to bioaccumulate (log Kow < 3). Therefore, following annex IX, section 9.2.1.3, column 2 of the REACH regulation EC 1907/2006, no further testing is required on biodegradation of ETU in soils as the chemical safety assessment does not indicate the need to.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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