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Diss Factsheets
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EC number: 940-730-5 | CAS number: -
- 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
Reliable toxicity tests with the registration substance have been carried out on earthworms, honeybees and higher plants.
Toxicity to soil macroorganisms except arthropods
A 28 day E(L)C50 value of >2000 mg/kg dry soiland NOEC value of 2000 mg/kg dry soil (nominal concentrations) (highest concentration tested) have been determined for effects of the test substance on survival and growth ofEisenia fetida.
A 56 day EC50 value of 777 mg/kg dry soil and NOEC value of 222 mg/kg dry soil (nominal concentrations) have been determined for the effects of the test substance on reproduction ofEisenia fetida.
Toxicity to terrestrial arthropods
A 48 hour LD50 value of >100 μg product/bee and 48 hour NOEL value of 100 μg product/bee (nominal concentration) (highest concentration tested) have been determined in an oral test for the effects of the test substance on mortality ofApis mellifera.
A 48 hour LD50 value of >100 μg product/bee and 48 hour NOEL value of 100 μg product/bee (nominal concentration) (highest concentration tested) have been determined in a contact test for the effects of the test substance on mortality ofApis mellifera.
Toxicity to terrestrial plants
A 21 day EC50 value of >1000 mg/kg dry soil and NOEC value of 1000 mg/kg dry soil (nominal concentrations) (highest concentration tested) have been determined for the effects of the test substance on seedling emergence, growth and phytotoxicity of wheat.
A 21 day EC50 value of >1000 mg/kg dry soil and NOEC value of 1000 mg/kg dry soil (nominal concentrations) (highest concentration tested) have been determined for the effects of the test substance on seedling emergence, growth and phytotoxicity of turnip.
A 21 day EC50 value of >1000 mg/kg dry soil and NOEC value of 1000 mg/kg dry soil (nominal concentrations) (highest concentration tested) have been determined for the effects of the test substance on seedling emergence, growth and phytotoxicity of buckwheat.
A 21 day EC50 value of >1000 mg/kg dry soil and NOEC value of 1000 mg/kg dry soil (nominal concentrations) (highest concentration tested) have been determined for the effects of the test substance on seedling emergence and phytotoxicity of dwarf bean.
A 21 day EC50 value of >1000 mg/kg dry soil and NOEC value of 309 mg/kg dry soil (nominal concentrations) have been determined for the effects of the test substance on growth of dwarf bean.
A 21 day EC50 value of >1000 mg/kg dry soil and NOEC value of 1000 mg/kg dry soil (nominal concentrations) (highest concentration tested) have been determined for the effects of the test substance on seedling emergence, growth and phytotoxicity of ryegrass.
A 21 day EC50 value of >1000 mg/kg dry soil and NOEC value of 1000 mg/kg dry soil (nominal concentrations) (highest concentration tested) have been determined for the effects of the test substance on seedling emergence, growth and phytotoxicity of tomato.
Additional information
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.