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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
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EC number: - | 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
Additional information
On the basis of experimental data in the form of a biodegradability screening study (OECD 301B), Diurea 8 is not considered readily biodegradable (Harlan 2012). Due to the very low predicted water solubility of Diurea 8 (Dawick 2012), the hydrolysis and degradation in surface water endpoints have been waived. The sediment and soil simulation testing have been waived on the basis that the Chemical Safety Assessment has not indicated a need to further investigate these endpoints. Diurea 8 only ever occurs within a base oil grease designed to minimise leaching and the log octanol-water partition coefficients for constituents are estimated to be above 6 (Dawick 2012) which indicates Diurea 8 is likely to reside within the hydrophobic base oil grease matrix. The predicted physical-chemical properties (water solubility, vapour pressure and octanol-water partition coefficient), coupled with the fact that Diurea 8 is only ever manufactured within a base oil grease indicate that environmental exposures of Diurea 8 to air, soil and water compartments will be severely limited. In the event that constituents of Diurea 8 leached out of the base oil grease matrix, environmental partitioning would be primarily to soil or sediment. However, this process is considered highly unlikely and the exposure concentrations of Diurea 8 which would be available for bioaccumulation are extremely limited.
The reactions to form Diurea 8 occur in-situ during the grease manufacturing process and consequently Diurea 8 only ever exists within the base oil grease matrix. The matrix effect, as recognised by the OECD Lubricant Emission Scenario document (OECD 2004), needs to be taken into account as the process of manufacturing the thickener in an inert base oil is likely to influence factors such as the exposure levels and availability of Diurea 8 to man and the environment. In the grease manufacturing process unique interactions, more appropriately defined as intermolecular interactions (rather than chemical bonding), occur between the hydrocarbons within the base oil and the Diurea 8 thickener constituents. The chemistry is complex and the intermolecular interactions between the thickener and hydrocarbons within the base oil do not strictly fall under the definitions of a reaction product nor do they act as a simple mixture of components. In realistic use scenarios, the Diurea 8 thickener constituents will be contained within base oil, with the formulated greases specifically designed to minimise the leaching of the thickener to the external environment.
Reference
OECD (2004) OECD Series on emission scenario documents, Number 10: Emission scenario document on lubricants and lubricant additives. Environment directorate: Joint meeting of the chemicals committee and the working part on chemicals, pesticides and biotechnology. ENV/JM/MONO(2004)21
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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