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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 922-435-3 | 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
Aquatic toxicity endpoints are based on test data following standard guidelines. All data are therefore considered to be reliable and relevant for the endpoint concerned.
Short-term toxicity to aquatic invertebrates
In acute ecotoxicity studies with Daphnia magna, Diurea 8 and Tetraurea 2 (in base grease) had 48-Hour EL50 (effective loading rate) values of greater than 100 mg/L WAF. The No Observed Effect Loading Rate (NOELR) for both Diurea 8 and Tetraurea 2 was 100 mg/L WAF.
The toxicity of Reaction product of m-tolylidene diisocyanate and cyclohexylamine and cyclohex-1,2-ylenediamine and (Z)-octadec-9-enylamine (in isolated form) toDaphnia magnawas investigated in an OECD guideline 202 study and the 48-hour EC50, based on nominal concentrations, was determined to be > 100 mg/L, the only concentration tested. The 48-hour NOEC was determined to be ≥ 100 mg/L.
Based on study results for category members, no toxicity to aquatic invertebrates is expected at the limit of solubility for substances within the TDI-I category.
Toxicity to aquatic algae and cyanobacteria
The effects of two TDI-I category members on the growth of Pseudokirchneriella subcapitata were investigated in two separate studies (one conducted in base grease and one conducted on the isolated thickener). The studies followed OECD guideline 201 and used water accommodated fractions. Both studies demonstrated EL50 (effective loading rate) values of greater than 100 mg/L WAF. Correspondingly the No Observed Effect Loading Rates (NOELR) were 100 mg/L WAF.
One study conducted with Diurea 8 in base grease did show effects at <100 mg/L, but this was considered to be due to impurities in the sample, and therefore the study was repeated on both the isolated substance and the substance in base grease. Both of these studies showed EL50 values >100 mg/L WAF and NOELR values of 100 mg/L WAF. The first study is therefore disregarded due to impurities in the test sample.
Based on the available data for category members, TDI-I substances are not considered to be toxic to algae at the limit of solubility.
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.