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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 482-020-3 | 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
Toxicological Summary
- Administrative data
- Workers - Hazard via inhalation route
- Workers - Hazard via dermal route
- Workers - Hazard for the eyes
- Additional information - workers
- General Population - Hazard via inhalation route
- General Population - Hazard via dermal route
- General Population - Hazard via oral route
- General Population - Hazard for the eyes
- Additional information - General Population
Administrative data
Workers - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 1.18 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 35
- Dose descriptor starting point:
- NOAEL
- Value:
- 50 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 44 mg/m³
- Explanation for the modification of the dose descriptor starting point:
The Starting point for the DNEL derivation (long term systemic, inhalation) is taken as the NOAEL for systemic effects of 50 mg/kg bw from the 2 - generation reproductive toxicity study.
The critical effects in this study were increases in Kidney weight in the top dose (150 mg/kg bw) in the parent and F1 parent generations.
Starting NOAEL = 50 mg/kg bw/day. Converted to Dose descriptor starting point according to ECHA guidance (practical guide 14). 50/0.38 x 0.67 x 0.5 = 44 mg/m3 ; It is assumed that the oral absorption rate is 50% of that of the inhalation absorption. This is a conservative assessment since the available TK data demonstrate >90% absorption via the oral route.
- AF for dose response relationship:
- 1
- Justification:
- Clear dose response with minimal toxicological findings up to the highest dose in the key study
- AF for differences in duration of exposure:
- 3
- Justification:
- A multigeneration study is used as the starting point which is similar in duration of the animals to a 90 day study.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- not required due to route to route extrapolation method
- AF for other interspecies differences:
- 2.5
- Justification:
- ECHA default
- AF for intraspecies differences:
- 5
- Justification:
- ECHA default
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA Default
- AF for remaining uncertainties:
- 1
- Justification:
- not required
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.45 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 6
- Dose descriptor:
- NOAEC
- AF for dose response relationship:
- 1
- Justification:
- ECHA default
- AF for differences in duration of exposure:
- 2
- Justification:
- The local effects are associated with concentration in the upper respiratory tract rather than the duration of exposure. Experience demonstrates that increasing the duration of exposure does not result in a non-irritating exposure level becoming irritating. Therefore a reduced factor of 2 has been allocated.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- ECHA Default
- AF for other interspecies differences:
- 1
- Justification:
- human will be less sensitive than rats in inhalation due to the local effect
- AF for intraspecies differences:
- 3
- Justification:
- Deviation from ECHA default due to lower variability for local effects - this approach is consistent with that adopted by SCOEL when setting OELS based on local irritation effects.
- AF for the quality of the whole database:
- 1
- Justification:
- ECHA Default
- AF for remaining uncertainties:
- 1
- Justification:
- not required
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- low hazard (no threshold derived)
Additional information - workers
Due to the potential for inhalation exposure (volatility is low, but uses involve spraying of the substance as part of a 2 component coating system), DNELs have been derived for local and systemic effects via inhalation (long term only).
The toxicity of this substance is limited to local effects only (Specifically irritation to the skin, eyes, respiratory system, and skin sensitising potential). In repeated dose toxicity studies there were no treatment related systemic effects (refer to repeated dose and reproductive toxicity sections). As such, protecting against local effects will protect against any systemic toxicity.
The local effects DNEL for inhalation (long term) is derived using the 90 -day inhalation study.
The systemic toxicity DNEL for inhalation (long term) is derived using the 2 -gen oral toxicity study in rats. The 90 -day inhalation study is not used as the starting point for the DNEL as the top dose was limited by local effects, and as such, although it was a NOEL for systemic toxicity, it is likely the actual NOEL for systemic toxicity is higher. Therefore the systemic toxicity NOAEL from the 2 -gen study is used with the appropriate assessment factors to account for dose duration.
DNELS for the dermal route of exposure have not been calculated since this substance is a skin sensitiser. Protection against sensitising potential will therefore protect against potential local irritation effects and systemic toxicity. Please refer to Sections 9 and 10 of the chemical safety report, and section 11 of the IUCLID for the personal protective equipment recommendations when handling this substance.
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- medium hazard (no threshold derived)
- Most sensitive endpoint:
- sensitisation (skin)
- Route of original study:
- Dermal
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
General Population - Hazard via oral route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - General Population
There are no consumer uses for this substance
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.