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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 500-057-6 | CAS number: 27104-30-9
- 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:
- 1.4 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):
- 37.5
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 52.9 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- for route extrapolation conditional decline (bw loss, decreased body weight gain and food consumption) is taken as systemic toxicity.
- AF for dose response relationship:
- 1
- Justification:
- starting point is mid-dose NOAEL in a subacute (gavage) study + DRF study.
- AF for differences in duration of exposure:
- 3
- Justification:
- The extrapolation factor from short term toxicity to the long-term scenario for a substance causing primary local toxicity is reduced by factor 2. For local irritation the concentration is in most cases the relevant parameter, and prolongation of exposure is expected to influence the severity of effect and morphology of changes, but not the NOAEL/NOAEC.
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- allometric scaling is not applicable for inhalation
- AF for other interspecies differences:
- 2.5
- Justification:
- default (not justified for local tox.)
- AF for intraspecies differences:
- 5
- Justification:
- worker population
- AF for the quality of the whole database:
- 1
- Justification:
- GLP compliant study data
- AF for remaining uncertainties:
- 1
- Justification:
- No AF(2) for oral to inhalation extrapolation is applied as there is no scientific rational that the substance absorption by the oral route is less efficient than pullmonary absorption. Equal absorption for oral ingestion and inhalation has been assessed from physico-chemical properties of the substance.
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 4.2 mg/m³
- Most sensitive endpoint:
- irritation (respiratory tract)
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 12.5
- DNEL extrapolated from long term DNEL
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 52.9 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- for route extrapolation conditional decline (decreased body weight gain and decreased food consumption) is taken as systemic toxicity.
- AF for dose response relationship:
- 1
- Justification:
- starting point is mid-dose NOAEL in a subacute (gavage) study
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- not applicable for inhalation
- AF for other interspecies differences:
- 2.5
- Justification:
- default
- AF for intraspecies differences:
- 5
- Justification:
- worker population
- AF for the quality of the whole database:
- 1
- Justification:
- GLP compliant study data
- AF for remaining uncertainties:
- 1
- Justification:
- No AF(2) for oral to inhalation extrapolation is applied as there is no scientific rational that the substance absorption by the oral route is less efficient than pullmonary absorption. Equal absorption for oral ingestion and inhalation has been assessed from physico-chemical properties of the substance.
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- irritation (respiratory tract)
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- irritation (respiratory tract)
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 0.25 mg/kg bw/day
- Most sensitive endpoint:
- skin irritation/corrosion
- Route of original study:
- Dermal
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 1 800
- Modified dose descriptor starting point:
- LOAEL
- Value:
- 450 mg/kg bw/day
- AF for dose response relationship:
- 3
- Justification:
- starting point is low-dose LOAEL (conditional decline: bw loss, death) in a subacute dermal study
- AF for differences in duration of exposure:
- 6
- Justification:
- The extrapolation factor from short term toxicity to the long-term scenario for a substance causing primary local toxicity is reduced by factor 2. For local irritation the concentration is in most cases the relevant parameter, and prolongation of exposure is expected to influence the severity of effect and morphology of changes, but not the NOAEL/NOAEC.
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- rat
- AF for other interspecies differences:
- 2.5
- Justification:
- default
- AF for intraspecies differences:
- 5
- Justification:
- worker population
- AF for the quality of the whole database:
- 2
- Justification:
- non GLP, pre-guideline test without NOAEL, but CPSC-reviewed data in rats and rabbits
- AF for remaining uncertainties:
- 1
- Justification:
- no remaining uncertainties; no AF for read-across is necessary (see read across justification)
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:
- 0.05 mg/cm²
- Most sensitive endpoint:
- skin irritation/corrosion
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 5
- Dose descriptor:
- other: NOAEL
- AF for dose response relationship:
- 1
- Justification:
- MTD taken from chronic painting study in mice
- AF for differences in duration of exposure:
- 1
- Justification:
- chronic NOAEL
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- Allometric scaling to adjust for physiological based species differences is widely accepted for systemic toxic substances, but this does not apply to direct local effects.
- AF for other interspecies differences:
- 1
- Justification:
- There is no evidence for differences in the general mode of action or kinetics, so there is no rational for an additional factor of 2.5 for remaining differences. This factor has no scientific basis, as the mode of action is direct chemical reactivity.
- AF for intraspecies differences:
- 5
- Justification:
- worker population
- AF for the quality of the whole database:
- 1
- Justification:
- MTD is considered reliable even if from non GLP, pre-guideline test; CPSC-reviewed data in mice
- AF for remaining uncertainties:
- 1
- Justification:
- no remaining uncertainties; no AF for read-across fromTHPC is necessary (see read across justification)
Acute/short term exposure
- Hazard assessment conclusion:
- no DNEL required: short term exposure controlled by conditions for long-term
- Most sensitive endpoint:
- skin irritation/corrosion
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- high hazard (no threshold derived)
Additional information - workers
The substance is characterised by primary local toxicity (irritation or corrosion) depending on the concentration applied. No significant inhalation exposure is expected. Systemic toxicity was seen after repeated oral and dermal (read-across) exposure to high doses. In order to perform a quantitative risk assessment, a dermal long-term systemic DNEL was calculated based on the sub-acute LOAEL (THPC: conditional decline, death) in rats. The dermal long-term local DNEL was calculated based on the NOAEL (THPC) from a chronic mice study. The inhalation DNELs were extrapolated from an maternal NOAEL (conditional decline) with the substance. The latter were found to be close to the TLV-TWA (US-ACGIH) for THPC, a closely related, precursor 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:
- 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
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
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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