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Diss Factsheets
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EC number: 939-649-8 | CAS number: 1474044-69-3
- 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:
- 14.69 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: ECHA REACH Guidance and ECETOC 2010
- Overall assessment factor (AF):
- 18
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 264.5 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- Route to route extraploation required for oral to inhalation route as no long term inhalation study available.
- AF for dose response relationship:
- 1
- Justification:
- The starting point for the DNEL calculation is a NOAEL, therefore an assessment factor of 1 is applicable.
- AF for differences in duration of exposure:
- 6
- Justification:
- Default AF for subacute to chronic studies (an OECD 422 study)
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- AF for allometric scaling not required as the differences in allometry (respiration rate and rat to human body sizes) were considered in the conversion from oral to inhalation starting point.
- AF for other interspecies differences:
- 1
- Justification:
- An extra AF for additional toxicodynamic differences was not applied, as inhalation absorption to oral absorption was assessed in the modification of starting point.
- AF for intraspecies differences:
- 3
- Justification:
- AF of 3 by ECETOC (2010) for workers is sufficiently conservative.
- AF for the quality of the whole database:
- 1
- Justification:
- All relevant studies conducted to GLP and of reliability 1.
- AF for remaining uncertainties:
- 1
- Justification:
- None identified.
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
DNEL related information
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 4.17 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- other: ECHA REACH Guidance and ECETOC 2010
- Overall assessment factor (AF):
- 72
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 300 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- Route to route extraploation required for oral to dermal route as no long term dermal study available.
- AF for dose response relationship:
- 1
- Justification:
- The starting point for the DNEL calculation is a NOAEL, therefore an assessment factor of 1 is applicable.
- AF for differences in duration of exposure:
- 6
- Justification:
- Default AF for subacute to chronic studies (an OECD 422 study)
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Default AF for allometric scaling for rats
- AF for other interspecies differences:
- 1
- Justification:
- An extra AF for additional toxicodynamic differences was not applied, as dermal absorption is expected to be lower in humans as in rats..
- AF for intraspecies differences:
- 3
- Justification:
- AF of 3 by ECETOC (2010) for workers is sufficiently conservative.
- AF for the quality of the whole database:
- 1
- Justification:
- All relevant studies conducted to GLP and of reliability 1.
- AF for remaining uncertainties:
- 1
- Justification:
- None identified.
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
- Most sensitive endpoint:
- acute toxicity
- Route of original study:
- Dermal
DNEL related information
Local effects
Long term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
Acute/short term exposure
- Hazard assessment conclusion:
- low hazard (no threshold derived)
- Most sensitive endpoint:
- skin irritation/corrosion
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - workers
The substance is classified for human health as a skin irritant (R38) according to Directive 67/548/EEC (DSD) criteria. However, the substance is not classified as a skin irritant according to CLP ((Regulation (EC) No 1272/2008).
Inhalation:
Inhalation is not considered to be a significant route of exposure based on the substances physico-chemical properties and use patterns. However, a long-term DNEL for systemic effects has been derived, based on the results obtained OECD 422 Oral (Gavage) Combined Repeat Dose Toxicity Study With Reproduction / Developmental Toxicity Screening Test in the Rat conducted on the substance.
Long-term systemic effects:
A modification of the dose descriptor starting point (oral to inhalation) was conducted. It is assumed as a worst case assumption that the oral absorption rate is 50% of that of the inhalation absorption.
The corrected dose descriptor (NOAEC) for inhalation was calculated in accordance with the ECHA Guidance on information requirements and chemical safety assessment, Chapter R.8: Characterisation of dose [concentration]-response for human health.
The conversion of an oral rat NOAEL into a corrected inhalatory NOAEC to assess human inhalatory exposure was performed using the modification of starting point equation as given in Figure R. 8-3 in ECHA Guidance: Characterisation of dose [concentration] - response for human health (Chapter R.8) (see below) for workers (in the case of 8 hour exposure/day).
Default parameters for rats and humans (for 8 hour exposure) were used for the modification of starting point under the allometric scaling principle as given in Table R. 8-2 of the above ECHA guidance.
Conversion of an oral rate N(L) OAEL into a correct inhalatory N(L) OAEC to assess human inhalatory exposure:
For workers (in case of 8h exposure/day):
Corrected inhalatory N(L) OAEC = oral N(L) OAEL x (1 / sRVrat) x (ABSoral-rat / ABSinh-human) x (sRVhuman / wRV)
Corrected inhalatory N(L) OAEC= 300 mg/kg bw/day x (1 / 0.38 m3/kg/d) x (0.5) x (6.7 m3(8h) / 10 m3(8h)) = 264.5 mg/m3
Where:
ABS: Absorption
sRV: standard Respiratory Volume
wRV: worker Respiratory Volume (light activity)
Default parameters:
sRVrat (8 h): 0.38m3/kg bw
sRVhuman (8 h): 6.7 m3/ person
wRV (8 h): 10 m3/ person
The appropriate assessment factors were then applied to give an overall assessment factor of 18
Long-term systemic DNEL (inhalation)= 14.69 mg/m3
This long-term inhalation systemic effect DNEL is used in the quantitative assessment of risk for systemic toxicity to workers via the inhalation route. The long-term DNEL shall also cover short-term exposure.
Any potential local effects from inhalation exposure are assessed qualitatively.
Dermal:
A DNEL has been derived for long-term systemic effects by the dermal route, based on the results obtained from a OECD 422 Oral (Gavage) Combined Repeat Dose Toxicity Study With Reproduction / Developmental Toxicity Screening Test in the Rat conducted on the substance.
Long-term systemic DNEL (dermal) = 4.17 mg/kg bw/day
This long-term inhalation systemic effect DNEL is used in the quantitative assessment of risk for systemic toxicity to workers via the dermal route.
Although the substance is a moderate skin irritant (low hazard), DNELs for local effects have not been derived as the dermal irritation study did not give adequate data for a DNEL to be determined. It is considered that a qualitative assessment of risk for local effects to workers is sufficient.
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
DNELs have not been derived for the general public (apart from via the oral route for systemic effects) as there will be no exposure to the general public/consumers as the substance only has industrial applications.
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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