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Diss Factsheets
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EC number: 275-073-7 | CAS number: 70969-70-9
- 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:
- 1.65 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):
- 75
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 123.4 mg/m³
- Explanation for the modification of the dose descriptor starting point:
- The oral NOAEL of 50 mg/kg bw/d is converted to a NOAEC by dividing by 0.38 m3/kg bw and multiplication with 6.7/10 to correct for worker ventilation and multiplicaton with 7/5 to correct for 7 days/week experimental exposure vs. 5 working days per week,according to ECHA Guidance R8. According to the toxicokinetic assessment, no difference in bioavailability after inhalation or oral exposure is considered relevant for this substance.
- AF for dose response relationship:
- 1
- Justification:
- not required, starting point is NOAEC
- AF for differences in duration of exposure:
- 6
- Justification:
- extrapolation from subacute to chronic
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- allometric scaling factor rat-human not applied for inhalation route as considered in NOAEC calculation
- AF for other interspecies differences:
- 2.5
- Justification:
- default factor for remaining differences
- AF for intraspecies differences:
- 5
- Justification:
- default factor for worker
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- 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:
- no hazard identified
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:
- DNEL (Derived No Effect Level)
- Value:
- 2.92 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 300
- Dose descriptor starting point:
- NOAEL
- Value:
- 50 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 875 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- According to the toxicokinetic assessment, the absorption rate from dermal route is assumed to be 8% and the absorption rate of oral route is considered to be 100%. Therefore, the oral NOAEL of 50 mg/kg bw/d is converted to a NOAEL of dermal route by dividing by 0.08 and by multiplicaton with 7/5 to correct for 7 days/week experimental exposure vs. 5 working days per week
- AF for dose response relationship:
- 1
- Justification:
- not required, starting point is NOAEL
- AF for differences in duration of exposure:
- 6
- Justification:
- extrapolation from subacute to chronic
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- allometric scaling factor rat-human
- AF for other interspecies differences:
- 2.5
- Justification:
- default factor for remaining differences
- AF for intraspecies differences:
- 5
- Justification:
- default factor for worker
- AF for the quality of the whole database:
- 1
- Justification:
- not required
- 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:
- no hazard identified
Acute/short term exposure
- Hazard assessment conclusion:
- no hazard identified
Workers - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - workers
According to the results of toxicokinetic assessment, the inhalation route is not considered a very relevant exposure route and uptake rate via inhalation is smaller than via the oral route so that, conservatively, the ratio of inhalation and oral bioavailability is assumed as 1. In addition, the absorption rate from dermal route is assumed to be 8% and the absorption rate of oral route is considered to be 100%. Therefore, the oral NOAEL of 50 mg/kg bw/d is converted to a dermal NOAEL of 500 mg/kg/day by dividing by 0.08 and multiplicaton with 7/5 to correct for 7 days/week experimental exposure vs. 5 working days per week.
As basis for DNEL derivation the result from a sub-chronic study with rats was used, performed according to OECD 422 under GLP. In this study, the test item was administered at dosages of 50, 250, and 1000/500 mg/kg body weight/day, and controls received the vehicle only. Based on the results of this study, a NOAEL (No Observed Adverse Effect Level) for systemic toxicity in rats was considered to be 50 mg/kg bw/day. Hence this study is chosen as basis for DNEL derivation. Based on the above description, the basis for the DNEL therefore is this oral NOAEL (50 mg/kg bw/day), and NOAELcorr for the dermal route is 875 mg/kg bw/day. According to ECHA guidance document the oral NOAEL is converted to an inhalative NOAEC(Worker) by dividing by 0.38 m³/kg and multiplying by 6.7/10 to take account for light work activities resulting in a NOAEC of 88.16 mg/m³ and multiplicaton with 7/5 to correct for 7 days/week experimental exposure vs. 5 working days per week.
No acute effects were seen in other studies performed using the substance, and therefore DNELs for acute effects were not derived.
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
With regard to consumer exposure the substance under concern is used only in cosmetic products. Therefore, the derivation of DNELs, assessment of exposure and risk characterization are not required (ECHA guidance on information requirements and chemical safety assessment - Chapter R.8: Characterisation of dose [concentration]-response for human health, Version 2.1, November 2012, ECHA-2010 -G-19 -EN). Furthermore, no indirect exposure assessment is necessary in accordance toECHA guidance on information requirements and chemical safety assessment - Chapter R.16: Environmental exposure assessment, Version 3.0, February 2016, ECHA-16 -G-03 -EN.
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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