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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 246-771-9 | CAS number: 25265-77-4
- 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:
- 123.42 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):
- 10
- Dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 1 234.21 mg/m³
- Explanation for the modification of the dose descriptor starting point:
The oral NOAEL in a rat 90- day study under OECD 408 was 300 mg/kg/day for male 1000 for female rats. The findings driving the NOAEL for male rats was due the a2u, which is only found in males rat, and not in any other species or sex of animals. No adverse effects were found in females. To compensate for the lack of adversity in females, and for findings only relevant to male rats in the males, the "remaining intraspecies" value was adjusted from 2.5x to 1
The NOAEL of 1000 mg/kg/day was converted to an inhalation dose using the conversion factor of 0.38 m3 /kg BW/8 hours. Further adjustments are made for light work (0.67) and for 100% vs. 50% bioavailability and 1.4x for a 7 day experimental exposure to a 5 -day workweek. This results in the modified dose descriptor of 1234.21 mg/m3
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 2
- Justification:
- Standard value for subchronic to chronic duration
- AF for other interspecies differences:
- 1
- Justification:
- The oral NOAEL in a rat 90- day study under OECD 408 was 300 mg/kg/day for male 1000 for female rats. The findings driving the NOAEL for male rats was due the a2u, which is only found in males rat, and not in any other species or sex of animals. No adverse effects were found in females. To compensate for the lack of adversity in females, and for findings only relevant to male rats in the males, the "remaining intraspecies" value was adjusted from 2.5x to 1
- AF for intraspecies differences:
- 5
- Justification:
- Standard value
- AF for the quality of the whole database:
- 1
- AF for remaining uncertainties:
- 1
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 617 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- DNEL extrapolated from long term DNEL
- Explanation for the modification of the dose descriptor starting point:
The standard derivation of the acute DNEL with DNEL(acute) = 5xDNEL(long-term) was used.
- Justification:
- Standard value
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:
- 35 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):
- 40
- Dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1 400 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The oral NOAEL in a rat 90- day study under OECD 408 was 300 mg/kg/day for male 1000 for female rats. The findings driving the NOAEL for male rats was due the a2u, which is only found in males rat, and not in any other species or sex of animals. No adverse effects were found in females. To compensate for the lack of adversity in females, and for findings only relevant to male rats in the males, the "remaining intraspecies" value was adjusted from 2.5x to 1
The NOAEL of 1000 mg/kg/day was adjusted by a factor of 1.4x for a 7 day experimental exposure to a 5 -day work week. The modified dose descriptor was 1400 mg/kg/day
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 2
- Justification:
- Standard value for subchronic to chronic duration
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Standard value
- AF for other interspecies differences:
- 1
- Justification:
- The oral NOAEL in a rat 90- day study under OECD 408 was 300 mg/kg/day for male 1000 for female rats. The findings driving the NOAEL for male rats was due the a2u, which is only found in males rat, and not in any other species or sex of animals. No adverse effects were found in females. To compensate for the lack of adversity in females, and for findings only relevant to male rats in the males, the "remaining intraspecies" value was adjusted from 2.5x to 1
- AF for intraspecies differences:
- 5
- Justification:
- Standard value
- AF for the quality of the whole database:
- 1
- AF for remaining uncertainties:
- 1
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 175 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):
- 100
- DNEL extrapolated from long term DNEL
- Explanation for the modification of the dose descriptor starting point:
The standard derivation of the acute DNEL with DNEL(acute) = 5xDNEL(long-term) was used.
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
Worker
The data from a 90-day repeat dose study in rats is used for DNEL calculation. The NOAEL of 1000 mg/kg/day was based on kidney effects that are based on a mechanism that is not relevant to humans or other animals other than male rats.
Worker DNEL long-term systemic for oral route
No oral DNEL for workers
Worker DNEL long-term systemic for dermal route
Start point: NOAEL: 1000mg/kg bw/day (based on oral 90-day rat study).
Differences in absorption: Abs (oral-rat) / Abs (dermal-human): 1
Correction for 7 day/week dosing in the study to a 5 day work week: 1.4
=>Corrected NOAEL: 1400 mg/kg bw/day
Interspecies differences: Allometric scaling: 4
Remaining interspecies differences: 1
Intraspecies differences: 5
Differences in duration of exposure (subchronic study to chronic): 2
Dose response and endpoint specific/severity issues: 1
Quality of database: 1
Overall factor (product of individual factors): 40
=>Worker DNEL long-term for dermal route-systemic: 35 mg/kg bw/day
Worker DNEL long-term systemic for inhalation route
Start point: NOAEL 1000 mg/kg bw/day (based on oral 90-day rat study).
Respiratory volume rat (sRV) (worker (8 h): 1/0.38): 2631.5 mg/m3
Correction for respiratory bioavailability (100%/50%): 1315.7 mg/m3
Corrected for 7 days of animal dosing to a 5 day work week (1.4x value): 1842.11 mg/m3
Differences in respiratory volume (default factor "light activity worker"): 1234.21 mg/m3
Corrected NOAEC: 1234.21 mg/m3
Remaining interspecies differences: 1
Intraspecies differences: 5
Differences in duration of exposure: 2
Dose response and endpoint specific/severity issues: 1
Quality of database: 1
Overall factor (product of individual factors): 10
=>Worker DNEL long-term for inhalation route-systemic: 123.42 mg/m3
General Population - Hazard via inhalation route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 21.7 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):
- 80
- Dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEC
- Value:
- 434.78 mg/m³
- Explanation for the modification of the dose descriptor starting point:
The oral NOAEL in a rat 90- day study under OECD 408 was 300 mg/kg/day for male 1000 for female rats. The findings driving the NOAEL for male rats was due the a2u, which is only found in males rat, and not in any other species or sex of animals. No adverse effects were found in females. To compensate for the lack of adversity in females, and for findings only relevant to male rats in the males, the "remaining intraspecies" value was adjusted from 2.5x to 1
The NOAEL of 1000 mg/kg/day was converted to an inhalation dose using the conversion factor of 1.15 m3 /kg BW/24 hours. Further adjustments are made for 100% vs. 50% bioavailability. This results in the modified dose descriptor of 434.78 mg/m3
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 2
- Justification:
- Standard value for subchronic to chronic duration
- AF for other interspecies differences:
- 1
- Justification:
The oral NOAEL in a rat 90- day study under OECD 408 was 300 mg/kg/day for male 1000 for female rats. The findings driving the NOAEL for male rats was due the a2u, which is only found in males rat, and not in any other species or sex of animals. No adverse effects were found in females. To compensate for the lack of adversity in females, and for findings only relevant to male rats in the males, the "remaining intraspecies" value was adjusted from 2.5x to 1- AF for intraspecies differences:
- 10
- Justification:
- Standard value
- AF for the quality of the whole database:
- 1
- AF for remaining uncertainties:
- 1
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 108.5 mg/m³
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- DNEL extrapolated from long term DNEL
- Explanation for the modification of the dose descriptor starting point:
Standard derivation of acute DNEL was used.i.e. Acute DNEL = Long term DNEL *5
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:
- DNEL (Derived No Effect Level)
- Value:
- 12.5 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):
- 80
- Dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1 400 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The oral NOAEL in a rat 90- day study under OECD 408 was 300 mg/kg/day for male 1000 for female rats. The findings driving the NOAEL for male rats was due the a2u, which is only found in males rat, and not in any other species or sex of animals. No adverse effects were found in females. To compensate for the lack of adversity in females, and for findings only relevant to male rats in the males, the "remaining intraspecies" value was adjusted from 2.5x to 1
The NOAEL of 1000 mg/kg/day was not adjusted as the study was dosed 7 days/week. The modified dose descriptor was 1000 mg/kg/day
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 2
- Justification:
- Standard value for subchronic to chronic:
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Standard value
- AF for other interspecies differences:
- 1
- Justification:
The oral NOAEL in a rat 90- day study under OECD 408 was 300 mg/kg/day for male 1000 for female rats. The findings driving the NOAEL for male rats was due the a2u, which is only found in males rat, and not in any other species or sex of animals. No adverse effects were found in females. To compensate for the lack of adversity in females, and for findings only relevant to male rats in the males, the "remaining intraspecies" value was adjusted from 2.5x to 1- AF for intraspecies differences:
- 10
- Justification:
- Standard value
- AF for the quality of the whole database:
- 1
- AF for remaining uncertainties:
- 1
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 62.5 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- DNEL extrapolated from long term DNEL
- Explanation for the modification of the dose descriptor starting point:
Standard derivation of acute DNEL was used.i.e. Acute DNEL = Long term DNEL *5
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:
- DNEL (Derived No Effect Level)
- Value:
- 12.5 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):
- 80
- Dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 1 000 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
The oral NOAEL in a rat 90- day study under OECD 408 was 300 mg/kg/day for male 1000 for female rats. The findings driving the NOAEL for male rats was due the a2u, which is only found in males rat, and not in any other species or sex of animals. No adverse effects were found in females. To compensate for the lack of adversity in females, and for findings only relevant to male rats in the males, the "remaining intraspecies" value was adjusted from 2.5x to 1
The NOAEL of 1000 mg/kg/day was not adjusted as the study was dosed 7 days/week. The modified dose descriptor was 1000 mg/kg/day
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 2
- Justification:
- Standard value for sub-chronic to chronic duration
- AF for interspecies differences (allometric scaling):
- 4
- Justification:
- Standard value
- AF for other interspecies differences:
- 1
- Justification:
The oral NOAEL in a rat 90- day study under OECD 408 was 300 mg/kg/day for male 1000 for female rats. The findings driving the NOAEL for male rats was due the a2u, which is only found in males rat, and not in any other species or sex of animals. No adverse effects were found in females. To compensate for the lack of adversity in females, and for findings only relevant to male rats in the males, the "remaining intraspecies" value was adjusted from 2.5x to 1- AF for intraspecies differences:
- 10
- Justification:
- Standard value
- AF for the quality of the whole database:
- 1
- AF for remaining uncertainties:
- 1
Acute/short term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 62.5 mg/kg bw/day
- Most sensitive endpoint:
- repeated dose toxicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- DNEL extrapolated from long term DNEL
- Explanation for the modification of the dose descriptor starting point:
Standard derivation of acute DNEL was used.i.e. Acute DNEL = Long term DNEL *5
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - General Population
General Population
General Population DNEL long-term systemic for oral route
Start point: NOAEL: 1000 mg/kg bw/day (based on oral 90-day rat study).
Differences in absorption Abs (oral-rat) / Abs (oral-human): 1
=> Corrected NOAEL: 1000 mg/kg bw/day
Interspecies differences:Allometric scaling: 4
Remaining interspecies differences: 1
Intraspecies differences: 10
Differences in duration of exposure (subchronic study to chronic study): 2
Dose response and endpoint specific/severity issues: 1
Quality of database: 1
Overall factor (product of individual factors): 80
=>General Population DNEL long-term for oral route-systemic: 12.5 mg/kg bw/day
General Population DNEL long-term systemic for dermal route
Start point: NOAEL: 1000 mg/kg bw/day (based on oral 90-day rat study)
Differences in absorption: Abs (oral-rat) / Abs (dermal-human):1
=>Corrected NOAEL: 1000 mg/kg bw/day
Interspecies differences: Allometric scaling: 4
Remaining interspecies differences: 1
Intraspecies differences: 10
Differences in duration of exposure (subchronic study to chronic): 2
Dose response and endpoint specific/severity issues: 1
Quality of database: 1
Overall factor (product of individual factors): 80
=>General Population DNEL long-term for dermal route-systemic: 12.5 mg/kg bw/day
General Population DNEL long-term systemic for inhalation route
Start point: NOAEL 1000 mg/kg bw/day (based on oral 90-day rat study).
Respiratory volume rat (sRV) (worker (8 h): 1/1.15): 869.57 mg/m3
Correction for respiratory bioavailability (100%/50%): 434.78 mg/m3
Corrected NOAEC: 434.78 mg/m3
Remaining interspecies differences: 1
Intraspecies differences: 10
Differences in duration of exposure: 2
Dose response and endpoint specific/severity issues: 1
Quality of database: 1
Overall factor (product of individual factors): 20
=>General PopulationDNEL long-term for inhalation route-systemic: 21.7 mg/m3
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