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Diss Factsheets
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EC number: 202-592-8 | CAS number: 97-59-6
- 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:
- 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
Workers - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 284 mg/kg bw/day
- Most sensitive endpoint:
- carcinogenicity
- Route of original study:
- Oral
DNEL related information
- DNEL derivation method:
- ECHA REACH Guidance
- Overall assessment factor (AF):
- 2.5
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 710 mg/kg bw/day
- Explanation for the modification of the dose descriptor starting point:
- The oral route of exposure is considered to be a conservative route of exposure as compared to dermal.
- AF for differences in duration of exposure:
- 1
- Justification:
- Chronic study
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- AF’s = 1 (Allometric scaling. Normally 4 for rat to human but this is an endogenous compound in both species and the reference toxicity value is a NOEL not a NOAEL).
- AF for other interspecies differences:
- 2.5
- AF for intraspecies differences:
- 1
- Justification:
- AF’s = 1 for Intraspecies differences workers. Normally this AF = 5 but this is an endogenous compound which is considered safe at single oral doses of 10 grams in both healthy and unhealthy patients and has been used safely in skin preparations for many years at concentrations of up to 2% by weight.
- AF for the quality of the whole database:
- 1
- AF for remaining uncertainties:
- 1
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
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
The long-term DNEL’s are based on the NOEL for the 2 year oral study in Fischer 344 rats. Body weight information is not available but chronic body weight for the male Fischer 344 rats has been estimated by the USEPA as 380 grams. The males consumed 40 grams of Allantoin during the 106 week study period. This equates to a NOEL of 142 mg/kg bw/d.
DNEL dermal long term workers:
Oral NOAEL 142 mg x 20% worst case measured skin absorption = 142 x 5 = 710 mg/kg bw d
AF’s = 1 (Allometric scaling. Normally 4 for rat to human but this is an endogenous compound in both species and the reference toxicity value is a NOEL not a NOAEL) x 2.5 (Remaining interspecies differences) x 1 (Intraspecies differences workers. Normally 5 but again this is an endogenous compound which is considered safe at single oral doses of 10 grams in both healthy and unhealthy patients and has been used safely in skin preparations for many years at concentrations of up to 2% by weight) x 1 (chronic study) x 1 (DR reliability) x 1 (Quality of the database) = 2.5
DNEL Dermal long term workers = 710/2.5 = 284 mg/kg bw d
General Population - Hazard via inhalation route
Systemic 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
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
General Population - Hazard via dermal route
Systemic effects
Long term exposure
- Hazard assessment conclusion:
- DNEL (Derived No Effect Level)
- Value:
- 284 mg/kg bw/day
- Most sensitive endpoint:
- carcinogenicity
- Route of original study:
- Oral
DNEL related information
- Overall assessment factor (AF):
- 2.5
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 710 mg/kg bw/day
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 1
- Justification:
- Chronic 2 yr study
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- AF’s = 1 (Allometric scaling. Normally 4 for rat to human but this is an endogenous compound in both species and the reference toxicity value is a NOEL not a NOAEL).
- AF for other interspecies differences:
- 2.5
- AF for intraspecies differences:
- 1
- Justification:
- AF’s = 1 for Intraspecies differences workers. Normally this AF = 5 but this is an endogenous compound which is considered safe at single oral doses of 10 grams in both healthy and unhealthy patients and has been used safely in skin preparations for many years at concentrations of up to 2% by weight.
- AF for the quality of the whole database:
- 1
- AF for remaining uncertainties:
- 1
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
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:
- DNEL (Derived No Effect Level)
- Value:
- 56.8 mg/kg bw/day
- Most sensitive endpoint:
- carcinogenicity
- Route of original study:
- Oral
DNEL related information
- Overall assessment factor (AF):
- 2.5
- Modified dose descriptor starting point:
- NOAEL
- Value:
- 142 mg/kg bw/day
- AF for dose response relationship:
- 1
- AF for differences in duration of exposure:
- 1
- Justification:
- Chronic 2 yr study
- AF for interspecies differences (allometric scaling):
- 1
- Justification:
- AF’s = 1 (Allometric scaling. Normally 4 for rat to human but this is an endogenous compound in both species and the reference toxicity value is a NOEL not a NOAEL).
- AF for other interspecies differences:
- 2.5
- AF for intraspecies differences:
- 1
- Justification:
- AF’s = 1 for Intraspecies differences workers. Normally this AF = 5 but this is an endogenous compound which is considered safe at single oral doses of 10 grams in both healthy and unhealthy patients and has been used safely in skin preparations for many years at concentrations of up to 2% by weight.
Acute/short term exposure
- Hazard assessment conclusion:
- hazard unknown (no further information necessary)
DNEL related information
General Population - Hazard for the eyes
Local effects
- Hazard assessment conclusion:
- no hazard identified
Additional information - General Population
The long-term DNEL’s are based on the NOEL for the 2 year oral study in Fischer 344 rats. Body weight information is not available but chronic body weight for the male Fischer 344 rats has been estimated by the USEPA as 380 grams. The males consumed 40 grams of Allantoin during the 106 week study period. This equates to a NOEL of 142 mg/kg bw d.
DNEL dermal long term general population:
Oral NOAEL 142 mg/kg bw d x 20% worst case measured skin absorption = 142 x 5 = 710 mg/kg bw d
AF’s = 1 (Allometric scaling. Normally 4 for rat to human but this is an endogenous compound in both species and the reference toxicity value is a NOEL not a NOAEL) x 2.5 (Remaining interspecies differences) x 1 (Intraspecies differences general population. Normally 10 but again this is an endogenous compound which is considered safe at single oral doses of 10 grams in both healthy and unhealthy patients and has been used safely in skin preparations for many years at concentrations of up to 2% by weight) x 1 (chronic study) x 1 (DR reliability) x 1 (Quality of the database) = 2.5
DNEL Dermal long term general population = 710/2.5 = 284 mg/kg bw d
DNEL Oral long term general population:
Oral NOAEL 142 mg/kg bw d
AF’s = 1 (Allometric scaling. Normally 4 for rat to human but this is an endogenous compound in both species and the reference toxicity value is a NOEL not a NOAEL) x 2.5 (Remaining interspecies differences) x 1 (Intraspecies differences general population. Normally 10 but again this is an endogenous compound which is considered safe at single oral doses of 10 grams in both healthy and unhealthy patients and has been used safely in skin preparations for many years at concentrations of up to 2% by weight) x 1 (chronic study) x 1 (DR reliability) x 1 (Quality of the database) = 2.5
DNEL oral long term general population = 142/2.5 = 56.8 mg/kg bw d
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